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Studies on Trace Element Analysis of Uranium Using Soild State
Nuclear Track Detection Technique
DISSERTATION SUBMITTED IN PARTIAL FULFILMENT OF THE REQUIREMENTS
FDR THE AWARD OF THE DEGREE OF
MASTER OF PHILOSOPHY FN
PHYSICS
BY
AMEER AZAM
Under the Supervision of
Dr. Rajendra Prasad
ALIGARH MUSLIM UNIVERSITY ALIGARH (INDIA)
1988
DS1197
h C K M 0 W L 3 D G E H E N T G
I am hlgi i ly indeb ted to my s u p e r v i s o r Dr . Raj endra Prasad ,
Reader, Ai 'plied Phys ics Department/ Z.ii . Co l l ege of Engg. Si
Technology v;ho guided me a t every s t a g e of my r e s e a r c h culminat inc
i n the p rc i sen ta t ion of t h i s d i s s e r t a t i o n . I wish to thank
Prof . R.K. Tyagi, Chainnan, AJ 'p l ied Phys i c s Department and
P ro f . l-i. Sbc.fi, Cnaiinuin, Phys ic s Department, A.M.U. for p rov id inc
t h e l a b o r a t o r y and S'-jminar f a c i l i t i e s .
I am ( j ra te fu l to Dr. D . 3 . S r i v a s t a v a who i n t r o d u c e d me
t h e t echn i ^ue o i Uolid s t - i t o t l a c l e a r Track D e t e c t i o n and gave
many useful sm. .- oi> Lions . I am al^o thankful to D r . L . Chand
who helpi:-!.! ino in l o a i n i n o tht^ J o l i d S t a t e Nuclear Track D e t e c t i o n
Techni^jUe. rtuinKs . i i r ,il;-o Liu>i to i^.iss V. liansal t o r g iv ing me
some s u g g e s t i o n s .
In t h e end i i n . i n c i a l suppor t r e c e i v e d from t h e Department
Sc ience jind Technology i s t h a n k f u l l y acknowledged.
i^-^^^
(AMEER AZAM)
P R E F A C E
This dissertation is aeing submitted in partial
fulfilment of the degree of Master of Philosophy (M.Phii) in
Physics, which is an essential pre-Ph.D. requirement in the
Aligarh Muslim University, Aligarh.
This dissertation has been divided into three chapters.
Chapter I contains brief description of the occurrence
and uses of Uranium. This chapter also contains the mechanism
of nuclear fission and the process of detection of fission
fragments using plastic track detectors. Tovjaxds the end of
the chapter a specific mention of the aims ana results of present
investigations has been made.
Chapter II contains brief description of historical
cevelopment of the Solid State Nuclear Track Detection Technique
The track formation mechanism and track development process
have also been explained in this chapter. Methods of track
visualization and evaluation and threshold characteristics of
the SSNTDs axe also mentioned.
Chapter III is the original contribution of the author.
Chapter III describes the application of Melinex-0
plastic track detector for the measurements of uranium content
in Soil and plant samples collected from various places of
Utter Pradesh, The chapter contains all experimental details
result and discussion on the determination of Uranium
content in various soil and plant samples. Finally
the dissertation ends with a list of references of the
v/ork consulted by the author in the preparation of this
dissertation.
^ o N T j E j i s a
Page No,
CHAPTfiR 0MB
1.1 I n t r o d u c t i o n • . • • • 1
1.2 N u c l e a r F i s s i o n • • • • • 4
1.3 Mechanism o f N u c l e a r F i s s i o n • • , . . 7
1.4 Spon taneous F i s s i o n and l i q u i d
Drop Model 7
1.5 Defor tna t lon of t h e L i q u i d Drop , i . , , , 11
1.6 D e t e c t i o n of F i s s i o n F r a g m e n t s U s i n g P l a s t i c T rack D e t e c t o r s • . . . . , 18
1.7 The P r e s e n t I n v e s t i g a t i o n s 21
CHAPTER T/VQ
2 . 1 I n t r o d u c t i o n 22
2 .2 P r i n c i p l e of D e t e c t i o n 23
2 . 3 H i s t o r i c a l Background 2 5
«i.4 Treek F o r m a t i o n Mechanism , . . , . . 27
2 . 5 Methods of T r f c k R e v e l a t i o n and v i s u a l i z a t i o n 3O
2 .6 Methods of T r a c k E v a l u a t i o n 39
2 . 7 T h r e s h o l d C h Q r > x : t e r i s t i c s of SSNTDs and P l a c e of P l a s t i c Among These D e t e c t o r s 40
GHAPPER THREE
3 . 1 I n t r o d u c t i o n 44
3 .2 E x p e r i m e n t a l D e t a i l s 47
3 . 3 R e s u l t s and D i s c u s s i o n s 52
REFERENCES 56
CHAPTER ~ I 1
1 . 1 INTRODUCTION s
Uranium I s a h e a v i e s t n a t t o r a l l y occx i r r ing t r a c e
e l e m e n t . I t h a s w i d e s p r e a d o c c u r r e n c e and i s found i n
minu te q u a n t i t i e s i n d l l r o c k s , sand and s o i l . Al though
r e g a r d e d a s a r a r e e l e m e n t i t h a s a c o n s i d e r a b l e h i g h e r
c o n c e n t r a t i o n i n t h e e a r t h ' s c r u s t t h a n o t h e r t o x i c e l e m e n t s
such a s SD, Cd, Bi and Hg and t h e p r e c i o u s m e t a l s . I t i s
n o t u n i f o r m l y d i s t r i b u t e d and o c c u r s m a i n l y i n a d i s p e r s e d
s t a t e . U 7SCF:AR r e p o r t s 1966;, 197 2 ^ ' ^ i n d i c a t e t h e t y p i c a l
c o n t e n t of u ran ium i n t h e a c c e s s i b l e l i t h o s p h e r e a b o u t
2 . 8 ppm bu t t h e c o n t e n t v a r i e s w i d e l y i n d i f f e r e n t t y p e of
r o c K s , Some a p p r o x i m a t e a b u n d a n c e s a r e shown i n t h e f o l l o -3
wing t a b l e .
U P^^S ppm of
Mafic i g n e o u s r o c k s - o a s a l t C , g a b b r o s
I n t e r m e d i a t e i g n e o u s r o c k s - d i o r i t e s
A::id i g n e o u s r o c k » - g r a n o d i o r i t e s
- g r a n i t e s
S e c i m e n t s - n o r m a l s h a l e s
- l i m e s t o n e s
- b l a c k s h a l e s
1
2
2 .6
4 .7
4
2
8
330
660
860
1600
13oO
660
2600
There h a s been found a l a r g e v a r i a t i o n (250-500)ppm
i n t h e c o n c e n t r a t i o n of u ran ium w i t h i n each t y p e of r o c k s .
In the economically viable uranium ores the conosntratlon
var ies from 1000"fe3000 ppm while in few of the pitchblende 4
samples 72% of U-Og has been found in lenses or veins ,
l^e concentration in phosphate rcrcks can be as high as 0,12
mg/g • Sea water uranium concentration has been found to
vary from 0.000 3 to 0.00 3 mg/1 ' . All of these sources
come in contact with water and thus t ransfer ce r ta in con
centrat ion of uranium.
Uranium has also been found in phosphate deposits
and can come from t a i l i n g s and phosphate deposits as well o
as runoff from phosphate f e r t i l i z e r , The average f e r t i l i z e r uranium concentration i s about loO /ig/g. Phosphate mineral
5 from Florida indicate uranium concentrat ions 4,5-83,4 pCi/g ,
After processing uranium follows the phosphoric acid whereas
radium found in phosphate deposit follows the by-product
gypsum and i s thus separated. In ammoniated phosphate and
t r i p l e superpnosphate the uranium contents have been estimated
to be 25.3 and 26 pCl/g respec t ive ly . The use of phosphate
f e r t i l i z e r may lead to increase the uranium concentration in
r i v e r s and thereby in the so i l in i t s neighbourhood and in
the p lan t s grown there . More than 99% of the uranium t r ans
ported by runoff from land to fresh water systems remains
with suspended p a r t i c u l a t e s on the sediments. Only a small o
amount of uranium remains in true solution in fresh water .
3
Uranium may be found in valence s t a t e s +2, +3,
+4, +5 or +6, the most comroon being the hexavalent and
t e t r ava len t s t a t e s , AP almost a l l the tetravalent compounds
are p r a c t i c a l l y Insoluble, the hfexavalent state i s important
one in water. Natural uranium has 99.2756 ^ , 0-7256 ^ TT 234 and 0.00 6% U and 1 ^g of uranium has an a c t i v i t y of
2+ 0.67 pCi, The uranium i s found as uranyl ionCUO* Jin nature
9 and a l l the natura l compounds of uranium contain oxygen .
The main use of uranium i s in the form of fuel in
nuclear power reac to rs and in nuclear weapons. I t a lso
finds uses in in te rna l guidance devices, gyrocompasses, as
a counterweight for mi^ile r e -en t ry vehicles and as A-ray
t a r g e t s , Urcinium compounds are also used in photographic
toners , coloured glasses^ceramic glasses , t i l e s and as
c a t a ly s t .
