alonso, 1998. quantitative determination of e. coli and fecal coliforms in water using a chromogenic...
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7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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This article was downloaded by [Southern Illinois University]On 18 July 2015 At 2105Publisher Taylor amp FrancisInforma Ltd Registered in England and Wales Registered Number1072954 Registered office 5 Howick Place London SW1P 1WG
Journal of Environmental
Science and Health
Part A ToxicHazardous
Substances and
EnvironmentalEngineeringPublication details including instructionsfor authors and subscription informationhttpwwwtandfonlinecomloilesa20
Quantitative
determination of Ecoli and fecal coliforms
in water using a
chromogenic mediumJL Alonso
a A Soriano
b I Amoros
a amp
MA Ferrusc
a Instituto de Hidrologiacutea y Medio Natural Universidad Politeacutecnica Camino de Vera14 Valencia 46022b Gamaser SL c Pedrapiquers 4
Valencia 46014c Departamento de Biotecnologiacutea
Universidad Politecnica SpainPublished online 15 Dec 2008
To cite this article JL Alonso A Soriano I Amoros amp MA Ferrus (1998)Quantitative determination of E coli and fecal coliforms in water using achromogenic medium Journal of Environmental Science and Health Part AToxicHazardous Substances and Environmental Engineering 336 1229-1248DOI 10108010934529809376785
To link to this article httpdxdoiorg10108010934529809376785
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J EN VIRON SCI HE ALTH A33(6) 12299830851248 (1998)
QU NTIT TIVE DETERMIN TION OF E COLI ND FEC L
COLIFORMS IN
W TER
USING CHROMOGENIC
M E I U M
Key Words Kcoli β 983085 galactosidase
β 983085 glucuronidase
water fecal coliforms
J L Alonso
1
A Soriano
2
I
Amoros
1
and MA
F e r rus
3
1
Inst i tu to
de Hidrologiacutea y Medio Natural Universidad Politeacutecnica Camino de Vera 14
46022 Valencia
2
Gamaser SL c Pedrapiquers 4 46014 Valencia
3
Departamento de Biotecnologiacutea Universidad Politecnica
Spain
STR CT
A new medium Chromocult Coliformreg Agar (CC agar) developed by E
Merck AG (Darmstadt Germany) was compared with the Standard Methods
membrane filtration fecal coliform (mFC) medium for fecal coliform detection and
enumeration In the CC agar non-E coli fecal coliforms (Klebsiella Enterobacter and
Citrobacter) (KEC) were identified by the production of a salmon to red colour from
p-galactosidase (LAC) cleavage of the substrate Salmon-GAL while E coli colonies
were detected by the blue colour produced by the cleavage of X-glucuronide by
β 983085
1229
Copyright copy 1998 by Marcel Dekker Inc wwwdekkercom
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1230 ALONSO ET AL
glucuronidase
G U S ) Statistically there was no significant differences between fecal
coliform counts obtained with the two media (CC agar and mFC agar) and two
incubation
procedures (2h983085 37degC plus 22h983085 445deg and 445degC) as determined by variance
analysis In our study K
coli
represented on average 705983085 925 of the fecal coliform
population A high incidence of
false
negative KEC (195 ) and
E
coli (296 )
colonies
was detected at 445degC Two
K
coli
GUS negative phenotype upon
reinoculation into CC agar were
G U S
+
A total of 31 KEC LAC colonies were
streaked on to
CC
agar and incubated at 37degC 29 KEC strains tha t failed to produce β 983085
galactosidase at 445degC were able to produce the enzyme at 37degC In our opinion the
physiological condition of the fecal coliform isolates could be responsible for the non983085
expression of P983085 galactosidase and P983085 glucuronidase activities at 445degC
INTRODUCTION
The
detection and enumeration of indicator organisms are of primary
importance
for the monitoring of sanitary and microbiological quality of water Fecal
coliforms have been long used as indicators of fecal contamination in water and food
The
term fecal coliform include all coliforms
tha t
can ferment lactose at 445degC trying
t o separate the non ubiquitous coliforms from those of true fecal origin (Dockins and
McFe t e r s 1978) The presence ofpound coli directly relates to fecal contamination with its
implied threat of the presence of enteric disease agents (Rice et al 1990) The other
members of the fecal coliform group Klebsiella Enterobacter and
Citrobacter)
may
be isolated in feces but their presence does not always suggest fecal contamination
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QUANTITATIVE DETERMINATION OF E COLI 1231
(Covert et al 1992) The abbreviation KE C will be used in this study for the
designation of non-E coli fecal coliforms (Klebsiella Enterobacter and Citrobacter)
A major limitation of current membrane filtration methods used for counting
fecal coliforms is the enumeration of microorganisms which are not exclusively of fecal
origin thereby giving a false indication of the sanitary quality of the water
(Au goustinos et al 1993) Identification of pound coli in the past has been laborious and
only recently methods have been developed that detect
E coli
rapidly with accuracy
and specificity (Alonso et al 1996 Shadix et al 1993) The identification of coliforms
based on detection of P-galactosidase activity (Manafi et al 1991) is a significant
departure from methods that utilize the bacterial end products of lactose fermentation
(APHA 1995)
A new chromogenic medium Chromocult Coliformreg agar (CC agar) has been
developed by E Merck AG (Darmstadt Germany) to detect coliforms and K coli
simultaneously A combination o f tw o chrom ogenic glycosides is used for th e detection
of p-galactosidase (LAC) and P-glucuronidase (GUS) The Salmon-GAL substrate
causes a salmon to red colour of the KEC coliform colonies (LAC
+
GUS ) and the
substrate X-glucuronide is used for the identification of P-glucuronidase E coli
cleaves both Salmon-GAL and X-glucuronide so that positive colonies take on a dark
blue to violet colour (LA C
+
GUS)
In this study the CC agar was compared w ith the M-FC medium recommended
in Standard Methods (1995) for the enumeration of fecal coliforms by the membrane
filtration technique
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1232 ALONSO ET AL
M A T E R I A L A N D M E T HOD S
Sampling
A total o f 40 w ater samples were collected from 6 different environmental
sources in the Valencia area The water samples were as follows 6 samples from the
Turia river near Valencia drinking water treatment plant (site TR) 11 samples from
two well water supplies (site PI 6 samples and site P2 5 samples) 8 samples from a
heavily polluted stream (site AP) 8 samples of seawater (salinity 21o) (Malvarrosa
beac h) influenced by sew age discharge (site M l ) and 7 samples of seawater from a
point located 200 m south of the previously mentioned sewage discharge (salinity
34o) (site M 2) All samples we re collected in sterile glass bo ttles refrigerated and
assayed within 24 h after collection Samples from sites TR A P M l and M 2 w ere
preassayed within 2 h to estimate bacterial density Several dilutions of these samples
were filtered to estimate the number of KEC and
K coli
present in collected waters
After 22 h incubation the most appropriate dilution was chosen and samples were
definitively analyzed
Bacterial Strains
Th e 32 reference strains from the Coleccioacuten Espantildeola de Cultivos Tipo (C EC T)
and 6 Salmonella strains from the Instituto de Hidrologiacutea y Medio Natural (IHMN)
stock culture collection used in this study are listed in Table 1 All strains except
Enterococcus strains were grow n and maintained on nutrient agar (M erck ) Th e
Enterococcus strains were grow n and maintained on brain heart agar (M erck)
Incubation Temperature Effect
Pure-culture studies were conducted with reference and IHMN strains
Bac teria we re resuspended in 5 ml of phosph ate buffer (APH A 1995) A loopfiil of th e
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QUANTITATIVE DETERMINATION OF E OLI
TABLE 1
Growth Conditions a t 37deg 41deg and 44 5degC of Different
Bacteria on Chromocult Coliform Agar
1233
Test Strain
Enterobacter aerogenes
Enterobacter cloacae
Enterobacter sakazakii
Enterobacter gergoviae
Klebsiella pneumoniae
Klebsiella oxytoca
Klebsiella ozaenae
Citrobacter diversus
Citrobacter amalonaticus
Citrobacter freundii
Escherichia coli
Hafnia alvei
Serratia odoriacutefera
Serratia marcescens
Serratia rubiadea
Cedecea davisae
Kluyvera ascorbata
Shigella flexneri
Shigella boydii
Shigella sonnei
Aeromonas hydrofila
Aeromonas caviae
Aeromonas media
A eromonas jandaei
Aeromonas schubertii
Aeromonas trota
Aeromonas eucrenophila
A
veronii bv veronii
Vibrio cholerae
Pseudomonas aeruginosa
Enterococcus faecalis
Enterococcusfaecium
Salmonella derby
S bredeney (4 strains)
Salmonella london
No
684
194
858
857
140
860
851
856
863
401
678
157
867
159
868
842
861
585
583
413
398
838
4232
4228
4241
4255
4224
4257
557
108
184
410
IHMN
IHMN
IHMN
37degC
G
b
C
c
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ c
+ t
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ r
+ r
+ r
+ c
-
-
+ c
+ t
+ t
41
G ~
+
+
+
+
+
+
+
+
+
+
+
+
+
+
-
+
+
+
+
+
+
+
+
-
+
+
+
+
+
-
-
+
+
+
degC
r
r
r
r
r
r
r
r
c
r
b
r
r
t
r
-
r
c
t
b
r
r
r
r
-
r
r
r
r
c
-
