Transcript
Page 1: Potential Impacts of Antibiotics in the Environment

Potential Impacts of Potential Impacts of Antibiotics in the Antibiotics in the

EnvironmentEnvironmentAmy Pruden

Assistant Professor, Civil Engineering, Colorado State

UniversityR1

OH O OH

R3 R4

OHO

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CONH2

R2

12

3

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Page 2: Potential Impacts of Antibiotics in the Environment

OverviewOverview

• Agricultural Antibiotics• Overview of potential impacts• Why study resistance genes?• Poudre River Study• Conclusions• Recommendations

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Agricultural AntibioticsAgricultural Antibiotics

• More than ½ used in U.S. Animals• Subtherapeutic use promotes weight

gain.• Animal waste > 130 x human waste

– (United States Senate Committee on Agriculture, 1997)

• Antibiotics can be excreted unaltered.

• Animal Waste Treatment??

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Antibiotic PathwaysAntibiotic Pathways

Modified from www.usda.gov

Page 5: Potential Impacts of Antibiotics in the Environment

Antibiotics Antibiotics Used:Used:

• Tetracyclines– Chlortet., oxytet.,

tet. ..

• Sulfonamides• Macrolides

– Tylosin, erythromycin..

• Ionophores– Monensin..

-lactams Penicilillin

R1

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R3 R4

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OH

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R2

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CH3 H

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Erythromycin (Ery)

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CH3 H

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N-O-CH2-O-CH2-CH2-OCH3

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Roxithromycin (Rox)

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Tylosin (Tyl)

Tetracylcline (Tet)

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Public ConcernPublic Concern

Page 7: Potential Impacts of Antibiotics in the Environment

Potential ImpactsPotential Impacts

• Toxicity to Aquatic life (H. Ramsdell, CSU)– Planaria, flathead minnow, and Hyalella– Chlortetracycline, tylosin, sulfamethazine,

metronidizine, monensin and lyolocid showed toxicity

– Monensin strong toxicity and widespread use• LD50 = 5 ppm in water for minnows• LD50 = 20 ppm in sediment for Planaria• LD50 = 1 ppm in water for Hyalella

– Sublethal effects?

Page 8: Potential Impacts of Antibiotics in the Environment

Potential ImpactsPotential Impacts

• Sub-lethal impacts: Endocrine disruptors– Micropollutants not

removed by wastewater treatment

– May cause hermaphroditism

– Effects on frogs– Fish in Chesapeake Bay

Sower et al., Env. Health Perspect. 2000

Page 9: Potential Impacts of Antibiotics in the Environment

Potential ImpactsPotential Impacts

• Plant Uptake– Antibiotic uptake by plants from soil

fertilized with animal manure- Kumara et al. U. Minn.

• J Environ Qual (2005)

– Greenhouse studies: corn, green onion, & cabbage

– Uptake of chlortetracycline, but not tylosin• Low: 2 – 17 ng/g, but correlates with manure

concentration

– Implications for allergic individuals

Page 10: Potential Impacts of Antibiotics in the Environment

Antibiotic Resistance Genes Antibiotic Resistance Genes (ARG)(ARG)

• Spread of ARG one of most urgent human health issues according to WHO

• Use of antibiotics selects for antibiotic resistant organisms– Shea, 2003; Fedorka-Cray et al., 2002; Smith

et al., 2002; Sørum and L’Abée-Lund, 2002; Teuber, 2001.

• Can be spread across microbial populations and in the environment– ARG as “pollutants”

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Resistance Gene TransferResistance Gene Transfer

ASM News November, 2004ASM News November, 2004

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Antibiotic Resistance GenesAntibiotic Resistance Genes

• If we can detect and quantify resistance genes, then we have an assay on the bioavailability/impact of the antibiotics.

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Mechanisms of ResistanceMechanisms of Resistance

• Alteration of the antibiotic or target site– tetM tetS tetO tetW tetQ tetT tetBP

• Impaired uptake or enhanced efflux– tetA tetB tetC tetD tetE tetG tetH tetJ tetY tetZ

• Overproduce target so higher concentration of antibiotic needed– sul genes (PABA overproduction to make folic

acid)• Degrade antibiotic

-lactams• Resistance transfer:Resistance transfer:

– Plasmids can be exchanged within and Plasmids can be exchanged within and between species……between species……

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MethodsMethods

• Plate counting:– R2A agar with antibiotics.

• Polymerase chain reaction (PCR) assays:– Presence/absence of a resistance gene

family.