Hydrolysis competes with organic and inorganic
complexation dnd control the environmental behaviour of
uranium. At pH6 and iaelow uranium forms very stable coro-
plexes with oxygen r ich organic cornpoxinds in the form of
humic and fulvic acids in the na tura l environment. This
in te rac t ion involves peats , coals , asphal t s , as well as
inorganic i n t e r ac t ions with s" a les , phosphorites, and g
carbonates , When put into solution uranium forms the 2+ uranyl ion (UO' ) and this ion forms soluble salts with
4
10 a l l common anions except phosphate , Uranium can a l s o be
in t roduced i n t o the water supply by human a c t i v i t y in tne
mining and m i l l i n g of uranium o r e , Ihe uranium concen t ra -
t i o n s of water may be i n f e r r e d from nearby ground and
surface s o i l .
1.2 NUCLE>iR FISSION :
11 12 Nuclear f i s s i o n ' was d iscovered in 1939 as a
p r o c e s s in which a uranium nuc leus a f t e r cap ture of
neu t rons s p l i t s up i n t o two p a r t s which a re c o n s i d e r a b l y
d i f f e r e n t from the t a r g e t nuc l eus . Although n u c l e a r
f i s s i o n has been produced from the bombardment of heavy
n u c l i d e s by neu t rons , p ro tons , deu t rons , a lpha p a r t i c l e s
and even e l ec t rons4nd gamma r a y s , nuc l ea r f i s s i o n of
p r a c t i c a l importance i s the neutron induced f i s s i o n of
uranium and plutonlura. A number of rev iews of v a r i o u s
13-21 a s p e c t s of f i s s i o n have been puo l i shed by many workers
The only n a t u r a l l y occuring n u c l e i t h a t can be f i s s i o n e d
with thermal neu t rons i s U v>*iich c o n s i t u t e s 0*11% of
n a t u r a l l y occur ing uranium, Vlhen a nuc leus of high atomic
number undergoes f i s s i o n , f i s s i o n fragments having two
dlmost equal p a r t s a re produced. The f i s s i o n fragments
con ta in too many neu t rons for them to be s t a b l e , Ihey can
approach s t a b i l i t y e i t h e r by e j e c t i n g one o r more neu t rons
or by the the emiss ion of b e t a - p a r t i c l e s ob ta ined from
the convers ion of neut ron i n t o p ro ton .
5
Fission in to more than two intermediate mass frag
ments i s extremely r a r e . The f iss ion fragments can be
anyone of the nuclides in centre t h i r d of the Periodic
Table. The f ission yield curvl^fcr ^ ^ U by thermal
neutrons has been shown in Figure 1,1, From the f iss ioning
of uranium ^itoyether about 300 s table and radioact ive
nucl ides have been found. About 180 dif ferent beta-emiters
have been iden t i f i ed among the products r e su l t ing from
uranium f iss ioning. As can be seen from the figure the
maximum yield occurs for mass numbers near 9 5 and 140.
The energy released for f iss ion of uranium has been
estimated to be around 200 MeV. About 17o MeV of t h i s energy
i s provided as the k inet ic energy of the f ission fragments.
Except for a very small fraction a l l f iss ion neutrons are
emmitted v i r t u a l l y instantaneously and are ca l led prompt
neutrons. According to the compound nucleus p ic tu re , these
are the neutrons which are boiled offftbm the highly exci ted
compound nucleus. In case of u 0.64% delayed neutrons are
emitted having a time lag of several seconds to more than
a minute af te r the f i ss ion. They a r i s e out of the rad io
active decay of a f ission fragment. The energy d i s t r ibu t ion
cons is t s of two d i s t i n c t groups having mean energies about
70 and loO MeV. Later s tudies based on the measurement of
ionizat ion v e l o c i t i e s of the f iss ion fragments indicate tha t
6
10
0 I
0 01
oooi
rt) I I I 1 I 1 I I I I 1 I
90 IK) 130 150 170 Moss
Figure 1,1
the K.5. of t-hese fragments is 167 Mev for ^^ fission
produced by slow neutrons. The two groups of energies have
maximum of about 6d and 9y Me».
1.3 MECHANISM OF IJUCLS.^ FISSION t
The mechanism of nuclear iission has been explained
23 by means of liquid drop model of the nucleus. It is
capable of explaining some of its chief features and gives
fair agreement with many experimental results.
According to this model the nucleus in equilibrium corresponding to its most stable configui
assumes a spherical shape/ . As long as the nucleus
is not disturbed, it remains in this state and shape under
the joint action of the
1) Cohesive shiort range nuclear forces acting throughout
its volume and along its surface.
2) The C-iloumb force of repulsion between the protons
present in the nucleus. This force tries to disrupt
the nucleus.
1 . 4 S P O N T A N S O U S F I S S I O N AtJD LIQUID EROP MODEL :
Spontaneous f iss ion can be predicted by emperical
nuclear mass equation. Assuming tne symmetric f iss ion as
a special case, the energy released, E^, upon f iss ioning
in to two equal par t s -
8
= 2 (B.B)^2 - (B.E.)^
Considering Vfelxsaker's semi-emperlcal mass
formula
E^ = ( - 3.42 A /- + 0.22 Z^/A^/^) MeV.
From t h i s equation i t i s c lear t ha t sp l i t t ing of
the nucleus a f fec t s coulomb energy and surface energy in
such a way tha t the change in one tends to cancel the
change in the other p a r t i a l l y . This i s expected as the
separation betv^en the proton groups increases by the
division of the nucleus. Therefore reduces t he i r coulomb
po ten t i a l energy. On the other hand the t o t a l nuclear
surface i s increased re su l t ing in the increase of surface
energy. Thus for spontaneous f i ss ion.
^ f > 0
or [- 3.42 A^/^ + 0 . 2 2 Z^A^/^J^O
or ~ r - > 15
Therefore the nuclear fission should be energetically
possible for nuclei with AN. 85. However the slow neutron
fission does not take place even in many of the heavy
nuclei. This discrepancy was explained by Bohr and wheeler
9
considering the conlomb potential barrier of the two frag-
iTients dt the instant of separation. Hie coulomb potential
carrier prevents the immediate splitting of these two. The
barrier height corresponding to the coulomb potential
between the two symmetric fragments v^en they are just in
contact with each otner is given Dy
^b
/Z, 2 2
47r£, 2R
1 Z2 e2
^/^Co 8 \ ^ t^''''
o 0.15 - ^ j - MeV
Thus the condition of Stability becomes
\ - \ ' ^ 0
or ~ <C 49
It is concluded that nuclei for v^ich the condition
of stabili ty is not fulfilled can not exist as the smallest
disturbance would be sufficient to trigger the disCruption
of the nucleus.
Figure 1.2 shows the relationship between E and
E, and their general behaviour as a function of A. Ihe
10
,
200
? 150 5
J 100
50
E
1 ' I
1 ^iy\
1 1
^J^E^
\ 1
1
/ -
1 50 100 150 200
Mass number
250 300
Figure 1,2
11
graph shows that for A = 250 E, becomes equal to B_, so
t h a t one does not expect nuclei \)ith A>250 to be found
in nature .
1.5 DSFORMATION OF THE LIQUID CROP j
If the force is applied to the drop of the liquid,
so that it is set into oscillations, the system passes
through the series of stages some of vhich are shown in
Figure 1,3.
The drop is elongated into an elipsold (B), If not
enough energy is available to overcome the siirface tension^
the drop will return to its original shape, but if the
deforming force is sufficiently large, the liquid acquire
a shape similar to the dumb-bell (C), Once this stage is
reached, it can not return to its Spherical shape but will
split into two droplets. These will be somevhat deformed (D)
but finally will become spherical (E),
Oho situation in nuclear fission is believed to be
analogous to the liquid drop. A compound nucleus is formed
by the absorption of a neutron by the target nucleus. Its
excitation energy is equal to the binding energy of the
neutron and the kinetic energy, if any, the neutron may
have had before capture. Ihe introduction of excitation
energy into nuclear system disrupts the equilibrium of the
nucleus. Once the incoming neutrons sufficiently distort
12
A B C D l .iquiil-droi) IIHMIC! of fission
Figure 1.3
• CRITICAL ENERGY
DiSIf lNCE: i iETWEEN FRAGMENTS
Fiyure 1,4
13 the Spherical shape of the nucleus, the equilibrium t h a t
exis ted in the undisturbed nucleus i s i r revocably destroyed.