-
c
t
t
445degC
G C
+ r
+ r
+ r
-
+ c
+ r
+ r
+ c
+ c
+ r
+ b
+ r
+ r
+ r
+ r
-
+ r
+ c
+ t
+ b
-
-
+ r
-
-
-
-
-
+ c
-
-
+ c
+ t
+ t
No of reference strain from the CECT
G
Growth +=Good +=Weak -=None
b
C
Colour r=Salmon to Red b=Dark Blue to Violet t=Light Blue to Turquoise
c=Colourless
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1422
24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1522
TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1622
1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1822
1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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J EN VIRON SCI HE ALTH A33(6) 12299830851248 (1998)
QU NTIT TIVE DETERMIN TION OF E COLI ND FEC L
COLIFORMS IN
W TER
USING CHROMOGENIC
M E I U M
Key Words Kcoli β 983085 galactosidase
β 983085 glucuronidase
water fecal coliforms
J L Alonso
1
A Soriano
2
I
Amoros
1
and MA
F e r rus
3
1
Inst i tu to
de Hidrologiacutea y Medio Natural Universidad Politeacutecnica Camino de Vera 14
46022 Valencia
2
Gamaser SL c Pedrapiquers 4 46014 Valencia
3
Departamento de Biotecnologiacutea Universidad Politecnica
Spain
STR CT
A new medium Chromocult Coliformreg Agar (CC agar) developed by E
Merck AG (Darmstadt Germany) was compared with the Standard Methods
membrane filtration fecal coliform (mFC) medium for fecal coliform detection and
enumeration In the CC agar non-E coli fecal coliforms (Klebsiella Enterobacter and
Citrobacter) (KEC) were identified by the production of a salmon to red colour from
p-galactosidase (LAC) cleavage of the substrate Salmon-GAL while E coli colonies
were detected by the blue colour produced by the cleavage of X-glucuronide by
β 983085
1229
Copyright copy 1998 by Marcel Dekker Inc wwwdekkercom
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 422
1230 ALONSO ET AL
glucuronidase
G U S ) Statistically there was no significant differences between fecal
coliform counts obtained with the two media (CC agar and mFC agar) and two
incubation
procedures (2h983085 37degC plus 22h983085 445deg and 445degC) as determined by variance
analysis In our study K
coli
represented on average 705983085 925 of the fecal coliform
population A high incidence of
false
negative KEC (195 ) and
E
coli (296 )
colonies
was detected at 445degC Two
K
coli
GUS negative phenotype upon
reinoculation into CC agar were
G U S
+
A total of 31 KEC LAC colonies were
streaked on to
CC
agar and incubated at 37degC 29 KEC strains tha t failed to produce β 983085
galactosidase at 445degC were able to produce the enzyme at 37degC In our opinion the
physiological condition of the fecal coliform isolates could be responsible for the non983085
expression of P983085 galactosidase and P983085 glucuronidase activities at 445degC
INTRODUCTION
The
detection and enumeration of indicator organisms are of primary
importance
for the monitoring of sanitary and microbiological quality of water Fecal
coliforms have been long used as indicators of fecal contamination in water and food
The
term fecal coliform include all coliforms
tha t
can ferment lactose at 445degC trying
t o separate the non ubiquitous coliforms from those of true fecal origin (Dockins and
McFe t e r s 1978) The presence ofpound coli directly relates to fecal contamination with its
implied threat of the presence of enteric disease agents (Rice et al 1990) The other
members of the fecal coliform group Klebsiella Enterobacter and
Citrobacter)
may
be isolated in feces but their presence does not always suggest fecal contamination
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 522
QUANTITATIVE DETERMINATION OF E COLI 1231
(Covert et al 1992) The abbreviation KE C will be used in this study for the
designation of non-E coli fecal coliforms (Klebsiella Enterobacter and Citrobacter)
A major limitation of current membrane filtration methods used for counting
fecal coliforms is the enumeration of microorganisms which are not exclusively of fecal
origin thereby giving a false indication of the sanitary quality of the water
(Au goustinos et al 1993) Identification of pound coli in the past has been laborious and
only recently methods have been developed that detect
E coli
rapidly with accuracy
and specificity (Alonso et al 1996 Shadix et al 1993) The identification of coliforms
based on detection of P-galactosidase activity (Manafi et al 1991) is a significant
departure from methods that utilize the bacterial end products of lactose fermentation
(APHA 1995)
A new chromogenic medium Chromocult Coliformreg agar (CC agar) has been
developed by E Merck AG (Darmstadt Germany) to detect coliforms and K coli
simultaneously A combination o f tw o chrom ogenic glycosides is used for th e detection
of p-galactosidase (LAC) and P-glucuronidase (GUS) The Salmon-GAL substrate
causes a salmon to red colour of the KEC coliform colonies (LAC
+
GUS ) and the
substrate X-glucuronide is used for the identification of P-glucuronidase E coli
cleaves both Salmon-GAL and X-glucuronide so that positive colonies take on a dark
blue to violet colour (LA C
+
GUS)
In this study the CC agar was compared w ith the M-FC medium recommended
in Standard Methods (1995) for the enumeration of fecal coliforms by the membrane
filtration technique
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1232 ALONSO ET AL
M A T E R I A L A N D M E T HOD S
Sampling
A total o f 40 w ater samples were collected from 6 different environmental
sources in the Valencia area The water samples were as follows 6 samples from the
Turia river near Valencia drinking water treatment plant (site TR) 11 samples from
two well water supplies (site PI 6 samples and site P2 5 samples) 8 samples from a
heavily polluted stream (site AP) 8 samples of seawater (salinity 21o) (Malvarrosa
beac h) influenced by sew age discharge (site M l ) and 7 samples of seawater from a
point located 200 m south of the previously mentioned sewage discharge (salinity
34o) (site M 2) All samples we re collected in sterile glass bo ttles refrigerated and
assayed within 24 h after collection Samples from sites TR A P M l and M 2 w ere
preassayed within 2 h to estimate bacterial density Several dilutions of these samples
were filtered to estimate the number of KEC and
K coli
present in collected waters
After 22 h incubation the most appropriate dilution was chosen and samples were
definitively analyzed
Bacterial Strains
Th e 32 reference strains from the Coleccioacuten Espantildeola de Cultivos Tipo (C EC T)
and 6 Salmonella strains from the Instituto de Hidrologiacutea y Medio Natural (IHMN)
stock culture collection used in this study are listed in Table 1 All strains except
Enterococcus strains were grow n and maintained on nutrient agar (M erck ) Th e
Enterococcus strains were grow n and maintained on brain heart agar (M erck)
Incubation Temperature Effect
Pure-culture studies were conducted with reference and IHMN strains
Bac teria we re resuspended in 5 ml of phosph ate buffer (APH A 1995) A loopfiil of th e
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E OLI
TABLE 1
Growth Conditions a t 37deg 41deg and 44 5degC of Different
Bacteria on Chromocult Coliform Agar
1233
Test Strain
Enterobacter aerogenes
Enterobacter cloacae
Enterobacter sakazakii
Enterobacter gergoviae
Klebsiella pneumoniae
Klebsiella oxytoca
Klebsiella ozaenae
Citrobacter diversus
Citrobacter amalonaticus
Citrobacter freundii
Escherichia coli
Hafnia alvei
Serratia odoriacutefera
Serratia marcescens
Serratia rubiadea
Cedecea davisae
Kluyvera ascorbata
Shigella flexneri
Shigella boydii
Shigella sonnei
Aeromonas hydrofila
Aeromonas caviae
Aeromonas media
A eromonas jandaei
Aeromonas schubertii
Aeromonas trota
Aeromonas eucrenophila
A
veronii bv veronii
Vibrio cholerae
Pseudomonas aeruginosa
Enterococcus faecalis
Enterococcusfaecium
Salmonella derby
S bredeney (4 strains)
Salmonella london
No
684
194
858
857
140
860
851
856
863
401
678
157
867
159
868
842
861
585
583
413
398
838
4232
4228
4241
4255
4224
4257
557
108
184
410
IHMN
IHMN
IHMN
37degC
G
b
C
c
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ c
+ t
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ r
+ r
+ r
+ c
-
-
+ c
+ t
+ t
41
G ~
+
+
+
+
+
+
+
+
+
+
+
+
+
+
-
+
+
+
+
+
+
+
+
-
+
+
+
+
+
-
-
+
+
+
degC
r
r
r
r
r
r
r
r
c
r
b
r
r
t
r
-
r
c
t
b
r
r
r
r
-
r
r
r
r
c
-
-
c
t
t
445degC
G C
+ r
+ r
+ r
-
+ c
+ r
+ r
+ c
+ c
+ r
+ b
+ r
+ r
+ r
+ r
-
+ r
+ c
+ t
+ b
-
-
+ r
-
-
-
-
-
+ c
-
-
+ c
+ t
+ t
No of reference strain from the CECT
G
Growth +=Good +=Weak -=None
b
C
Colour r=Salmon to Red b=Dark Blue to Violet t=Light Blue to Turquoise
c=Colourless
D o w n l o a d e d b y [ S o
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
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315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
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1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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J EN VIRON SCI HE ALTH A33(6) 12299830851248 (1998)
QU NTIT TIVE DETERMIN TION OF E COLI ND FEC L
COLIFORMS IN
W TER
USING CHROMOGENIC
M E I U M
Key Words Kcoli β 983085 galactosidase
β 983085 glucuronidase
water fecal coliforms
J L Alonso
1
A Soriano
2
I
Amoros
1