• Quantitative real-time PCR (Q-PCR)– Quantify resistance gene families.

Goal: Indicator of Bioavailability/impact of AntibioticsGoal: Indicator of Bioavailability/impact of Antibiotics

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Study Site: Poudre RiverStudy Site: Poudre River

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Map of Study SitesMap of Study Sites

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CFU at Sites: April 2004CFU at Sites: April 2004

site 1 site 2 site 3 site 4 site 5

CF

U P

er G

ram

of

Sed

imen

t

102

103

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ChlortetracyclineOxytetracyclineMecolcyclineSulfamethoxazoleSulfamethazineErythromycinTylosinMonensinNo

Ab.

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CFU at Sites: February 2005CFU at Sites: February 2005

site 1 site 2 site 3 site 4 site 5

CF

U P

er G

ram

of

Sed

imen

t

102

103

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ChlortetracyclineOxytetracyclineMecolcyclineSulfamethoxazoleSulfamethazineErythromycinTylosinMonensinNo Ab.

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Pitfalls of Culture-Based Pitfalls of Culture-Based MethodsMethods

• 99% of environmental organisms cannot be cultured on standard media (Amann et al., Pace et al.).

• 16S rRNA gene as a target for detecting microorganisms in environmental samples (Woese et al.).

• Targeting of functional genes….

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Molecular Biology ApproachMolecular Biology Approach

• Polymerase Chain Reaction (PCR)– Exponentially amplify target genes using

primers specific to the target.– Low detection limit.– Provides a means of presence/absence

detection.

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PhylogenetiPhylogenetics of cs of SulSul GenesGenes

sul I

sul III

sul A

sul BC

sul Bcr

sul D

sul II

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New New SulSul Primers Primers

Specificity verified by cloning and sequencing the inserts.Specificity verified by cloning and sequencing the inserts.

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Detection of PCR ProductDetection of PCR Product

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PCR Presence / Absence PCR Presence / Absence AssayAssay

Gene ID

April 2004 high-flow spring

February 2005 low-flow winter

+ control

Site 1

Site2

Site3

Site4

Site5

Site1

Site2

Site3

Site4

Site5

tetB(P)

- - - - + - - - - - +

tet(O) + - + + + + + + + + +

tet(S) - - - - + - - - - - +

tet(T) - - + + + - - - - - +

tet(W) - + + + + + + + + + +

sul(I) + + + + + + + + + + +

sul(II) - - + + + - - + + + +

sul(III)

- - + + + - - - - - +

sul(A) - - + - + - - - - - +

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Real-time PCRReal-time PCR

Number of Cycles

Flu

ore

scen

ce

0 5 10 15 20 25 30 35 40 45 50

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Sul ISul I Gene Calibration Gene Calibration

Threshold Cycle (CT) Value

0 10 20 30 40 50

Lo

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op

y o

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ul I

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pe

r R

eac

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0

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12y = -0.22 x + 12.13

r2 = 0.9978

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April, 2004: Spring High-April, 2004: Spring High-FlowFlow

site 1 site 2 site 3 site 4 site 5Co

py

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G /

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16S

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10-10

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10-3

10-2sul(I)sul(II)tet(W)tet(O)

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Feb, 2005: Winter Low-FlowFeb, 2005: Winter Low-Flow

site 1 site 2 site 3 site 4 site 5

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10-2sul(I)sul(II)tet(W)tet(O)

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Aug, 2005: Summer Low-Aug, 2005: Summer Low-FlowFlow

site 1 site 2 site 3 site 4 site 5

Co

py

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10-2sul(I)sul(II)tet(W)tet(O)

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ConclusionsConclusions

• Resistance genes in Poudre sediments– correlate with human and agricultural

activity

• No direct correlation with antibiotics– High sulfonamide resistance compared to

tet resistance– Fate of antibiotics vs fate of genes?

• High-flow versus low-flow?– Implications for transport?

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RecommendationsRecommendations

• Need further studies into the origin of the antibiotic resistance genes and their fate– Human vs agricultural– Do genes persist longer than antibiotics?

• Investigate and apply treatment strategies for mitigating risk.

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Composting Field StudyComposting Field Study

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““Biodegradation” of ARGBiodegradation” of ARG

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Students!!!Students!!!

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Thank You!!Thank You!!• Thank you to USDA NRI and to the

CSU Agricultural Research Station for supporting this research!!

• Ken Carlson & Sung-chul Kim• Jessica Davis & Kathy Doesken

•Questions??Questions??


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