If the energy i s insuf f ic ien t to cause deformation beyond (B)
the in t - ranuclear forces wil l compel the nucleus to i t s
o r ig ina l Spherical form and the exci ted compound nucleus
wil l get r i d of i t s excess energy by the ejcpulsion of a
p a r t i c l e . But once tlie c r i t i c a l point of d i s to r t ion i s
reached, the t o t a l energy of the nucleus wil l continue to
decrease v/ith increai^inc deformation and wil l f i na l l y lead to an i r r e v e r s i o i e oroaK up of the nuclear drop. The mutual po ten t ia l onertj/ oi the rwo symetrical f iss ion fragments
against the distance betv.eon them i s shown in Figure 1.4,
At E t'..'o f ission fragments are far apart so tha t the
po ten t i a l ener^iy is zero. As the fragments come close
together, there i s an increase in the po ten t ia l energy due
to coulor.'h force of repulsion between the fragments, Vhen
the fragments are roughly in contact, a t the point C, the
nuclear forces b' come dominant and the po ten t i a l energy
s t a r t decreasing.
Tho |,ot^t)Llal curve has a maximum value a t C, Tl:!e hump
rcprcs-^nts the ba r r i e r against spontaneous s p l i t t i n g , Ihe
po ten t i a l energy ba r r i e r as seen from the inside of the
nucleus i s oiven by E. - S^ vA ere E, denotes the height of • ' o f D
coulomb barrier and S is the deformation energy available
for fission. The presence of this barrier explains why
fission does not take place Spontaneously in all cases
14 where E,->0. An addi t ional amount of energy B « E. - B-.,
the ac t ivat ion energy i s required by the nuclear system to
allow the f iss ion to take place.
The f i r s t t h e o r i t i c a l treatment of the f i ss ion process
was given toy Bohr and wheeler in 19 39 and they made deta i led
ca lcu la t ions about the behaviour of a nuclear drop under
deformation. For small ax i a l l y syBainetric d i s t o r t i ons the
radius can oe written as
R (er) = R Q L^ "*• 2 ^^°^ ^ 1
where ©"is the angle of the radius vector, cCn is a parameter
describing quadrupole distortion and R is the radius of the
undistorted sphere. For spheroidal distortions additional
terms starting with <^APA ^^^ required. However for small
spheroidal distortions o is considerably less than (A~2*
The surface and coulomb energies for small distortions are
given by (Bhor t« Wieelar 19 39).
% = E° ( 1 - - I - ^ ^ •
where E and E^ are the surface and coulomb energies of
undistor ted spheres. For the charged l iqu id drop to be
stable against small d i s to r t i ons the decrease In coulomb
energy AE = - -r— oC E° must be smaller than the
15
increase in surface energy A B = » ^^ B^, The drop
becomes unstable when | E I -^ E = 1 or \^en
I C • ' S
E° /2E° = 1 . E° / 2 E° i s known as the f i s s i l i t y
parameter x.
For X - 1 the drop will be stable against small
d i s to r t i ons . For x^ 1 there wil l be no potential barrier
to i nh ib i t spontaneous division of the drop. Star the
ideali/ied spherical nucleus we have
v^ere 2 i s the number of protons, Ihe surface energy
where Jlis the surface tension. Green (19 54) performed the
analys is of these equations expressed in terms of mass
number A and nuclear charge Z oy f i t t i n g experimental
masses with the semi-empirical masses and obtained
E° = 0.710 3 Z^ / A /-
and E° = 17,80 A^^^
2 Subst i tut ing those values one gets x = 2 /SO. 13 A.
2 Some typ ica l values of Z / A and x are 35.56 and 0.71
16
for - U and 38.11 and 0.76 for ^^^C{ and are well below
the limiting value of 45, This indicates that all naturally
occuring nuclides are stable with respect to small defor-
mation. For deformations that exceeds the critical limit,
the nucleus breaks apart. The critical energy required to
cause such a break up (activation energy E ) calculated on a
tne b a s i s of Bohr - '.iSieeler theory i s given oy the expre
s s i o n . E = S, - E-a b f
2 = A^/^ X 0.89 (1-0.0 22 — • )
If E is less than the excitation energy S provi
ded by the absorption of a thermal neatron by a particular
nucleus, the fission can be produced in this nucleus by
thermal neutrons. The excitation energy, contributed to the
resultant compound nucleus by the capture of a neutron is
equal to the binding energy of the neutron in the compound
nucleus,
E = B (A + 1, 2) - B (A, Z)
and can be c a l c u l a t e d from the semi-emperical mass formula.
The Taole 1,1 shows the v a l u e s of E and E^ for some n u c l e i , e a
17
YAF3LB 1. 1
Compound E (MeV) B (MaV) E^ - B
(MaV)
^^S 6.6 4.6 2.0
2^^U 6 .6 5 . 5 1.1
^^^U 5.9 6 . 5 - 0 . 6
^^•^Th 5.1 6 .S - 1 . 4
^^^Np 5.0 4 . 2 0 . 8
^ ^ P u 6 .4 4.0 2 . 4
18
238
It is clear that in the case of U a critical deforma
tion energy of 6,5 MeV is necessary for fission but it
acquires only 5.9 MeV by absorbing a neutron of zero
kinetic energy. Thus no fission is possible in ^
with thermal neutrons, vghereas the thermal neutrons can
23 5 produce fission in U as the excitation energy provided
by the thermal neutrons is greater than the activation
238 energy. However fast fission i s possible vdth U. The
238 experimental threshold energy for fast fission of U is 1.1 MeV as compared to th' predicted value of 0.6 MeV.
The liquid drop model has been applied success
fully to explain some of the main feat\ires of nuclear
fission. I t fails to explain the observed non-symmetry
of the masses of the fission fragments as syrrenetrlc
fission should be most favoured division according to
t h i s t h e o r y .
1.6 DETSCTIQN 0 [•' FISSION FRAGMENTS USING PLASTIC
TRACK ©BTSCTOiiS:
Nowadays a large number of plastic track detectors
are available which can be used as a charged particle
detector. The Commonly used plastics are Cellulose Nitrate,
Cellulose Acetate, Polycarbonates, Polyethylene terephthalates
e t c . In the follovjing table 1,2 are l i s t e d some well known
p l a s t i c detectors used to record the t racks of charged
p a r t i c l e s . Column 2 gives t h e i r chemical composition. They
have been l i s t e d in order of t h e i r increasing sens t iv i ty .
The l a s t column ind ica tes the smallest ionizing ion being
detected by them.
I t can be observed that Cellulose Ni t ra te and
CR_39 p l a s t i c s can even record the lowest ionizing ion
(proton) vrfiereas polycarbonates can not record proton.
The polycarbonates such as Lexan, Makrofol etc , do not
produce etchable t racks of protons but they are sens i t ive
to low energy c?(,-particles and a l l other heavy ions* The
polyethylene te rephthala te p l a s t i c l ike Melinex, Cronar
and Mylar e t c . a r e not able to record the t racks of
p/C-particles and protons but they do record the t racks
of heavier iono>^B. Therefore, the sui table p l a s t i c
det(^ctors con \y^. used for the detection of f iss ion frag
ments in the presence of l i gh t charged p a r t i c l e s l ike
e^-par t ic les , protons e t c . \'^.ich they can not record. For
the detection of f ission fragmenijLexan and Makrofol
p l a s t i c de tec tors have been very extensively used. Melinex-0
p l a s t i c has been r a r e ly used as a f iss ion product detector 24
although i t appears to be be t t e r than Lexan and Makrofol
TADLB 1^2
20
Name of p l a s t i c d e t e c t o r
Chemica l c o m p o s i t i o n
Least i o n i z i n g i on d e t e c t e d
CH, Polyethylene
Polyvinylchloride(PVC)
Polyimide
P o l y e t h y l e n e t e r e p l i t h a l a t e Cj. H. 0
(Cronar^ Nfellnex, Mylar)
CH3CI + CjHjCl
S i "4 °4 "2
Polyoxymethy lene
(Cfelrin)
CH^O
F i s s i o n F ragmen t s
42 MeV ^^S
36 I^V ^^0
28 MBV 1 4 N
28 hfeV ^ ^
B i s p h e n o l A _ p o l y c a r b o n a t e ^1 g^i 4* -1
(Lexan, Makrofo l , Kimfol ,
Merlon)
0 . 3 MeV *He
C e l l u l o s e t r i a c e t a t e
( C e l l i t _ T , T r i a t o l - T ,
KG dace 1 TA-401
u n p l a s t i c i z e d )
S"4°2 3 I^V ^He
C e l l u l o s e a c e t a t e
B u t y r a t e
C e l l u l o s e N i t r a t e
( D a i c e l l , Nixon-Baldwin)
S2"l8°7
^ 6 " 8 ° 9 ^ 2
3 MeV 'He
0 . 5 5 MeV - H
P o l y t e c h GR-.39 S 2 " l 8 S 1 MeV proton
21
p l a s t i c a s i t does not r e co rd the t r a c k s of charged
p a r t i c l e s having low i o n i z i n g power. Also the backi-
ground e t ch p i t s developed due t o i t i ^ r f e c t i o n S a r e much
l e s s and e a s i l y i d e n t i f i a b l e than those in the oase of
Lexan and jMakrofol e t c . . Therefore^ we have used Melinex-O
p l a s t i c d e t e c t o r to r ecord the t r a c k s of f i s s i o n p roduc t s
produced by (n, f) r e a c t i o n used for the determination of
uraniMTO con ten t in s o i l and p l a n t samples,
1.7 THE PRBS' IJT INVESTIGATIONS:
The aim of the p r e s e n t i n v e s t i g a t i o n s was t o
measure the uranium con ten t c?f s o i l and p l a n t samples
c o l l e c t e d from d i f f e r e n t p l a c e s of U t t a r Pradesh us ing
SSNTD Technique. The a p p r o p r i a t e e t c h i n g cond i t ion for
Melinex-0 was used a s 6N, NaOH a t 60 C for 90 minutes .