and MA
F e r rus
3
1
Inst i tu to
de Hidrologiacutea y Medio Natural Universidad Politeacutecnica Camino de Vera 14
46022 Valencia
2
Gamaser SL c Pedrapiquers 4 46014 Valencia
3
Departamento de Biotecnologiacutea Universidad Politecnica
Spain
STR CT
A new medium Chromocult Coliformreg Agar (CC agar) developed by E
Merck AG (Darmstadt Germany) was compared with the Standard Methods
membrane filtration fecal coliform (mFC) medium for fecal coliform detection and
enumeration In the CC agar non-E coli fecal coliforms (Klebsiella Enterobacter and
Citrobacter) (KEC) were identified by the production of a salmon to red colour from
p-galactosidase (LAC) cleavage of the substrate Salmon-GAL while E coli colonies
were detected by the blue colour produced by the cleavage of X-glucuronide by
β 983085
1229
Copyright copy 1998 by Marcel Dekker Inc wwwdekkercom
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1230 ALONSO ET AL
glucuronidase
G U S ) Statistically there was no significant differences between fecal
coliform counts obtained with the two media (CC agar and mFC agar) and two
incubation
procedures (2h983085 37degC plus 22h983085 445deg and 445degC) as determined by variance
analysis In our study K
coli
represented on average 705983085 925 of the fecal coliform
population A high incidence of
false
negative KEC (195 ) and
E
coli (296 )
colonies
was detected at 445degC Two
K
coli
GUS negative phenotype upon
reinoculation into CC agar were
G U S
+
A total of 31 KEC LAC colonies were
streaked on to
CC
agar and incubated at 37degC 29 KEC strains tha t failed to produce β 983085
galactosidase at 445degC were able to produce the enzyme at 37degC In our opinion the
physiological condition of the fecal coliform isolates could be responsible for the non983085
expression of P983085 galactosidase and P983085 glucuronidase activities at 445degC
INTRODUCTION
The
detection and enumeration of indicator organisms are of primary
importance
for the monitoring of sanitary and microbiological quality of water Fecal
coliforms have been long used as indicators of fecal contamination in water and food
The
term fecal coliform include all coliforms
tha t
can ferment lactose at 445degC trying
t o separate the non ubiquitous coliforms from those of true fecal origin (Dockins and
McFe t e r s 1978) The presence ofpound coli directly relates to fecal contamination with its
implied threat of the presence of enteric disease agents (Rice et al 1990) The other
members of the fecal coliform group Klebsiella Enterobacter and
Citrobacter)
may
be isolated in feces but their presence does not always suggest fecal contamination
D o w n l o a d e d b y [ S o
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QUANTITATIVE DETERMINATION OF E COLI 1231
(Covert et al 1992) The abbreviation KE C will be used in this study for the
designation of non-E coli fecal coliforms (Klebsiella Enterobacter and Citrobacter)
A major limitation of current membrane filtration methods used for counting
fecal coliforms is the enumeration of microorganisms which are not exclusively of fecal
origin thereby giving a false indication of the sanitary quality of the water
(Au goustinos et al 1993) Identification of pound coli in the past has been laborious and
only recently methods have been developed that detect
E coli
rapidly with accuracy
and specificity (Alonso et al 1996 Shadix et al 1993) The identification of coliforms
based on detection of P-galactosidase activity (Manafi et al 1991) is a significant
departure from methods that utilize the bacterial end products of lactose fermentation
(APHA 1995)
A new chromogenic medium Chromocult Coliformreg agar (CC agar) has been
developed by E Merck AG (Darmstadt Germany) to detect coliforms and K coli
simultaneously A combination o f tw o chrom ogenic glycosides is used for th e detection
of p-galactosidase (LAC) and P-glucuronidase (GUS) The Salmon-GAL substrate
causes a salmon to red colour of the KEC coliform colonies (LAC
+
GUS ) and the
substrate X-glucuronide is used for the identification of P-glucuronidase E coli
cleaves both Salmon-GAL and X-glucuronide so that positive colonies take on a dark
blue to violet colour (LA C
+
GUS)
In this study the CC agar was compared w ith the M-FC medium recommended
in Standard Methods (1995) for the enumeration of fecal coliforms by the membrane
filtration technique
D o w n l o a d e d b y [ S o
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i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1232 ALONSO ET AL
M A T E R I A L A N D M E T HOD S
Sampling
A total o f 40 w ater samples were collected from 6 different environmental
sources in the Valencia area The water samples were as follows 6 samples from the
Turia river near Valencia drinking water treatment plant (site TR) 11 samples from
two well water supplies (site PI 6 samples and site P2 5 samples) 8 samples from a
heavily polluted stream (site AP) 8 samples of seawater (salinity 21o) (Malvarrosa
beac h) influenced by sew age discharge (site M l ) and 7 samples of seawater from a
point located 200 m south of the previously mentioned sewage discharge (salinity
34o) (site M 2) All samples we re collected in sterile glass bo ttles refrigerated and
assayed within 24 h after collection Samples from sites TR A P M l and M 2 w ere
preassayed within 2 h to estimate bacterial density Several dilutions of these samples
were filtered to estimate the number of KEC and
K coli
present in collected waters
After 22 h incubation the most appropriate dilution was chosen and samples were
definitively analyzed
Bacterial Strains
Th e 32 reference strains from the Coleccioacuten Espantildeola de Cultivos Tipo (C EC T)
and 6 Salmonella strains from the Instituto de Hidrologiacutea y Medio Natural (IHMN)
stock culture collection used in this study are listed in Table 1 All strains except
Enterococcus strains were grow n and maintained on nutrient agar (M erck ) Th e
Enterococcus strains were grow n and maintained on brain heart agar (M erck)
Incubation Temperature Effect
Pure-culture studies were conducted with reference and IHMN strains
Bac teria we re resuspended in 5 ml of phosph ate buffer (APH A 1995) A loopfiil of th e
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QUANTITATIVE DETERMINATION OF E OLI
TABLE 1
Growth Conditions a t 37deg 41deg and 44 5degC of Different
Bacteria on Chromocult Coliform Agar
1233
Test Strain
Enterobacter aerogenes
Enterobacter cloacae
Enterobacter sakazakii
Enterobacter gergoviae
Klebsiella pneumoniae
Klebsiella oxytoca
Klebsiella ozaenae
Citrobacter diversus
Citrobacter amalonaticus
Citrobacter freundii
Escherichia coli
Hafnia alvei
Serratia odoriacutefera
Serratia marcescens
Serratia rubiadea
Cedecea davisae
Kluyvera ascorbata
Shigella flexneri
Shigella boydii
Shigella sonnei
Aeromonas hydrofila
Aeromonas caviae
Aeromonas media
A eromonas jandaei
Aeromonas schubertii
Aeromonas trota
Aeromonas eucrenophila
A
veronii bv veronii
Vibrio cholerae
Pseudomonas aeruginosa
Enterococcus faecalis
Enterococcusfaecium
Salmonella derby
S bredeney (4 strains)
Salmonella london
No
684
194
858
857
140
860
851
856
863
401
678
157
867
159
868
842
861
585
583
413
398
838
4232
4228
4241
4255
4224
4257
557
108
184
410
IHMN
IHMN
IHMN
37degC
G
b
C
c
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ c
+ t
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ r
+ r
+ r
+ c
-
-
+ c
+ t
+ t
41
G ~
+
+
+
+
+
+
+
+
+
+
+
+
+
+
-
+
+
+
+
+
+
+
+
-
+
+
+
+
+
-
-
+
+
+
degC
r
r
r
r
r
r
r
r
c
r
b
r
r
t
r
-
r
c
t
b
r
r
r
r
-
r
r
r
r
c
-
-
c
t
t
445degC
G C
+ r
+ r
+ r
-
+ c
+ r
+ r
+ c
+ c
+ r
+ b
+ r
+ r
+ r
+ r
-
+ r
+ c
+ t
+ b
-
-
+ r
-
-
-
-
-
+ c
-
-
+ c
+ t
+ t
No of reference strain from the CECT
G
Growth +=Good +=Weak -=None
b
C
Colour r=Salmon to Red b=Dark Blue to Violet t=Light Blue to Turquoise
c=Colourless
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
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7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
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(1994)
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Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
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Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
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Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
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Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
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Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
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2236-2243 (1996)
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Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
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1230 ALONSO ET AL
glucuronidase
G U S ) Statistically there was no significant differences between fecal
coliform counts obtained with the two media (CC agar and mFC agar) and two
incubation
procedures (2h983085 37degC plus 22h983085 445deg and 445degC) as determined by variance
analysis In our study K
coli
represented on average 705983085 925 of the fecal coliform
population A high incidence of