In our s t u d i e s on uranium con ten t measurement in
s o i l and p l a n t samples, we have found t h a t the U-content
v a r i e s very vddely from p lace t o p l a c e . Wie v a l u e s of
U-content v a r i e s from 0.0 23 ppm t o 0 .43 ppm in s o i l
samples and from 0.026 ppm t o C.'206 ppm in p l a n t
samples.
CHAPTER - II 22
2.1 INTRODUCTION :
Unique information can be ext rac ted from the per
manent ' track* l e f t in the s t ruc tures of certain minerals
and mater ia ls by the passage of high-energy, sub-atomic
p a r t i c l e s . Materials in which nuclear t racks have been
observed are:
Glass Materials : Volcanic g la s s (obsidian), t e k t l t e s ,
soda lime g lass , phosphate g lass ,
meteori tes (glass and ol ivine) e t c ,
ii^^atite, epidote, quartz, micas,
sphene, zircon e t c .
Cellulose n i t r a t e (LR - 115, Dalcel
e tc^ , ce l lu lose accetate , polycarbonates
(Lexan, Makrofol), polyethylene t e r e -
pthala te (Cronar, Melinex), CR-39 e t c .
These mater ia ls , vh^jn used to detect the charged p a r t i c l e s ,
are known as Soli a State Nuclear Track Etetectors (SSNTDs)
and the technique of detecting charged p a r t i c l e s by these
mater ia ls i s known as Solid State Nuclear Track Detection
(S»]TD) Technique, The so-cal led SSNTDs were f i r s t i n t r o
duced as an important tool for appl ica t ions in Nuclear
Minerals
Organic Polymers
23
Science and Geophysics in the e a r l y n in t een s i x t e e s by 25
F l e i s c h e r e t a l .
2.2 PRINCIPLE OF D5T5CTI0N :
All charged p a r t i c l e s cause narrow t r a i l s of r a d i a
t i o n damage in the m a t e r i a l s v^en they p a s s through them.
As a r e s u l t of e x c i t a t i o n and i o n i z a t i o n m a t e r i a l damage
t a k e s p lace along t h e i r t r a j e c t o r y . The damaged reg ion of
the s o l i d has d i f f e r e n t chemical and p h y s i c a l p r o p e r t i e s
than the bulk m a t e r i a l and i s c a l l e d ' l a t e n t t r a c k ' which
i s in the form of a c y l i n d e r o f ^ 5 0 - l o O A° r a d i u s . This
l a t e n t t r a c k i s i n v i s i b l e under o p t i c a l microscope. However^
the l a t e n t t r a c k can be seen d i r e c t l y a s d i f f r a c t i o n c o n t r a s t
images us ing t r ansmiss ion e l e c t r o n microscopy (TEM), If,
however, one p l a c e s the o rgan ic p l a s t i c m a t e r i a l in a
chemical e t ch ing s o l u t i o n ( e , g , 6N, NaOH) the volume around
the l a t e n t t r ^ c k vdU be a t t a c k e d p r e f e r e n t i a l l y .
The t r a i l of the nuc lea r p a r t i c l e becomes v i s i b l e under an
o p t i c a l microscope as a c y l i n d r i c a l cone-shaped ho le of
^—1-30 pm leng th , i f we cons ide r <7(.-particles or f i s s i o n
fragments.
Nowadays Sol id S t a t e Nulcear Track Etetectors (SSNTDs)
a re p r e f e r r ed over o t h e r p r e v a l e n t nuc l ea r d e t e c t o r s ^s they
24
have in themselves the proper t ies of track recording detec
to r s l ike the cloud chambers, nuclear emulsions e tc , together
with th' ' compactness and single p a r t i c l e counting a b i l i t y
of semiconductor detectors without requir ing any special
dark room processing or cos t ly e lectronic equipments,
Da^ to t he i r many useful feature^^ these detectors have been
used extensively for the l a s t two decades in almost a l l
branches of nuclear science and technology, radiation dosi-
metry, health physics and geo-sciences , SSNTDs have wide
appl icat ions in the study of low cross-section nuclear
reac t ions , nuclear f ission reac t ions , identif ication of
cosmic-ray p a r t i c l e s of solar a r i galactic origin, neutron
flux riioasurements, study of rad ia t ion history of meteorites
and lunar samples, age determination of geological and
archaeolo; ical samples, microdistr ibut ion s tudies and
microanalysis of some elements l ike U, Th, I^i, Li, B, Be
e t c , neutron and charged p a r t i c l e radiography, radon and
thoron dosinr^try and th^ i r study for predict ion of earth
quakes, study of spreadin'-, of sea-beds, as micropore f i l t e r s
for f i l t e r a t i o n of cancer blood c e l l s ^ virus and bac te r ia
in beer industry, for measuring f l igh t a l t i t ude of birds ajnci
for heavy ion l i thography e t c . In fact these detectors
have been found to have po ten t ia l appl ica t ions in almost
every branch of Science and Technology. In addition to the
25
0 ft
book written by Fleischer e t a l . having exce l len t
t r e a t i s e on t h i s subject and elaborate l i s t of l a t e s t
references covering a l l top ics many review a r t i c l e s have «
a p p e a r e d on s p e c i a l r e f i n e m e n t s o f t h e SSNTD t e c h n i q u e s 25-37 and i t s a p p l i c a t i o n s
2 .3 HISTORICAI., BACKGROUND :
The N u c l e a r T rack E te tec t ion Techn ique (SSNTD) began
i n t h e l a t e n i n t e e n - f i f t i e s wi th two n e a r l y s i m u l t a n e o u s
b u t a p p a r e n t l y i n d e p e n d e n t works by members o f t h e same
e s t a b l i s h m e n t , t h e Atomic Energy E s t a b l i s h m e n t a t H a r w e l l ,
38
Eng land . In t h e f i r s t of t h e s e ifoung , i n v e s t i g a t i n g t h e
c o l o r a t i o n indi.iced In KCl by f i s s i o n f r a g m e n t s showed t h a t
f i s s i o n f r a g m e n t s i n L i F l e f t i n d i v i d u a l t r a i l s o f damage
v/hich c o u l d be e t c h e d by a s u i t a b l e r e a g e n t t o r e v e a l
i n d i v i d u a l e t c h - n i t s . Each p i t c o r r e s p o n d s t o t h e p a s s a g e 39 of a s i n g l e f i s s i o n f r a g m e n t . E.C.H. S i l k and R. S, Ba rnes
t i i r e c t l y obt ;erved a f l a k e of mica bombarded wi th f i s s i o n
f r a g m e n t s by e l e c t r o n microscopy.* The r e s u l t i n g ( u n - e t c h e d )
t r a c k s , a n n e a l e d o u t and d i s a p p e a r e d d u r i n g p r o l o n g e d
o b s e r v a t i o n u n d e r t h e e l e c t r o n beam.
26
In 1961, P.O. Price and R.M. Vfalker of the General
E lec tr i c Company Research and Development Centre, a t
Schncctady (Hew York), apparently ignorant of the Young's
o b s e r v a t i o n s , followed up th^ l i lk-Barnes work by r e d i s
covering the chemical e t c h i n g of f i s s i o n tracks and showed
t h a t the e tched t r a c k s in mica l e f t permanent features
v/hich may be s t ud i ed a t l e i s u r e . In 1963, R, L, Fle ischer
jo ined th-^ ter^m of Price and Walker. Afterwards for
several yea r s , almost a l l the work in t h i s f i e l d was
c a r r i e d cvit by these i n v e s t i g a t o r s . During t h i s time
t hey not only developed and put the technique on firm
footir.g but a l s ; aop l i ed i t very s u c c e s s f u l l y to Neutron
dosiroetry, Fissi ' jn s t u d i e s , Biology, Cosmology, Geophysics,
•Archaeology e t c . F i n a l l y they showed that f o s s i l tracks
could be induced in many m a t e r i a l s other than mica. In
f ac t they showed t h a t almost any i n s u l a t o r could be used
40-43 ao a ch:iryed p a r t i c l e t r a c k d e t e c t o r .
Today GS 'TDs are being used in more than f i f t y
l a b o r a t o r i e s of the v;orld i n c l u d i n g Australia, Austria,
Bangladesh, B raz i l , China, Czechoslovakia, England, France,
Hungary, I nd i a , I r a q , I r a n , I t a l y , Japan, Mexico, Pakistan,
Spain, Sweden, the U.S.A., the U. S. S.R., Vfest Germany and
Yugoslavia. C.'--/. Np.eeer (USA), D. Lai ( India) , E. V. Benton
27
(trSA)-, G.A. Wagner (W. Germany), G. Sotnogj|l (Hungary),
H.A, Khan ( P a k i s t a n ) , H. S, Virk ( I n d i a ) , L. Tommasino
( I t a l y ) , M. Monnin (France) , R, %)hor (w. Germany),
R.H. Iye r ( I n d i a ) , V,p. Pe re lyga in (US^) and W, Bnge
(W, Germany) are some of tue S c i e n t i s t s who have made
some impor tan t c o n t r i b u t i o n s t o t h i s new f i e l d .
2.4 TR^K FORMATICK MECHANISM :
Charged p a r t i c l e t r a c k s in s o l i d s a re narrow
( < 50A^ r a d i u s ) , s t a b l e , chemica l ly r e a c t i v e c e n t r e s of
s t r a i n t h a t are composed most ly of d i sp laced atomic
r a t h e r than e l e c t r o n i c de fec t s . On the b a s i s of
exper imenta l t e s t s conducted (a) on the measuremeitit of
e f f e c t s of e l e c t r o n i r r a d i a t i o n on chemical d i s s o l u t i o n
r a t e s of s o l i d s and (b) on the measurement of the r a d i a l
d i s t r i b u t i o n of e t c h a b l e damage in s o l i d s . I t h a s )Deen
concluded t h a t two sepa ra te mecJianisms of trac)c formation
e x i s t . One for the i no rgan i c s o l i d s and g l a s s and the
o the r for tho oruanic s o l i d s or polymers ( p l a s t i c s ) ,
(A) For Inorgan ic Sol ids : VJien a heavy charged p a r t i c l e
pa s se s through a s o l i d i t e x c i t e s a s well a s ionizes^ the
atoms of s o l i d in i t s p a t h . In the case of i n o r g a n i c s o l i d s
28
the primary damage tha t r e s u l t s from the excitation and
ionizat ion caused by the incident heavy ion i s believed to
be roainly responsible for the development of an etchable 4
t rack i . e . for the higher chemical e tchabi l i ty of the
damaged t r a i l s . There are strong evidences t ha t the
secondary e f fec t s of del ta rays are uniJfiportant for the 44 45
case of inorganic so l ids ' . Infact , in the inorganic
solicSs the las t ing the raa l ly etchable damage cons i s t s of
atomic disorder and vacancies. Fig. 2.1 shows the formation of t racks in the
inorganic so l ids according to the Ion-Explosion spike 46 model of Fleischer e t a l , . The incoming heavy ion f i r s t
knocks out e lec t rons (black c i rc les ) 4* om the atoms in
i t s path (open c i r c l e s ) thus creat ing an unstable array
of adjacent +ve ions. The charge centres or +ve ions, so
produced, may produce secondary e lec t rons or de l ta - rays
from tVie atoms of the solid v^ich may further produce
exc i ta t ion and ionizat ion i f they carry enough energy,The
del ta rays deposit energies around the t r a j ec to ry of the
incident p a r t i c l e , Then the +ve ions repel and force one
another away from tiieir normal s i t e s in to the i n t e r s t i t i a l
pos i t ions in the c rys t a l l a t t i c e , thus creat ing vacant
29
iJlgure 2.1
30
lattice sites due to their coulomb repulsive forces.
Thereafter the elastic relaxation reduces the intense
local stresses by spreading the strain more widely. The
damage produced by atomic collosions consist of displaced
atoms and resultant vacancies ani can be etdied pre
ferentially with respect to the host.
(B) For Organic Polymers or Plasticsx In the case of
organic polymers or plastics the belief is that both the
primary and secondary ionization and excitation play roles
in the production of etchable tracks. In plastics, the
long chain molecules that makeup the material are broken
by the energetic charged particles. Ftee radicals and
excited molecular states are produced which increase in
the chemical reactivity at the broken ends, making the
track areas more susceptible to etching (Pig 2,2). In the
case of plastics the contribution of delta-rays in
depositing the energy sideways of the trajectory of the
48 49 incident ion is most important ' ,
2.5 METHODS OF TRACK REVELATION AND VISUALIZATION*
Many methods have so far been used for the revela
t ion and visual izat ion of charged p a r t i c l e t racks in
31
Figure 2.2
32
dielectric solids. They are as follows:
(i) Direct observation of latent tracks In thin crys-
tallins solids using Scanning Electron Microscope
(11) Selective chemical etching for all types of SSNTD
41 40 42 viz plastics ^ glasses and minerals and their subsequent observation using optical microscope.
(iii) Track decoration in minerals and their observations
with optical microscope using violet or near ultra-
52 5T violet light^^' - .
(iv) Track revela t ion in photochromic mater ials with the 54 help of colour centre ,
(v) Detecting the presence of l a t en t damage t rack in 55 c rys ta l s using X-rays ,
(vi) Grafting and dyeing of t racks in some selected p l a s t i c s 56-58 and the i r observation using opt ica l microscope .
(vii) Electro Chemical Etching (ECE) technique^^~ ^.
All the above mentioned methods except the se lec t ive
chemical etching have some drawbacks and l imi ta t ion asso
c ia ted with them. Although electrochemical etdhing (ECE)
enlarges the t racks to very large s izes , i t s appl icat ion i s
33
l imited to , some p l a s t i c s only and for specif ic type
of t r a c k s , I t also requi res high frequency and high voltage
c i r c u i t elements. The se lect ive chemical etcSiing of t racks
revela t ion and t h e i r v i sua l iza t ion using opt ica l microscope
i s the simplest and convenient technique. I t has been most
extensively used in the case of a l l types of SSNTDs
(p l a s t i c s , glasses and minerals) from the very inception
of t he i r discovery.
In the case of se lec t ive chemical etching the d i
e l e c t r i c sol id containing charged p a r t i c l e damage t r a i l s
i s immersed in su i table etching solution ( S ^ Table 2,1)
maintained at a fixed temperature. Inside the solut ion,
the bulk material of solid dissolves in general a t a
constant r a t e , V known as bulk or general etch r a t e vhile
the material along damaged region dissolves at a mudi
fas ter ra te V^ cal led the t rack etch r a t e , here assumed
to be constant at every point on the trajectory of the
p a r t i c l e . Since v^ i s greater than V , after soroetiiije the
p re fe ren t i a l chemical a t tack enlarges the damaged region
in the form of a conical e t c h - p i t . When the size of the
e t ch -p i t becomes comparable to the wavelength of v i s i b l e
l i gh t , i t s t a r t s scat t3r ing the l i g h t and can be seen by
op t ica l microscope a t magnifications of 100 x or more.
TABLE 2 . 1
E t c h i n g c o n d i t i o n s for Some D s t e c t o r i
34
S,No, Name o f t h e D e t e c t o r E t c h i n g Condi t ion
1.
2.
3 .
4 .
5.
6.
7 .
8 .
9 .
Soda Lime G l a s s
V i t r e o u s U u a r t z G l a s s
Muscov i t e Mica
Makrofo l -E
Makrofol-N
Lexan
M e l i n e x - 0
CR - 39
Ho s t a p h an
489i HF, 22°C
43% HF, 22®C
48% HF, 22°C
6N, NaOH, 50+1°^
6N, NaOH, 50t l °C
6N, NaOH, 50+1 °C
6N, NaOH, SOtl^C
6N, NaOH, 10±l^C
33% 6N, NaOH +
33% H^O + 33% CH^OH,
40+l°C.
35
Figure 2,3 shows the <3evelopment of charged p a r t i c l e
t rack by chemical etching process in an i so t rop ic sol id
( l ike g lass or p las t i c ) assuming tha t the p re fe ren t i a l
t rack etching s t a r t s j u s t from the surface of the detector
i t s e l f . Since V > V , an etched p i t i s formed. The etched
t rack remains conical t i l l tho time v^en the etchant
reaches the end of tlie par t ic le ' s t r a j ec to ry (Fig. 2,3c)
After tha t the p re fe ren t i a l etching along the t r a j ec to ry
stops and the material etches out a t the same general bulk
r a t e V_ a l l along the surface of the t rack hollow ,
Tho wall of the t rack remains conical
but the end of the t rack becomes spherical (Fig 2,3d) . C o
This i s ca l led the t r ans i t i on phase
Prolonged etching will lead to a posi t ion v*iere the
conical walls of the track-hollow wil l also vanish, and
the en t i r e etched hollow wil l become spherical (Fig 2 ,3e) ,
This i s known as ' spher ica l phase*.