false
negative KEC (195 ) and
E
coli (296 )
colonies
was detected at 445degC Two
K
coli
GUS negative phenotype upon
reinoculation into CC agar were
G U S
+
A total of 31 KEC LAC colonies were
streaked on to
CC
agar and incubated at 37degC 29 KEC strains tha t failed to produce β 983085
galactosidase at 445degC were able to produce the enzyme at 37degC In our opinion the
physiological condition of the fecal coliform isolates could be responsible for the non983085
expression of P983085 galactosidase and P983085 glucuronidase activities at 445degC
INTRODUCTION
The
detection and enumeration of indicator organisms are of primary
importance
for the monitoring of sanitary and microbiological quality of water Fecal
coliforms have been long used as indicators of fecal contamination in water and food
The
term fecal coliform include all coliforms
tha t
can ferment lactose at 445degC trying
t o separate the non ubiquitous coliforms from those of true fecal origin (Dockins and
McFe t e r s 1978) The presence ofpound coli directly relates to fecal contamination with its
implied threat of the presence of enteric disease agents (Rice et al 1990) The other
members of the fecal coliform group Klebsiella Enterobacter and
Citrobacter)
may
be isolated in feces but their presence does not always suggest fecal contamination
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QUANTITATIVE DETERMINATION OF E COLI 1231
(Covert et al 1992) The abbreviation KE C will be used in this study for the
designation of non-E coli fecal coliforms (Klebsiella Enterobacter and Citrobacter)
A major limitation of current membrane filtration methods used for counting
fecal coliforms is the enumeration of microorganisms which are not exclusively of fecal
origin thereby giving a false indication of the sanitary quality of the water
(Au goustinos et al 1993) Identification of pound coli in the past has been laborious and
only recently methods have been developed that detect
E coli
rapidly with accuracy
and specificity (Alonso et al 1996 Shadix et al 1993) The identification of coliforms
based on detection of P-galactosidase activity (Manafi et al 1991) is a significant
departure from methods that utilize the bacterial end products of lactose fermentation
(APHA 1995)
A new chromogenic medium Chromocult Coliformreg agar (CC agar) has been
developed by E Merck AG (Darmstadt Germany) to detect coliforms and K coli
simultaneously A combination o f tw o chrom ogenic glycosides is used for th e detection
of p-galactosidase (LAC) and P-glucuronidase (GUS) The Salmon-GAL substrate
causes a salmon to red colour of the KEC coliform colonies (LAC
+
GUS ) and the
substrate X-glucuronide is used for the identification of P-glucuronidase E coli
cleaves both Salmon-GAL and X-glucuronide so that positive colonies take on a dark
blue to violet colour (LA C
+
GUS)
In this study the CC agar was compared w ith the M-FC medium recommended
in Standard Methods (1995) for the enumeration of fecal coliforms by the membrane
filtration technique
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1232 ALONSO ET AL
M A T E R I A L A N D M E T HOD S
Sampling
A total o f 40 w ater samples were collected from 6 different environmental
sources in the Valencia area The water samples were as follows 6 samples from the
Turia river near Valencia drinking water treatment plant (site TR) 11 samples from
two well water supplies (site PI 6 samples and site P2 5 samples) 8 samples from a
heavily polluted stream (site AP) 8 samples of seawater (salinity 21o) (Malvarrosa
beac h) influenced by sew age discharge (site M l ) and 7 samples of seawater from a
point located 200 m south of the previously mentioned sewage discharge (salinity
34o) (site M 2) All samples we re collected in sterile glass bo ttles refrigerated and
assayed within 24 h after collection Samples from sites TR A P M l and M 2 w ere
preassayed within 2 h to estimate bacterial density Several dilutions of these samples
were filtered to estimate the number of KEC and
K coli
present in collected waters
After 22 h incubation the most appropriate dilution was chosen and samples were
definitively analyzed
Bacterial Strains
Th e 32 reference strains from the Coleccioacuten Espantildeola de Cultivos Tipo (C EC T)
and 6 Salmonella strains from the Instituto de Hidrologiacutea y Medio Natural (IHMN)
stock culture collection used in this study are listed in Table 1 All strains except
Enterococcus strains were grow n and maintained on nutrient agar (M erck ) Th e
Enterococcus strains were grow n and maintained on brain heart agar (M erck)
Incubation Temperature Effect
Pure-culture studies were conducted with reference and IHMN strains
Bac teria we re resuspended in 5 ml of phosph ate buffer (APH A 1995) A loopfiil of th e
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QUANTITATIVE DETERMINATION OF E OLI
TABLE 1
Growth Conditions a t 37deg 41deg and 44 5degC of Different
Bacteria on Chromocult Coliform Agar
1233
Test Strain
Enterobacter aerogenes
Enterobacter cloacae
Enterobacter sakazakii
Enterobacter gergoviae
Klebsiella pneumoniae
Klebsiella oxytoca
Klebsiella ozaenae
Citrobacter diversus
Citrobacter amalonaticus
Citrobacter freundii
Escherichia coli
Hafnia alvei
Serratia odoriacutefera
Serratia marcescens
Serratia rubiadea
Cedecea davisae
Kluyvera ascorbata
Shigella flexneri
Shigella boydii
Shigella sonnei
Aeromonas hydrofila
Aeromonas caviae
Aeromonas media
A eromonas jandaei
Aeromonas schubertii
Aeromonas trota
Aeromonas eucrenophila
A
veronii bv veronii
Vibrio cholerae
Pseudomonas aeruginosa
Enterococcus faecalis
Enterococcusfaecium
Salmonella derby
S bredeney (4 strains)
Salmonella london
No
684
194
858
857
140
860
851
856
863
401
678
157
867
159
868
842
861
585
583
413
398
838
4232
4228
4241
4255
4224
4257
557
108
184
410
IHMN
IHMN
IHMN
37degC
G
b
C
c
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ c
+ t
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ r
+ r
+ r
+ c
-
-
+ c
+ t
+ t
41
G ~
+
+
+
+
+
+
+
+
+
+
+
+
+
+
-
+
+
+
+
+
+
+
+
-
+
+
+
+
+
-
-
+
+
+
degC
r
r
r
r
r
r
r
r
c
r
b
r
r
t
r
-
r
c
t
b
r
r
r
r
-
r
r
r
r
c
-
-
c
t
t
445degC
G C
+ r
+ r
+ r
-
+ c
+ r
+ r
+ c
+ c
+ r
+ b
+ r
+ r
+ r
+ r
-
+ r
+ c
+ t
+ b
-
-
+ r
-
-
-
-
-
+ c
-
-
+ c
+ t
+ t
No of reference strain from the CECT
G
Growth +=Good +=Weak -=None
b
C
Colour r=Salmon to Red b=Dark Blue to Violet t=Light Blue to Turquoise
c=Colourless
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
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315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1231
(Covert et al 1992) The abbreviation KE C will be used in this study for the
designation of non-E coli fecal coliforms (Klebsiella Enterobacter and Citrobacter)
A major limitation of current membrane filtration methods used for counting
fecal coliforms is the enumeration of microorganisms which are not exclusively of fecal
origin thereby giving a false indication of the sanitary quality of the water
(Au goustinos et al 1993) Identification of pound coli in the past has been laborious and
only recently methods have been developed that detect
E coli
rapidly with accuracy
and specificity (Alonso et al 1996 Shadix et al 1993) The identification of coliforms
based on detection of P-galactosidase activity (Manafi et al 1991) is a significant
departure from methods that utilize the bacterial end products of lactose fermentation
(APHA 1995)
A new chromogenic medium Chromocult Coliformreg agar (CC agar) has been
developed by E Merck AG (Darmstadt Germany) to detect coliforms and K coli
simultaneously A combination o f tw o chrom ogenic glycosides is used for th e detection
of p-galactosidase (LAC) and P-glucuronidase (GUS) The Salmon-GAL substrate
causes a salmon to red colour of the KEC coliform colonies (LAC
+
GUS ) and the
substrate X-glucuronide is used for the identification of P-glucuronidase E coli
cleaves both Salmon-GAL and X-glucuronide so that positive colonies take on a dark
blue to violet colour (LA C
+
GUS)
In this study the CC agar was compared w ith the M-FC medium recommended
in Standard Methods (1995) for the enumeration of fecal coliforms by the membrane
filtration technique
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1232 ALONSO ET AL
M A T E R I A L A N D M E T HOD S
Sampling
A total o f 40 w ater samples were collected from 6 different environmental
sources in the Valencia area The water samples were as follows 6 samples from the
Turia river near Valencia drinking water treatment plant (site TR) 11 samples from
two well water supplies (site PI 6 samples and site P2 5 samples) 8 samples from a
heavily polluted stream (site AP) 8 samples of seawater (salinity 21o) (Malvarrosa
beac h) influenced by sew age discharge (site M l ) and 7 samples of seawater from a
point located 200 m south of the previously mentioned sewage discharge (salinity
34o) (site M 2) All samples we re collected in sterile glass bo ttles refrigerated and
assayed within 24 h after collection Samples from sites TR A P M l and M 2 w ere
preassayed within 2 h to estimate bacterial density Several dilutions of these samples
were filtered to estimate the number of KEC and
K coli
present in collected waters