The shape and size of the t racks depend upon the
type of the p a r t i c l e as well as on the c h a r a c t e r i s t i c s of
the detector and etchants , These a l so vary with angle of
entrance. The' t rack saci-ion of normally entering p a r t i c l e
i s in general c i r cu la r and tha t of obliquely enter ing
pa r t i c l e i s e l l i p t i c a l . Grazing t racks show conical
36
Unetched defector S u r f j c f
, P»rf ,c(e '» t r a j t c t o r y
fa)
Etch ing Solt .on
(b)
(Conrcal phase)
]
(e)
(d) ( • )
Figure 2 . 3
37 projections for short etching times (Fig 3^,4),
The geometry of etched tracks for the isotropic as
well as anisotropic so l ids haVe been' studied in great
detai l s by Henke and Bentom. # Soroogyi and flzalay , All
and Durrani , and Somagyi , The expressions for the
diameter of the track d, c r i t i ca l angle ^ , and etching
eff ic iency ^^2^ in 2 rT -geometry are:
= 2 V^. t / VT - Vg ( i )
V + V
L = ^ and
^T
V
( i i )
7 ] . ^ = 1 - _ !G_ ( i i i ) ^T
V„ T Obviously, the greater the value of -Tf , the
smaller will t>? the c r i t i c a l angle ^^ and the greater
will be the etching eff ic iency 7l2jr for trac^ etching
in 2tf -geometry.
38 itrt
» o
o M
v?x
N s / ' > '
-{"-'/ • i -; ,> ' V / ' «-
< A . L ' '
X ' - <
< "*! V
H M
rn
)(
m »o « ' 3 7 IAJ
"» , -a. 'u.
I C
r i-K -< i4>
^ .^ -»
» , n c/>
-» o •»•©
O 3
a o # - f» m o n or * >—
c u •• C - .
O Q. » *
3 O
T
1
I > ' * ^ \
• * !
39
2 . 6 METHODS OF TR.^^K BVALUATION :
G e n e r a l l y e t c h e d t r a c k s a r e o b s e r v e d u s i n g an
o p t i c a l b i n o c u l a r r e s e a r c h m i c r o s c o p e a t m a g n i f i c a t i o n
of 100 X t o 1500 X, In some c a s e s t o t a l number o f t r a c k s
and i n some o t h e r s t r a c k c f e n s i t y _ ^ ( t r a c k s / c m ) i s
r e q u i r e d . For f i n d i n g t r a c k d e n s i t y t r a c k s a r e c o u n t e d i n
a b o u t 50 t o 100 f i e l d s and a v e r a g e i s d e t e r m i n e d . A s q u a r e
g r a t i c u l e i n t h e f i e l d of v iew i s c a l i b r a t e d for . i t s a r e a
by u s i n g a s t a g e m i c r o m e t e r g l a s s s l i d e .
The t r a c k l e n g t h and d i a m e t e r o f t r a c k s c o n t a i n
i n f o r m a t i o n a b o u t t h e p a r i c l e ' s c h a r g e - ~ 2, mass M
7 3 - 7 5 and e n e r g y 2 . The measurement o f d i a m e t e r t h d l e n g t h
i s done by u s i n g a F i l l e r t y p e e y e - p i e c e m i c r o m e t e r .
E n t r a n c e a n g l e o f t h e p a r t i c l e t r a c k can be measured by
u s i n g '^ - a x i s mot ion sc rew o f t h e microscope . 2he v i s u a l
c o u n t i n g u s i n g o p t i c a l m ic roscope I s v e r y t ime 'consuming
and t i r i n g , e s p e c i a l l y i n t h e c a s e of l a r g e number o f 4
t r a c k s ;?- l o . For a v o i d i n g such p r o b l e m s many more methods
have been d e v e l o p e d fo r t r a c k r e v e - l a t i o n b u t t h e s e have
s t i l l n o t found g r e a t p o p u l a r i t y among t r a c k o l o g i s t s
b e c a u s e of t h e i r i n h e r e n t p r o b l e m s . V a r i o u s me thods o f
t r a c k e v a l u a t i o n s a r e :
40
( i ) Scanning E l e c t r o n Microscope and R e p l i c a t i n g
T e c h n i q u e ,
( i i ) T rack c o u n t i n g by R e f l e c t a n c e and T r a n s m i t t a n c e
Measurements .
( i i i ) Coun t ing wi th u n a i d e d Eye Uging P r o j e c t i o n
iMicroscope o r S l i d e P r o j e c t o r .
( i v ) Automat ic Scanning us ing E l e c t r o n i c C i r c u i t o r
Image Ana lys ing Dev ices wi th O p t i c a l M i c r o s c o p e s .
(v) Automat ic Scanning u s i n g Jumping ^ a r k T e c h n i q u e .
( v i ) L o c a t i n g c h a r g e d p a r t i c l e t r a c k s by Naked Eye .
( v i i ) T rack c o u n t i n g by C o n d u c t i v i t y ^ a s u r e m e n t s
th rough E tched T r a c k s .
2 .7 THRESHOLD CHARACTERISTICS OF SSNTDs AND PL/CE
OF PL-AJTICS AMOUG TH33E DETECTORS:
Sxpor inK-n ta l ly i t h a s been found t h a t t h e SSNTDs
a r e t h r e s h o l d type of p a s s i v e d e t e c t o r s , ^ e r e l a t i v e
s e n s i t i v i t y of t h e SSNTDs i s unote rs tood i n t e r m s of c r i t i c a l
16 v a l u e of pr irr .ary i o n i z a t i o n ( J ) c r l t • ^ c r i t i c a l v a l u e
dE 77
of r e s t r i c t e d e n e r g y l o s s r a t e CRSL)^,J.J^^ o r (;jir")v/<.wCvif •
P r a c t i c a l l y for e v e r y SSNTD t h e r e e x i s t s a c r i t i c a l v a l u e
o f m a t e r i a l damage o n l y above which t h e t r a c k s become
41
etchabla, ,^J)crlt ^^ ^^'^^W^ Wfcrit ^QP^o»en*» *hi» c r i t i c a l
damage. If a par t ic le produces an excitation and ionization
in a SSNTD to such an ext»nt that result ing damage i s above
the ('J)crit °^ ^^^^cr i t ^°^ ^^^^ material, i t s tracks can
be preferential ly etched and observed with the help of a
microscope. If the damage produced by any par t ic le i s less
than ( J )c r i t ' ^^^^ par t icular pa r t i c l e ' s trade can not be
etched in that 3SNTD. These threshold or c r i t i c a l values
are shown by horizontal l ines in Fig, 2,5.PleJL8cher et al
obtained these lings by experimentally detecting the
registration and non-registration of tracks of accelerated
heavy ions. The open c i rc les represent non-registration,
while the f i l led circles represent 100% regis t ra t ion.
I t is evident from this -figure that plast ic track
detectors are most sensit ive as the threshold represented by
c r i t i c a l value of primary ionization («I)cj.it ^° lower for
p las t ics (f'ig 2.5), Among the plast ics themselves, the
Oaicell CN is more sensit ive than Nixon-Baldwin, Malinex-0
i s the leas t sensitive p las t ic as i t has th« highest value
of c r i t i c a l primary ionization (J)cx:it* *^i''*«*-0 can not
record the tracks of protons ojf o'-particle and i s e n a b l e
of racording the tracks of ions heavier than oxygen and fission
fragmaits, The Lexan polycarbonate p las t ic records tracks
12
5 10 20 • T
ENERGY / NUCLEON (MeV)
50 100 200 300 • i(fO 1000 20QQ
|iiTlQ»iJUC_¥iliLRA!.4_:
0.4 0.5 0.6 VELOCITY, /^-v/e
Figure 2 , 5
13
of f i s s i o n fragments and low energy a lpha p a r t i c l e s
(belovv'^0.5 5eV> v?hile i t does not record the tracks of
p r o t o n s . S imi l a r l y the g l a s s e s a re more s e n s i t i v e than
mica and m e t e o r i t i c mine ra l s . Muscovite mica and g l a s s do
not r ecord the t r a c k s of l i g h t e r charged p a r t i c l e s v i z
alpha p a r t i c l e s and p ro tons viiereas they record the tracks
of f i s s i o n fragments and o t h e r ions h e a v i e r than oxygen.
S i m i l a r l y the mica r eco rds the Ne ions of energy upto 20 2 feV while the g l a s s r eco rds Ne heavy ions of energy
upto 20 NteV.
CFU39 p l a s t i c t r a c k d e t e c t o r s have been found to
be the most s e n s i t i v e t r a c k d e t e c t o r known so far . This
p l a s t i c i s made by the po lymer iza t ion of a l iqu id monomer
of a l l y l d ig iyco l carbonate and I s ab le to record even the 78
t r a c k s of 1 MeV pro tons
CHAPTER . Ill 44
3.1 INTRODUCTION;
Uranium is a normal constituent of organism and its
-4 -9 concentration in organism varies between 10 % and 10 % by
79 80 weight »^^, it plays an important role in various cosmo-
chronological, nucleo-synthesis events, , toxicity and environ
mental pollution hazard. Its toxicity to plant is moderate
but it can result in variation of colour in flowers, presence
of abnormal fruits, increase in chromosomes of nucleus sti-
81 mulation . Plant ash normally contains 0.2 to 1.0 ppm
uranium. The uranium content of plants grown in ore however,
may range from 1 to 100 ppm, Iberefore, the high content of
uranium in plant sample may be an indication of mineralized
ground.