After 22 h incubation the most appropriate dilution was chosen and samples were
definitively analyzed
Bacterial Strains
Th e 32 reference strains from the Coleccioacuten Espantildeola de Cultivos Tipo (C EC T)
and 6 Salmonella strains from the Instituto de Hidrologiacutea y Medio Natural (IHMN)
stock culture collection used in this study are listed in Table 1 All strains except
Enterococcus strains were grow n and maintained on nutrient agar (M erck ) Th e
Enterococcus strains were grow n and maintained on brain heart agar (M erck)
Incubation Temperature Effect
Pure-culture studies were conducted with reference and IHMN strains
Bac teria we re resuspended in 5 ml of phosph ate buffer (APH A 1995) A loopfiil of th e
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E OLI
TABLE 1
Growth Conditions a t 37deg 41deg and 44 5degC of Different
Bacteria on Chromocult Coliform Agar
1233
Test Strain
Enterobacter aerogenes
Enterobacter cloacae
Enterobacter sakazakii
Enterobacter gergoviae
Klebsiella pneumoniae
Klebsiella oxytoca
Klebsiella ozaenae
Citrobacter diversus
Citrobacter amalonaticus
Citrobacter freundii
Escherichia coli
Hafnia alvei
Serratia odoriacutefera
Serratia marcescens
Serratia rubiadea
Cedecea davisae
Kluyvera ascorbata
Shigella flexneri
Shigella boydii
Shigella sonnei
Aeromonas hydrofila
Aeromonas caviae
Aeromonas media
A eromonas jandaei
Aeromonas schubertii
Aeromonas trota
Aeromonas eucrenophila
A
veronii bv veronii
Vibrio cholerae
Pseudomonas aeruginosa
Enterococcus faecalis
Enterococcusfaecium
Salmonella derby
S bredeney (4 strains)
Salmonella london
No
684
194
858
857
140
860
851
856
863
401
678
157
867
159
868
842
861
585
583
413
398
838
4232
4228
4241
4255
4224
4257
557
108
184
410
IHMN
IHMN
IHMN
37degC
G
b
C
c
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ c
+ t
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ r
+ r
+ r
+ c
-
-
+ c
+ t
+ t
41
G ~
+
+
+
+
+
+
+
+
+
+
+
+
+
+
-
+
+
+
+
+
+
+
+
-
+
+
+
+
+
-
-
+
+
+
degC
r
r
r
r
r
r
r
r
c
r
b
r
r
t
r
-
r
c
t
b
r
r
r
r
-
r
r
r
r
c
-
-
c
t
t
445degC
G C
+ r
+ r
+ r
-
+ c
+ r
+ r
+ c
+ c
+ r
+ b
+ r
+ r
+ r
+ r
-
+ r
+ c
+ t
+ b
-
-
+ r
-
-
-
-
-
+ c
-
-
+ c
+ t
+ t
No of reference strain from the CECT
G
Growth +=Good +=Weak -=None
b
C
Colour r=Salmon to Red b=Dark Blue to Violet t=Light Blue to Turquoise
c=Colourless
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
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315(1996)
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AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
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1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
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i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF
E COLI
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Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
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2684 (1988)
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Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
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for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
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w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
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Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
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E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1232 ALONSO ET AL
M A T E R I A L A N D M E T HOD S
Sampling
A total o f 40 w ater samples were collected from 6 different environmental
sources in the Valencia area The water samples were as follows 6 samples from the
Turia river near Valencia drinking water treatment plant (site TR) 11 samples from
two well water supplies (site PI 6 samples and site P2 5 samples) 8 samples from a
heavily polluted stream (site AP) 8 samples of seawater (salinity 21o) (Malvarrosa
beac h) influenced by sew age discharge (site M l ) and 7 samples of seawater from a
point located 200 m south of the previously mentioned sewage discharge (salinity
34o) (site M 2) All samples we re collected in sterile glass bo ttles refrigerated and
assayed within 24 h after collection Samples from sites TR A P M l and M 2 w ere
preassayed within 2 h to estimate bacterial density Several dilutions of these samples
were filtered to estimate the number of KEC and
K coli
present in collected waters
After 22 h incubation the most appropriate dilution was chosen and samples were
definitively analyzed
Bacterial Strains
Th e 32 reference strains from the Coleccioacuten Espantildeola de Cultivos Tipo (C EC T)
and 6 Salmonella strains from the Instituto de Hidrologiacutea y Medio Natural (IHMN)
stock culture collection used in this study are listed in Table 1 All strains except
Enterococcus strains were grow n and maintained on nutrient agar (M erck ) Th e
Enterococcus strains were grow n and maintained on brain heart agar (M erck)
Incubation Temperature Effect
Pure-culture studies were conducted with reference and IHMN strains
Bac teria we re resuspended in 5 ml of phosph ate buffer (APH A 1995) A loopfiil of th e
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E OLI
TABLE 1
Growth Conditions a t 37deg 41deg and 44 5degC of Different
Bacteria on Chromocult Coliform Agar
1233
Test Strain
Enterobacter aerogenes
Enterobacter cloacae
Enterobacter sakazakii
Enterobacter gergoviae
Klebsiella pneumoniae
Klebsiella oxytoca
Klebsiella ozaenae
Citrobacter diversus
Citrobacter amalonaticus
Citrobacter freundii
Escherichia coli
Hafnia alvei
Serratia odoriacutefera
Serratia marcescens
Serratia rubiadea
Cedecea davisae
Kluyvera ascorbata
Shigella flexneri
Shigella boydii
Shigella sonnei
Aeromonas hydrofila
Aeromonas caviae
Aeromonas media
A eromonas jandaei
Aeromonas schubertii
Aeromonas trota
Aeromonas eucrenophila
A
veronii bv veronii
Vibrio cholerae
Pseudomonas aeruginosa
Enterococcus faecalis
Enterococcusfaecium
Salmonella derby
S bredeney (4 strains)
Salmonella london
No
684
194
858
857
140
860
851
856
863
401
678
157
867
159
868
842
861
585
583
413
398
838
4232
4228
4241
4255
4224
4257
557
108
184
410
IHMN
IHMN
IHMN
37degC
G
b
C
c
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ c
+ t
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ r
+ r
+ r
+ c
-
-
+ c
+ t
+ t
41
G ~
+
+
+
+
+
+
+
+
+
+
+
+
+
+
-
+
+
+
+
+
+
+
+
-
+
+
+
+
+
-
-
+
+
+
degC
r
r
r
r
r
r
r
r
c
r
b
r
r
t
r
-
r
c
t
b
r
r
r
r
-
r
r
r
r
c
-
-
c
t
t
445degC
G C
+ r
+ r
+ r
-
+ c
+ r
+ r
+ c
+ c
+ r
+ b
+ r
+ r
+ r
+ r
-
+ r
+ c
+ t
+ b
-
-
+ r
-
-
-
-
-
+ c
-
-
+ c
+ t
+ t
No of reference strain from the CECT
G
Growth +=Good +=Weak -=None
b
C
Colour r=Salmon to Red b=Dark Blue to Violet t=Light Blue to Turquoise
c=Colourless
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
D o w n l o a d e d b y [ S o
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i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
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315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
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1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
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1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
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Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
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Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E OLI
TABLE 1
Growth Conditions a t 37deg 41deg and 44 5degC of Different
Bacteria on Chromocult Coliform Agar
1233
Test Strain
Enterobacter aerogenes
Enterobacter cloacae
Enterobacter sakazakii
Enterobacter gergoviae
Klebsiella pneumoniae
Klebsiella oxytoca
Klebsiella ozaenae
Citrobacter diversus
Citrobacter amalonaticus
Citrobacter freundii
Escherichia coli
Hafnia alvei
Serratia odoriacutefera
Serratia marcescens
Serratia rubiadea
Cedecea davisae
Kluyvera ascorbata
Shigella flexneri
Shigella boydii
Shigella sonnei
Aeromonas hydrofila
Aeromonas caviae
Aeromonas media
A eromonas jandaei
Aeromonas schubertii
Aeromonas trota
Aeromonas eucrenophila
A
veronii bv veronii
Vibrio cholerae
Pseudomonas aeruginosa
Enterococcus faecalis
Enterococcusfaecium
Salmonella derby
S bredeney (4 strains)
Salmonella london
No
684
194
858
857
140
860
851
856
863
401
678
157
867
159
868
842
861
585
583
413
398
838
4232
4228
4241
4255
4224
4257
557
108
184
410
IHMN
IHMN
IHMN
37degC
G
b
C
c
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ r
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ c
+ t
+ b
+ r
+ r
+ r
+ r
+ c
+ r
+ r
+ r
+ r
+ c
-
-
+ c
+ t
+ t
41
G ~
+
+
+
+
+
+
+
+
+
+
+
+
+
+
-
+
+
+
+
+
+
+
+
-
+
+
+
+
+
-
-
+
+
+
degC
r
r
r
r
r
r
r
r
c
r
b
r
r
t
r
-
r
c
t
b
r
r
r
r
-
r
r
r
r
c
-
-
c
t
t
445degC
G C
+ r
+ r
+ r
-
+ c
+ r
+ r
+ c
+ c
+ r
+ b
+ r
+ r
+ r
+ r
-
+ r
+ c
+ t
+ b
-
-
+ r
-
-
-
-
-
+ c
-
-
+ c
+ t
+ t
No of reference strain from the CECT
G
Growth +=Good +=Weak -=None
b
C
Colour r=Salmon to Red b=Dark Blue to Violet t=Light Blue to Turquoise
c=Colourless
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
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7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
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Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
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i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
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1234 ALONSO ET AL
phosphate buffer culture was streaked onto CC agar plates and incubated at three
different incubation temperatures (37degC 41degC and 445degC) After growth was
observed the P-galactosidase and p-glucuronidase activities of 32 reference strains and
6 Salmonella strains w ere tested
Microbiological Analysis
Samples were decimal diluted or concentrated according to the expected
bacterial density as above described Duplicates of each sample dilution were filtered
through sterile 045 urn pore size membranes (Whatman) using the standard membrane
filtration technique The membranes were placed onto a pre-prepared layer of CC agar
in a 47-mm petri-dish These were then incubated at 445degC in a water bath for 24 h
All salmon to red colonies (LAC
+
GUS ) were counted as presumptive KEC coliforms
and all blue to violet colonies (LAC GUS) were counted as presumptive
K coli
For
comparison the second duplicate membrane of each pair was processed by a standard
method for fecal coliforms The membranes were layered onto M-FC agar (Merck) and
incubated at 445degC in a water bath for 24 h All blue colonies were counted as fecal
coliforms (APHA 1995) Rosolic acid from M-FC medium was eliminated as
suggested by Presswood and Strong (1978) These authors observed that eliminating
rosolic acid from M-FC medium improves the M-FC procedure by allowing higher
fecal coliform colony recoveries
In the modified method the membranes were placed on CC agar and M-FC
agar and were incubated at 37degC for 2 h before incubation at 445degC in a water bath
for 22-2 4 h Ro se et al (1975) suggested the need for a repair phase prior to incubation
at the elevated temperature
D o w n l o a d e d b y [ S o
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
D o w n l o a d e d b y [ S o
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
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1 5
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
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i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
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315(1996)
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edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
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Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
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i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1235
A total number of 587 colonies from the most appropriate dilution of CC agar
were submitted to qualitative analysis For each sample site salmon to red colonies
(LAC
+
GUSO dark blue to violet colonies (LAC GUS
4
) light blue to tu rquo ise (LAC
GUS) and colourless colonies (LAC GUS ) were randomly picked and subcultured on
nutrient agar (Merck) Purified cultures were further identified by the following cultural
characteristics indole production growth on Simmons citrate agar (Merck) methyl
red and Voges-Proskauer reactions gas production in EC broth (Merck) reaction on
triple sugar iron agar (TSI) (Merck) and possesion of cytochrome oxidase and
catalase A total number o f 66 isolates were further identified using the A PI 20 E
system (bioMerieux)
Statistical Analysis
Bacterial counts were logarithmically transformed prior to statistical treatment
Results were analyzed by linear regression to verify the linearity of the relationship
between E coli and KEC coliforms obtained with CC agar To examine the medium
performance (CC agar) over a range of sample types and concentrations the samples
w ere groupe d by sample site by E coli and KEC coliform counts on CC agar by fecal
coliform counts on mFC agar and by incubation temperatures A unifactorial variance
analysis was performed on the means of the data All statistics were obtained using
Statgraphics software
RESULTS AND DISCUSSION
E coli and K E C cou nts on CC agar and fecal coliform coun ts on mF C aga r at
two incubation procedures are compared in Table 2 In this study E coli was isolated
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
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7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
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336-344 (1992)
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(1994)
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1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF
E COLI
1247
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207-214 (1991)
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D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
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for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
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Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1236 ALONSO ET AL
TABLE 2
N o n - pound
coli
Fecal Coliforms
Klebsiella
spp
Enterobacter
spp and
Citrobacter
spp) KE C ) and
Escherich ia coli
Recovered on Ch romocult Coliform Ag ar
(C C aga r) and Fecal Coliform s Recovered on M FC Agar
Sampling
source
TR
EC-CCA
b
KEC-CCA
C
EKEC-CCA
d
F C - m F C
PI
EC-CCA
KEC-CCA
EKEC-CCA
FC-mFC
AP
E C - C C A
K E C - C C A
EKEC-CCA
FC-mFC
M l
EC-CCA
K E C - C C A
EKEC-CCA
FC-mFC
M2
EC-CCA
K E C - C C A
E K E C - C C A
FC-mFC
Mean
215
197
239
245
195
081
150
168
672
596
679
673
535
451
541
536
307
253
318
313
2h37deg-445degC
SD
151
163
156
167
062
025
080
071
020
014
019
019
124
112
122
125
093
083
091
098
Min
070
030
085
085
111
048
048
060
646
578
656
652
338
270
346
336
208
154
220
208
Max
408
420
445
461
258
108
259
262
700
623
705
703
672
570
676
671
448
370
454
462
Mean
287
264
237
241
179
060
161
161
671
582
676
673
532
439
537
536
300
240
311
307
445
SD
141
148
157
158
055
026
072
077
019
016
018
019
122
129
123
123
102
085
098
101
degC
Min
158
100
078
104
118
030
048
048
651
560
657
652
338
230
341
338
194
140
205
181
Max
426
420
453
448
250
095
250
256
699
611
703
704
669
604
678
668
457
378
463
458
Data are reported as log values per 100 ml The results are expressed as
arithmetic mean (M ean) standard deviation (SD ) minimum (Min)
and maximum (Max)
EC-CCA = Escherichia coli (LAC GUS) recovered on C C agar
K E C-C C A = N o n - pound coli fecal coliforms (LAC
+
GUS ) recovered on CC agar
d
EKEC-CCA = E coli and non-Ecoli fecal coliforms recove red on CC agar
T C -m F C = Fecal coliforms recovered o n mFC agar
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
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AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
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i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
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336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1237
from all of the six zones analyzed but at different densities (Table 2) The data of site
P2 were not reported because of low number of samplings with positive results The
highest levels of E coli w ere detected at sites AP and M l with densities up to 10
s
CFU100 ml These zones also showed high numbers of KEC coliforms Table 3
summarizes the values of the correlation coefficients (r) and the confidence levels (P)
obtained b etween th e concentrations of K coli and KE C At site P2 the presence of E
coli (1 CFU100 ml) was detected only in four samples and it was not included in the
statistical analysis Positive correlations (Plt001) were found at sites TR M l and M 2
Th ere was no correlation at sites P I and AP Counts of E coli and KEC on CC agar
were compared with fecal coliform counts on mFC agar Statistically there was no
significant differences between coliform counts obtained with the two media (CC agar
and mF C agar) and two incubation procedures (2h-37degC plus 22h-445degC and 4 45degC )
as determined by variance analysis ANOVA on the K coli data at two incubation
procedures of CC agar indicated no significant differences among incubation
proc edu res K EC coliforms represented on average 79-2 95 of the fecal coliform
popu lation Figueras et al (1994 ) demonstrated the low specificity o f mF C m edium for
the enum eration and detection of fecal coliforms from seawater on th e basis of the high
incidence of false positive colonies (thermotolerant non-fecal coliforms) Many authors
(Caplenas and Ka narek 1984 Charriere et al 1992 Dufour 1977 Evison 1988)
consider tha t the adjective fecal is no t properly applied and questioned the usefulness
of fecal coliforms other than E coli as fecal indicators We agree with other authors
(Brodsky 1997 Mossel 1997) that in order to provide more comparative results the
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
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315(1996)
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AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