I t has been e s t a b l i s h e d t h a t some p l a n t s p e c i e s
absorb much more uranium than o t h e r s . The underground r o o t 82
vege t ab l e s are high mineral absorber and can absorb the
high degree of uranium from s o i l and v ien consumed by human
be ings can pose a h e a l t h hazard . I t has a l so been
observed t h a t p l a n t s t h a t r e a d i l y absorb large amount of
sodium, sulphur, selenium and calcium bu t small amount of
potass ium wi l l a l s o absorb xxranium r e a d i l y . Due to t h i s .
Coni fe rs and d e s e r t shrubs of the ro se family can be used
45
t s indicator plants in sanpling programs in uranium d i s t r i c t s .
238 The radioactivity from U ser ies i s transferred to
plants and water from s o i l . When radio-isotopes are inside
the body, they cause greater health hazard because the
internal t i ssues are irradiated continuoixsly t i l l the isotope
loses i t s radioactivity by natural decay or e l se eliminated
in the feces and urine. The tetravalent form of natural
uranium being unstable i s oxidised to the more toxic hexa.
valent form. The hexavalent form then combines with active
s i t e s (phosphate gro\:{j) on the surface of c e l l s blocking 83 normal metabolic processes for c e l l ' s survival .
Several methods such as Mass spectrometry. Activa
tion analysis, X-rayfluorescence, Delayed neutron coun
ting^ Radiometric titethod. Alternating current polazo-
graphy e tc . are available for the determination of trace
quantities of uranium. Sol id State Nuclear Track d«tectors
provide cheap, rapid and ef fect ive technl(|a« #or trace
element analysis . The technique having n««(ted s ens i t i v i ty
and potwitial capability of mlcroroa^plng ev«i at sub ppb
levels of f issionable impurities with (n , f ) , (n, a) md (p,o:)
reactions e tc . i s the so-ca l led Solid State Nuclear Track Detec
tion (SSNTD) Technique. I t has beoai widely used In diverse f ie lds
l ike anthropology, archaeology, biology, medical scitnces and
46
technology \ Many workers have u t i l i s ed th is techni-^
que for tha detenidnation of uranium in water, milk powders,
semiconductors, c i ga r e t t e s tobacco, human blood, plants,
so i l s , Portland cement, detergents and soaps, coal, flyash
and s tee l e t c . In the present case th i s technique has been
exploited for the t race determination of so i l and plant
samples col lected from various places of Uttar Pradesh,
The external detector method was used in our cftse, I h i s
method consis ts of placing a sample whose uranium concent
ration i s to be measured in intimate contact with a uranium
poor t rack detector . A standard glass sample of known
uranium concentration i s also included and the entire
assembly i s i r r ad i a t ed with thermal neutrons in a reactor. 235
Tlie thermal neutrons cause f iss ion in U and f iss ion fracjm-^nts produce / a t e n t damage in the p las t ic detectors
232
which are in close contact with the samples. Th if present
in the sample contributes very little to the total damage
from the (n,f) reaction due to its very low fission cross-
section i.e. 40 micro barn as compar^gd to 580 barn for 235
U. Following irradiation, the detectors are etched in a
proper etching so,lution and scanned under an optical micro
scope. The uranium concentration C of unknown samples can
be calculated by compring the measured track densities directly
47
with those of standard materials, simultaneously irradia-
8 16 ted ' using the relation
A -^ s
'•"^ere y ^ r e f e r s t o t r a c k d e n s i t i e s and s u b s c r i p t
s and X r e f e r t o t h e s t a n d a r d and the unknown, r e s p e c t i v e l y
3 . 2 I XP' RIKSNT.AL DGT.^^LS :
The s o i l and p l a n t s amples were c o l l e c t e d from the
p l a c e s of Agra, J a w a l a p u r (Har idv /a r ) , Nadrai ( S t a h ) ,
R i s h i k e s h , S a h a s t r a d h a r a , Dehra Ran s i t u a t e d i n the s t a t e of
U t t a r P r a d e s h . Washed p o l y t h e n e b a g s were used for c o l l e c t i n g
s a m p l e s . In Agra ©oi l samples were taken from the bank o f
t h 3 R i v e r Yamuna, K a t o l a and Company Garden, P l a n t samples
were a l s o c o l l e c t e d from t h e company Garden, Agra,
5 o i l samples were t a k e n from t h e bank of the Ganges cana l
and some d i s t a n t p l a c e s In Jawalcour (Haridwar). Samples were
a l s o c o l l e c t e d from d i f f e r e n t depths a t Jawalapur t o s tudy
t h e v a r i a t i o n of U - c o n t e n t wi th d e p t h . In the same way
Samples were chosen from t h e bank of t h e River Kal i and,
T a t a r p u r colony^ some' d i s t a n c e away from t h e bank. The s o i l
Samples were chosen from t h e bank and some d i s t a n c e p l a c e s
,/^ 400. Nc. Y ,
is
to study the possible contr ibution of water in r a i s ing the
U-contant of the so i l of the r i ve r bank as i t might t ranspor t
uranium from some d i s t an t source.
Soil samples were grinded properly and sieved through
a 100 mesh sieve. Plant samples were f i r s t dried in an
oven a t 160 G for 24 hours. These plant samples were fused
in a contamination free s i l i c a crucible in a furnace a t
700^C for 2 hours. After grinding the plant Rskes. properly,
•ikese w® - sieved through IQQ mesh sieve (1.5 x 10 cm
ape r tu re ) . A homogeneous mixture of accurately weighed
sample powder and methyl ce l lu lose in the r a t i o l i 2 by
weight was press-^d in to a f l a t p e l l e t of about 1,3 Cm dia
meter by the ha^'^-p^^sssing p e l l e t making machine, spec ia l ly
d'^sgined for t h i s purpose. The p e l l e t making machine i s shown
in Fig.3.land cons i s t s of the following p a r t s .
Part A- M.S. p la te of size 1.25" x 5" x lO" having four holes ,
of size 3/8'* for f i t t i n g the machine on table and
having two side holes of the same size to support
the p i l l a r s G St F,
Part B - M. S. adjustable guide of size I"x4"xl0" to support
the p i l l a r s having two side holes of size 3/8" to
adjust the same upward & downward.
9i-'f Si
Hri5"K'S'kio')
0 7'J'W- -r\07S"i
PKLLBI MAKING MACH(N£
St
50
Par t C - M.S. guide of s ize 1. 25''x4"xlO" f ixed with p i l l a r s
by H. S. n u t s of heavy duty.
P a r t D _ M. 3. handle of s i ze 0 .73" ^ x 16" to rotate the
p a r t K upward or downward.
P a r t S _ C . I . tush to support p a r t H,
Pa r t F & G - M. S. |> i ] l a r s of s i ze 1" (j> x 15" having upper
p a r t 0 . 7 5 " x 1.25" duly threaded to f i x i t with
p a r t C with n u t s and lower part of s i z e 0 ,75"xl ,25"
to f i x them in the b a s e .
Pa r t H _ High carbon s t e e l screw of s i ze 1" 0 x 10,5" having
upper p a r t of 2" ^ having hole of s i z e 0,7 5" 6 x
1,5" for hand le .
Pa r t J - M.S. d i sc of 1.5" (j> x 0 , 7 5 " as per drawing.
Par t )< - 3p<?cial K s t e e l punch having upper part of
0 .5" (f) X 1.5" and lower part of 13 rron ^ x 3" duly
hardened, tempered and gr inded surface.
P a r t L _ Special K s t e e l die of 1.5" f x 3.75" duly hardened,
tempered and gr inded s u r f a c e .
Pa r t M - Special K s t e e l base of 2" f x 0.7 5" lower part and
13 mm ^ X 0.75" upper part duly hardened, tempered
and gr inded su r f ace .
51
Each p e l l e t was sandwi-ched between two already
washed in double d i s t i l l e d water Meline:&-0 detector pieces
of the same s ize . Several such 'sandwi-ched p e l l e t s along
with a standard glass with known U-content >«ere packed in
an aluminium capsule and sealed t i g h t l y to make the
intimate contact . This assembly was i r r ad i a t ed with thermal
netitrons in the core of APSARA reactor for one hours a t a 12 2
place where the nominal neutron flux was 2 x 10 n/cm /See (10 to 15% fast neutrons) .
After i r r ad i a t i on detector pieces were taken out and
washed. These washed pieces were etched in 6N, NaOH a t 6o°C
for 90 min as i t i s the optimum etching condition for
Melinex-0 p l a s t i c de tec tors . The etched detector pieces were
a i r dried and scanned under binocular research microscope
at a magnification of 430 X, The t rack dens i t i es were deter
mined by counting the fission t racks in the e n t i r e area of
the detector . Trncko were counted on both the pieces of the
detector and mean was taken to determine the t rack densi ty .
The square marked on the g r a t i cu l e in the eye piece represen--4 2
ting one field had a calibrated area of 1.69 x 10 cm . The
standard glass detector was etched in 48% HF at 23°C for
5 sec and track density was calculated.