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1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
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336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
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Microbiol 57 1528-1534(1991)
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Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
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Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
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E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1238
ALONSO ET AL
T A B L E 3
Regression an d Correlation Parameters from Data O btained Us ing Chrom ocu lt
Coli form Agar CC Agar)
Sample
site
T R
P I
AP
M l
M 2
Parameters
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
EC37-KEC37
EC44-KEC44
R
099
098
069
064
068
040
099
099
099
098
P
lt001
lt001
N S
b
N S
N S
N S
lt001
lt001
lt001
lt001
Intercept
(a)
0340
0405
0571
1729
0977
3981
0419
1185
0257
0170
Slope
(b )
0916
0936
1701
0108
0963
0468
1093
0941
1112
0182
a
EC37-FC37=poundscOTc7ij coli and non-pound coli fecal coliforms (Klebsiella
Enterobacier and Citrobacter) (KEC) recovered on CC agar (2h 37deg-445degC) EC44-
FC44=pound coli and non-pound coli fecal coliforms recovered on CC agar (445deg C)
^ 5 = ^ 1 significant
term fecal coliform should be revised and replaced with the more definitive fecal index
organism Escherichia coli
The p-galactosidase and P-glucuronidase activities of 32 reference strains and 6
Salmonella strains at 37degC 41degC and 445degC are show n in Table 1 Th e ability to
produce p-galactosidase of Klebsiella pneumoniae Citrobacter diversus and C
amalonaticus strains on CC agar was inhibited at 445degC The grow th o f Aeromonas
reference strains was inhibited at 445degC except in the case of
Aeromonas jandaei
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1522
TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
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315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
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D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1239
Salmonella bredeney (4 strains) and S london showed P-glucuronidase activity at the
three temperatures tested
The identities of the four types of colonies (LAC
+
G U S L A C
+
G U S
+
LAC
GUS and L A C GUS ) on C C agar are shown in Table 4 The identity of 66 isolates
was verified with the API 20E system (Table 5) The KEC LAC
+
GUD species
identified were Klebsiella oxytoca (2 strains) K pneumoniae (2 strains) Enierobader
cloacae (4 strains) Citrobacterfreundii (6 strains) and C amalona ticus (1 strain)
Of the 212 blue colonies (LAC
+
GUS
4
) 207 (98 ) were confirmed as E coli
giving a false positive rate of 2 (5 o f 212 colonies) A total of 9 L A C G U S colonies
15 L A C G U S
+
colonies and 8 7 LA C
+
G US were E coli resulting in a false negative
rate of 296 (111 of 375 colonies) Covert et al (1992) reported that the false-
negative rates with natural populations of E coli ranged from 186 with the
Coliquikreg test (C L) t o 23 4 with the Colilertreg test (C L) (these enzyme detection tests
contains the fluorogenic substrate 4-methylumbelliferyl-P-D-glucuronide M U G )
Ciebin et al (199 5) enco untered a lower incidence of P-glucuronidase-negative E Coli
isolates with river (98 and 93) and lake (78 and 88) samples with FC-BCIG and
TEC-BCIG media (m-FC and m-TEC media supplemented with the chromogenic
substrate 5-bromo-6-chloro-3-indolyl-P-D-gIucuronide BCIG) respectively Two E
coli GUS negative phenotype at 445degC were incubated on CC agar at 37degC to
determine whether the expression of GU S formation was temperature dependent Bo th
E coli strains showed GUS production at 37degC Alonso et al (1996) found that false
negative K coli G U S colonies occurred less frequently at 35degC than at 445 degC S everal
auth ors (C lark et al 1 991 Cov ert et al 1992 Palmer et al 1995) showed that som e
M U G negative Ecoli isolates regained the M U G phenotype upo n further culture O ne
mechanism that could cause GUS negative phenotype would be failure of the permease
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1522
TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1622
1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
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QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1822
1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1922
QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1422
24
ALONSO ET AL
TABLE 4
Num ber o f
coli
a nd N o n-E
coli
Fecal Coliforms Isolates G row n on C C Aga r
Identified on the Basis of IMV IC Cytochrom e O xidase Catalase and TSI Ag ar
Reactions
Phenotype
LAC GUS
AP
C
M l
M 2
TR
PI
P2
Total
LAC
+
GUS
+
AP
M l
M 2
T R
PI
P2
Total
LACGUS
A P
M l
M 2
T R
P I
P2
Total
LAC GUS-
A P
M l
M2
TR
PI
P2
Total
Isolates
N o
37
31
42
41
31
11
193
24
29
48
48
52
11
212
2
9
0
3
2
0
16
17
23
15
36
46
29
166
E
N o
14
10
25
19
18
1
87
24
27
48
46
52
10
207
2
8
0
3
2
0
15
0
2
1
5
1
0
9
coli
( )
38
32
59
46
58
9
45
100
93
100
96
100
91
98
100
89
0
100
100
0
94
0
9
7
14
2
0
5
K E C
No
23
20
17
17
8
1
86
0
2
0
2
0
1
5
0
1
0
0
0
0
1
17
20
12
14
6
2
71
( )
62
68
41
42
26
9
45
0
7
0
4
0
9
2
0
11
0
0
0
0
6
100
87
80
39
13
7
43
Non
coliform
b
No
0
0
0
0
3
5
8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
2
12
22
10
47
( )
0
0
0
0
10
46
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4
13
33
48
34
28
N ot
identified
No
0
1
0
5
2
4
12
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
17
17
39
( )
0
3
0
12
6
36
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
14
37
59
24
KEC
Klebsiella Enterobacter and Citrobacter
b
Oxidase + P seudomonas spp Vibrio spp Aeromonas spp
Sampling sites
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1522
TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1622
1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1722
QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1822
1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1922
QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1522
TAB LE 5
Identif ication o f Colonies Picked from C C Agar Using the A PI 20E System
O
m
sect
o
L A C
+
G U S
N o
L A C
+
G U S N o L A C G U S
4
N o L A C G U S -
No
Enterobacter cloacae
Klebsiella oxytoca
K Pneuntoniae
Citrobacterfreundii
C Amalonaticus
Escherichia coli
4
2
2
6
1
6
pound co
Cfreundii
8
1
ot l
E co
21
Pseudomonas
spp
P fluorescens
Acinetobacter
spp
Flavobacterium
spp
Proteus
spp
Salmonella typhi
Citrobacterfreundii
C amalonaticus
Klebsiella oxytoca
K pneumoniae
Enterobacter cloacae
E agglomerans
E sakazakii
Escherichia coli
4
1
1
1
1
1
8
1
4
2
3
1
1
4
33
a
LA C
+
G US salmon to red colonies
bull LAC GU S
+
dark-blue to violet colonies
l A C
G US
+
light-blue to turquoise colonies
d
L AC GU S colourless colonies D o
w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1622
1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1722
QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1822
1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1922
QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1622
1242 ALONSO ET AL
to transport the glucuronide substrate across the cell membrane (Coyne and Schuler
1994) Som e authors (Bej et al 1 991 Cleuziat and Rob ert-Baud oy 1990 Fen g et al
1991
Flicker and Flicker 1994 Green et al 19 91 M artins et al 199 3
Venkateswaran et al 1996) observed that part of the genetic sequences of the uidA
gene which encodes for the GUS enzyme was present in most if not all E coli
isolates regardless of the GUS phenotype Frampton and Restaino (1993) indicated
that the following factors may influence the GUS assay substantially whichever GUS
detection system is used strain differences in response to particular substrates and
substrate concentration effects of carbohydrate content and selective agents in the
medium incubation time and temperature pH changes ionic strength effects and
possible interference by large numbers of competing bacteria or substances in the
sample
itself
W e have isolated one strain of Citrobacter freundii LAC
+
G U S
+
Although P-glucuronidase activity has been reported in some strains of coliforms
(Enterobacter agg lomerans E cloacae E amnig enus C itrobacter freundii C
amalonaticus Escherichia vulneris and Hqfnia alvet) Aeromonas sp and
Acinetobacter sp (Heizmann 1988 Kaacutempfer et al 199 1 Perez et al 1986 Sartory y
Howard 1992 Watkins et al 1988) their occurrence appears to be very infrequent
(Sartory and Howard 1992) The reason for the production of p-glucuronidase by
these strains is not know n but o ther investigators (Brenner et al 1993) have sugge sted
tha t the reaction ma y be plasmid mediated
The specificity of the medium for KEC coliforms was low Of the 193 salmon to
red colonies (LAC
+
GUS ) 86 (45) were confirmed as KEC coliforms giving a false
positive rate of 5 5 (127 of 193 colonies) A total of
7
LAC GUS colonies 1 LAC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1722
QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1822
1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1922
QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1722
QUANTITATIVE DETERMINATION OF E COLI 1243
G U S
+
colony and 5 LAC
+
GUS
+
colonies were KEC coliforms resulting in a false
negative rate of 195 (77 of 394 colonies) A high incidence of false negative (L A C )
KEC colonies was detected Because enzyme activities are subject to the physiological
status o f the bacteria a variable fraction of the coliform bacteria m ay be stressed wh en
changes in irradiation salinity temperature and nutrient concentration of the
environment occur (Pommepuy et al 1992) Fecal coliform bacteria comprise several
bacterial species and their response to environmental factors may not be the same for
each species (Pommepuy et al 1996) In treated drinking water injured coliforms can
comprise between 50 and gt90 of coliforms present (McFeters 1989) A total of 31
L A C G U S colonies were streaked onto CC agar and incubated at 37degC 29 K EC
strains that failed to produce P-galactosidase at 445degC were able to produce the
enzyme at 37degC Dockins and McFeters (1978) observed that optimal activity of 0-
galactosidase enzyme in freshly sonic extracts fecal coliforms typically occurred at
30+2degC and the activity decreased rapidly as the temperature increased above 35 to
38degC At 445degC fecal P-galactosidase activity was 25 to 50 of the optimal
tem peratu re (D ockins and M cFeters 1978) This decrease in p-galactosidase activity in
fecal coliforms has been indirectly observed by Warren et al (Warren et al 1976) who
found that lowering the 445degC incubation temperature by 1 or 2degC resulted in
significantly faster rate of ONPG hydrolysis Munro et al (1987) observed that P-
galactosidase activity of pound coli starved cells disappeared gradually with time The
physiological condition of KEC isolates could be responsible for the non-expression of
enzym e activity at 445degC
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1822
1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1922
QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1822
1244 ALONSO ET AL
When LAC
+
GUS LAC
+
GUS
+
and LAC GUS colonies were considered as
fecal coliforms (included E coli) more than 95 (401 of 421 colonies) of the
identified colonies belonged to the fecal coliform group giving a false positive rate of
4 8 (20 of 421 colonies) Nevertheless LAC GUS colonies represented 481 (80
of 166 colonies) of the identified coliform gro up
Results of the study indicated that 94 (205 of 219 colonies) of the E coli
LAC
+
GUS strains produced gas in the EC medium (Table 6) Thermotolerant E coli
was the most frequently isolated in the 6 environmental conditions as expected
Ho we ver the percentage was variably ranging from 8 2 (P2) to 100 (AP ) A total
of 219 E coli strains (LAC
+
GUS) were verified in EC broth and 12 (5) gas
negative strains were encountered In EC broth K coli must transport lactose throug h
the cell membrane transform the substrate to glucose metabolize glucose through the
glycolytic cycle to pyruvate and then convert pyruvate to the desired end prod uct
either acid or gas (Edberg et al 1988) Because lactose fermentation at 445degC is
determined by a complex of different enzymes a number of anomalous results may
occur such as false negative gas production (Edberg et al 1988 Gtammanco et al
1992)
Leclerc et al (1977) observed that the activity of formic h ydrogen lyase which
is needed for gas production from lactose is quite often reduced and sometimes
entirely suppressed under conditions that do not favour survival of coliforms in water
Munro et al (1987) suggested that the disappearance of P-galactosidase activity in
non-salt adapted
E coli
cells starved in seawater could have implications for their
enumeration by standard cultural methods all of which being grounded on the
acidification and fermentation of lactose
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1922
QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 1922
QUANTITATIVE DETERMINATION OF E COLI 1245
TABLEOacute
Percentage of Thermotolerant ThermosensUive and iacutendo le Negative
K coli
LAC GUS) Strains Recovered in C C A ga r
Sampling
sites
AP
M l
M2
TR
PI
P2
N o of
strains
24
30
53
46
55
11
Thermo-
tolerant
No
24
28
51
42
51
9
100
93
96
91
93
82
Thermo-
sensitive
b
No
0
2
2
4
3
12
0
7
4
9
5
5
Indol-
No
0
2
3
2
1
9
0
7
6
4
2
4
Therm otolerant gas formed from lactose a 1445degC
k
Therm osensitive gas not formed from lactose at 445degC
The data obtained suggested that specificity of CC agar for fecal coliforms was
related to the incubation temperature and we are of the opinion that lowering the
445 degC incubation temp erature to 41degC may reverse the expression of P-galactosidase
and P-glucuron idase activities of som e metabolically injured fecal co liforms
REFERENCES
Alonso JL Amoros I Chong S and Garelick H J Microbiol Methods 25 309-
315(1996)
AP HA Standard Metho ds for the Examination of W ater and W astewater 19th
edition Am erican Public Health Association N ew Y ork (1995 ) 9 pp
1-117
Augo ustinos MT Grabow NA and Kfir R W at Sci Tech 27 267-270 (1993)
Bej
AK McCarty SC and Atlas RM Appl Environ Microbiol 57 2429-2432
(1991)
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2022
1246 ALONSO ET AL
Brenner KP Rankin CC Roybal YR and Stelma JrG Appl Environ
M icrobiol 59 3534-3544 (1993)
Brodsky MH A SM N ews 63 345-346 (1997)
Caplenas NR and Kanarek MS Am J Publ Hlth 74 1273-1275 (1984)
Charriere G Mossel DAA Beaudeau P and Leclerc H J Appl Bacteriol 76
336-344 (1992)
Ciebin BW Brod sky MH Edding ton R Horsnell G Choney A Palmateer G
Ley A Joshi R and Shears G Appl Environ M icrobiol 6 1 3940-3942 (1995)
Clark DL Milner BB Stewart MH Wolfe RL and Olson BH Appl Environ
Microbiol 57 1528-1534(1991)
Cleuziat P and Robert-Baudoy J FEMS Microbiol Lett 72 315-322 (1990)
Cov ert TC Rice EW Johnson SA B erman D Johnson CH and Mason PJ
J A W W A 84 98-104 (1992)
Coy ne M S and Schuler J C J Environ Qu al 2 3 126-129 (1994 )
Do ckins W S and M cFeters GA Appl Environ Microbiol 36 341-348 (1978 )
Dufour A P Bacterial IndicatorsHealth Haz ards Associated with W ater Ed AW
Ho adley and BJ Dutka American Society for Testmg M aterials Philadelphia (197 7)
pp 48-58
Edberg SC Allen M J Smith D B and the National Collaborative Study Appl
Environ Microbiol 54 1595-1601 (1988)
Evison LM Wat Sci Tech 20 309-315 (1988)
Feng P Lum R and Chang G W Appl Environ M icrobiol 5 7 320-323 (1991)
Figueras M J Po lo F Inza I and Guarro J Lett Appl M icrobiol 19 446-450
(1994)
Frampton EW and Restaino L J Appl Ba cterio l 74 223 -233
Fricker EJ and Fricker CR Lett Appl M icrobiol 19 44-46 (199 4)
Giammanco G Pignato S and Biondi M Zbl H y g 193 99-105 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2122
QUANTITATIVE DETERMINATION OF
E COLI
1247
Green DH Lewis GD Rodtong S and Loutit MW J Microbiol Methods 13
207-214 (1991)
Heizmann W Doumlller P C Guumltbrod B and W erner H J Clin Microbiol 26 268 2-
2684 (1988)
Kampfer P
Rauhoff
D and D ott W J Clin M icrobiol 29 2877-28 79 (1 991 )
Lec lerc H M ossel D A A Trinel PA and Gavini F Bacterial IndicatorsHealth
Haza rd A ssociated with Water Ed AW Hoadley and BJ Dutka Am erican Society
for Testing M aterials Philadelphia (1977) pp 22 -36
Manafi M Kneifel W and Bascomb S Microbiol R e v 55 335-348 (1991)
M artins M T Rivera IG Clark D L Stewart M H W olfe RL and Olsen B H
Appl Environ M icrob iol 5 9 2271-2276 (199 3)
M cFe ters G A Injured index and pathogenic bacteria occurrence and detection in
foods
w ater and feeds Ed B Ray CRC Press Bo ca Raton (1989) pp 179-210
Mossel D A A A SM New s 63 175 (1997)
M un ro P M Gauthier MJ and Laumond F M Appl Environ Micro biol 53
1476-1481 (1987)
Palmer C J Tsai Y L ang AL and Sangermano L R A ppl Environ M icrob iol
59 786-790(1995)
Perez J L Berrocal CI and Berrocal L J Appl Ba cteriol 6 1 541-545 (19 86)
Pom mepuy M Guillard J F Duprey E D errien A Le Guyader F and Cormier
M W at Sci T ec h 2 5 93-103 (1992)
Pomm epuy M Fiksdal L Gourmelon M M elikechi H Caprais M P Cormier
M and Colwell RR J Appl Ba cterio l 8 1 174-180 (1996)
Pressw ood W G and Strong D K A ppl Environ M icrobiol 36 90-94 (1978 )
Rice
E W Allen MJ and Edberg SC Appl Environ M icrob iol 56 1203-1205
(1990)
Ro se R E Geldreich EE and Litsky W Appl M icrobiol 29 532-536 (1975)
Sartory DP and How ard L Lett Appl M icrobiol 15 273-276 (1992)
D o w n l o a d e d b y [ S o
u t h e r n I l l i n o i s U n i v e r s i t y ] a t 2 1 0 5 1 8 J u l y 2 0 1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5
7232019 Alonso 1998 Quantitative determination of e coli and fecal coliforms in water using a chromogenic mediumpdf
httpslidepdfcomreaderfullalonso-1998-quantitative-determination-of-e-coli-and-fecal-coliforms-in 2222
1248 ALONSO ET AL
Shadix LC Dunnigan M E and Rice E W Can J M icrobiol 39 1066-1070
(1993)
Venkateswaran K Murakoshi A and Satake M Appl Environ Microbiol 62
2236-2243 (1996)
Warren LS Benoit RE and Jessee JA Appl Environ Microbiol 35 136-141
(1976)
Watkins WD Rippey SR Clavet CR Kelley-Reitz D J and Burkhardt W
Appl Environ Microbiol 54 1874-1875 (1988)
e c e i v e d
December
22 1997
D o w n l o a d e d b y [ S o u t h e r n I l l i n o i s U n i v e r s
i t y ] a t 2 1 0 5 1 8 J u l y 2 0
1 5