52
3.3 RESULTS AIN D DISCUSSION;
Uranium c o n t e n t o f unknown samples was d e t e r m i n e d
u s i n g t h e r e l a t i o n (3 .1 )»The Ul-conten t of s o i l s amples and
p l a n t samples a r e summarised i n T a b l e 3 . 1 and Tab le 3 .2
r e s p e c t i v e l y .
I t i s obse rved^rom Tab le 3 . 1 t h a t U - c o n t e n t of
s o i l samples v a r i e s from 0 . 0 2 3 t o 0 .430 ppm. I t i s a l s o
e v i d e n t t h a t t h e U - c o n t e n t of t h e s o i l samples c o l l e c t e d
from t h e bank h a s h i g h e r v a l u e t h a n t h a t of t h e s o i l
3ampl'-»s c o l l e c t o d from some d i s t a n t p l a c e s . The h i g h e r
v a l u e of u ran ium i n t h e s o i l a c r o s s t h e bank of t h e r i v e r s
may i n d i c a t e t h e c o n t r i b u t j ^n of w a t e r i n r a i s i n g t h e
u ran ium c o n t e n t t h r o u g h r u n o f f p h o s p h a t e f e r t i l i z e r s and
some o t h e r s o u r c e s . Among t h e r i v e r bank s o i l s a m p l e s , t h e
s o i l sample c o l l e c t e d from t h e Yamuna r i v e r bank h a s t h e
h i g h e s t Value of u ran ium c o n t e n t (0 .430 ppm). T h i s sample
was t aken fro"i a p l a c e b e h i n d t h e Ta j Mahal. P r e v i o u s l y
waste p r o d u c t s were dumped i n t h e r i v e r b e f o r e t h i s p l a c e ,
v/hich migh t be t h e p o s s i b l e c a u s e of t h i s h i g h e r v a l u e .
The u ran ium c o n t e n t of s o i l s amp le s c o l l e c t e d from t h e
p l a c e 15 mete r away from t h e c a n a l bank and from d i f f e r e n t
d e p t h s v;ere found t o d e c r e a s e wi th i n c r e a s e i n d e p t h . Across
t h e bank s o i l i s d e p o s i t e d by w a t e r l a y e r a f t e r l a y e r , I he
TABLE g-i
Uranium Content of Soi l Samples
53
S.No. Location Total No, of U-content in ppm tracks
4.
5.
6.
7 .
8.
9 .
10.
1 1 .
Bank of Ganges Canal, Jawalapur (Haridwar)
A p lace about 15 meter away from the Ganges cana l bank and
(a) 6" deep from the upper surface
(b) 12" deep from the upper surface
(c) 18" deep from the upper surface
A f i e l d about 4 Khi away from the canal bank, Jawalapur,
Yamuna River Bank Agra
Matola, Agra
Company Garden, Agra
Kali River bank Nadrai (Btah)
Tatarpur Colony about 300 meter away from the Kali River bank
Sahas t radhara (Dshra EVin)
Local Bus s t a n d . D ^ r a Dun
Bus Stand, Rishikesh
1537 0.2331.00 54
1300
850
611
937
2786
151
1620
1044
508
1489
1208
1500
O.a02i.OO5O
0. 132 Qt, 004
0.093±.003 5
0.143t .0042
0. 430±.0073
0 .023t .00 l7
0. 2471.0056
0 . l 6 1 t . 0 0 4 5
0.077+.0031
0.23 2+^0053
0,2631.0048
0.2301^0054
54
OS U1 U) to
^1 Oi 3
o cu •1
s-3
>
0 X
JO
& h*
g" s-
1 O
0) 3
o 0) •1
» 3
3 (D CO 3
> O iQ O
3 1 0> 3
O (U H
^ 3
M 3 M M-
^ ^1
o
J Qi 3
O (U 1-1
» 3
o H
• 0 0) 3
s? 3*
01
3
P ^ 0)
^ t M
c n
o c
cu
o o
o
cn
3
n
w O
• o to OH
o o )-» CD
3 W
H-iQ O H-
0)
3 a a •I
O O
0)
3 0) a 3 H- (0
3
1 ^ o o p. O
f ir o> 3 f t Qi
<Q "O C (fl 0> H-i_». Cu 01 H-
< c 0) 3
>Q ^3 C CO 0) H-
«_.. a 01 H-< c 0> 3
CA
.? CO 0
Ti 3*
^ ff
(A
o •o 3-S ^
1 0) O V 3"
*< ??
1 W 0 tJ 3-
^ /?
i? CO o
^ < sr
1 s ^ s; 1?
H-» - J tn
ON ON t-»
-0 •J -J
o 00 -^
»-» en >t^
10 00 (O
u> vO l-»
o w
o o
CD
O o u>
o
o o m
- J
o o :5
o to
o o
o
to
(0
o
o (0
O 3
OH •1 O O O
•o o
O »
O
a* ?r as (0 O
o ft
•1 (U 3 H-
3
3 ?f 3 (+ O M>
•O M
s > fO
55
lower value of the uranium content indicates the higher
age of the so i l and the higher value indicates the lower
age of the so i l of tha t pa r t i cu l a r place.
I t i s c lear from Table 3,2 tha t the uranium
content of plant leaves samples var ies from 0.0 26 to
0.206 ppm and tha t var ia t ion takes place from plant to
plant and place to p lace . This i s due to the fact that
the uranium content might be d i f ferent in so i l and water
where the p lan t s were grown.
The uranium content of so i l and p lant samples
reported by u.s ^.re d i f ferent from those reported by til 91
Goswani e t a l . and Virk e t a l . This disagreement i s due
CO the fact that the p lan t s samples chosen by Goswani e t a l .
and Virk e t a l . v;ere of different v a r i e t i e s from those
invest igated by us and the soi l belongs to d i f ferent regions
of the country.
56 R E F B R B N C S S
1 . UNSCEAR
2 . UNSCSAR
IAEA
4 , Hardy, C . J .
: Report of Uni ted Nations S c i e n t i f i c -
Committee on t h e Effec ts of Atomic
Radia t ion , Uni ted Nat ions ,
New York, (1966) .
: " I o n i z i n g Rad ia t i on : Levels and
Ef fec t s " , Vol I , Report of t h e
United Nat ions S c i e n t i f i c
Committee on t h e Ef fec t s of Atomic
Radiat ion, Uni ted Nat ions ,
New York, (1972) .
: " s i g n i f i c a n c e of Mineralogy in t h e
Development of Flowsheets fo r
f ' rocessing Uranium Ores", Technical
Report S e r i e s No. 196, I n t e r n a t i o n a l
Atomic Energy Agency, Vienna, (1980)
: "The Chemistry of Uranium Milling",
Rad. Chlm. Acta, 25 (1978) 121-134.
226, 5 . Roess le r , C.E. , : "Uranium and Radium " * ' i n F lor ida
smith Z.A., bolch, w.F. Phosphate M a t e r i a l s " , Heal th Phy.
and Pr ince R.J . 37 (1979) 269-2 77 .
6 , Turkian K.K. and
Chan, L.H.
"The Marine Geochemistry of Uranium
I so topes , " Th and ^^^Pa, from
Activation Analysis", ins Geochemistry
57
J and Cosmochemistry (Edltad by
A.O. Brunfe l t an<3 E. Ste lnnes) ,
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L.O. and Je f f rey , Trans, Am. Geophys. U. 37 (19 56),
L.M. 697-701.
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Conc' n t r a t i o n s " . Science 17 5 (1972)
629-631.
9. Kat^, J . J . and : "The Chemistry of Uranium, the Element
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Yor.<: Ebver) (19 51),
10. Longane, J. J . , : "Analyt ica l Chemistry of Selected
M e t a l l i c Elemeftts (New York*
Reinhold) (1966).
11. Turner L. A. t Rev. >tod. Phys . , 12 (1940), 1,
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Nostrand Co., I n c . , Chapters XIII and
XIV. (19 50) .
13. Halpern I . : Ann. Rev. Nuc. S c l . , 9 , (1959), 245.
58
14, Hui^enga J . R. and
Vandenbosch R.
15. V*ieelar J . A.
16. Hui?ienga J . R.
17. Wile ts L.
18. Fraser J . S. and
Milton J .C. D.
19. Gindler J . E. and
Hui,6enga J . R.
20. Fong P.
20. Bohr N, and Wheeler J .A ,
: In "Nuclear Reac t ions" , (Edi ted
by P.M. Endt and P. B. Smith),
Chapter I I , North-Holland P u b l . ,
Ansterdam (1962),
I In "Pas t Neutron P h y s i c s " (Edited
by J . B. Marion and J . L, Ibwle r ) .
Wiley ( I n t e r s c i e n c e ) , New York
(1963).
J In "Nuclear S t ruc tu re and
Elec t romagnet ic I n t e r a c t i o n s "
(Edi ted by N. Mac Donald), Plenum,
New York (19 65) .
: "Theories of Nuclear F i s s i o n " .
Oxford Univ. P r e s s (Clarendon),
London and New York (1964).
: Ann. Rev. Nuc. Sc i . 16 (1966), 379.
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