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Int. J. Life. Sci. Scienti. Res., 2(4): 451-453 (ISSN: 2455-1716) Impact Factor 2.4 JULY-2016
http://ijlssr.com IJLSSR © 2015 All rights are reserved Page 451
Histopathological Impact of Dimethoate on the
Kidney of Freshwater Fish, Garra mullya (Sykes)
Borane VR*
Department of Zoology Jijamata Arts, Science and Commerce College, Nandurbar, Maharashtra, India
*
Address for Correspondence: Dr. Borane V. R, Head cum Associate Professor, Department of Zoology, Jijamata Arts,
Sci. and Comm. College, Nandurbar, India
Received: 12 May 2016/Revised: 28 May 2016/Accepted: 16 June 2016
ABSTRACT- The present investigation was carried out to the effect of dimethoate on histopathological changes in
kidney of freshwater fish, Garra mullya. Fishes was exposed to sub lethal concentration of dimethoate (0.0238ppm of
96hrs.) for 7, 14, 21 days. Fishes exposed to dimethoate were characterized by loosening of haemopoietic tissue,
uriniferous tubules have lost their original appearance, vacuolated cytoplasm, degeneration in the epithelial cells of renal
tubule, narrowing of the tubular lumen and damaged glomeruli. The lesions in the vital organ might have resulted in
physiological and metabolical dysregulations. In chronic treatment of dimethoate exposure may pose serious threat to fish
health and affect their population.
Key-words- Dimethoate, Histopathology, Kidney, Garra mullya
-------------------------------------------------IJLSSR-----------------------------------------------
INTRODUCTION
The availability of adequate water supply in terms of both
quantity and quality is essential for human existence.
However, our exploitation of water resources to fulfill the
growing need of man has exerted tremendous pressure,
thereby deteriorating its quality substantially. Hence,
conservation of water has become of utmost importance.
The water pollution is thus no longer considered to be an
aesthetic problem, but a serious economic and public
health problem as well. Unfortunately, raw or inadequately
treated sewage of millions of people still flow into our
lakes and rivers, creating several kinds of disorders. The
release of discharge of large number of pollutants,
especially heavy metals and pesticides, pose a threat to
human life (Saikia, 1988). Pollution of aquatic
environment by heavy metals is an extremely important
and serious problem and has attracted the attention of the
scientists all over the world.
Pesticides are occasionally used indiscriminately in large
amounts causing environmental pollution and potential
health hazards.
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DOI:
10.21276/ijlssr.2016.2.4.20
Dimethoate is systemic insecticides produced by reacting
salts of Dimethyldithio-phosphoric acid with
N-methylchloroaecetamide, in aqueous medium in the
presence of some organic solvents is widely used against a
broad range of insects and mites and is also used for
indoor control of houseflies. The extensive use of DM
poses a health hazard to animals and humans because of its
persistence in soil and crops (WHO/IPCS, 1996). One of
the major agricultural chemical groups is pesticide which
play important role in increasing agricultural productivity
through controlling pest. But on the other hand, they cause
much damage to the non-target organisms both in
terrestrial and aquatic environment. Fishes are
accumulating pollutants directly from contaminated water
and indirectly via food chain (Sasaki, et al., 1997). The
runoff from treated areas enters the river and aquaculture
ponds that are supplied by rivers and adversely affect the
quality of water surfaces and creates hazards for aquatic
life resulting in serious damage to non-target species,
including fishes (Bondarenko, et al., 2004).
Histopathology deals with the study of pathological
changes induced in the microscopically structure of body
tissue. Any alteration in normal structure of tissue indicates
presence of disease or the effect of toxic substances like
heavy metal and pesticides. Sprague, (1973) described
histopathology as important tool for evaluating the action
of any toxicant at tissue level. Histopathology provides data
concerning tissue damage. Histopathological alterations can
be used as indicators for the effect of various anthropogenic
pollutants on organisms and are a reflection of overall
health of the entire population in the ecosystem. These
Research Article (Open access)
Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 4
http://ijlssr.com IJLSSR © 2015 All rights are reserved Page 452
histopathological biomarkers are closely related to the other
biomarkers of stress since many pollutants have to undergo
metabolic activation in order to be able to provoke cellular
change in the affected organism (Muhammad Ismail, et al.,
2009). The present study was under taken to analyze the
impact of chronic concentration of dimethoate in liver of
fish, Garra mullya.
MATERIALS AND METHODS
Healthy adult fish, Garra mullya were collected from local
river Shivan Dist. Nandurbar, India in the month of
December, 2015. Fishes were washed with 0.1% of
potassium per magnate (KMnO4) solution to avoid dermal
infection. They were then rinsed in water and acclimatized
to the laboratory conditions in the department of Zoology
for two weeks in 500 l. capacity glass aquaria. Dead fish
were removed immediately that such mortality may deplete
dissolved oxygen with resultant effect on other fishes.
During acclimatization fishes were fed with pieces of live
earthworm on alternate days. Water also changed once in
every day. The experiment was conducted natural and
photoperiod of temperature 25·1 ± 3·20
C. Water quality was
measure as per by APHA (2005), Conductivity- 0.64 ± 0.3,
Dissolved O2
-
6.3±1.1 (ml/L), pH- 8.60 ± 0.3,
Acidity- 2.5± 0.1, Alkalinity- 44.1 ± 0.5, Total
hardness- 67.5 ± 0.3. LC50 of dimethoate for 96 hours was
determined by probit analysis method (Finney, 1971). The
animals were dissected and kidney tissues carefully
removed. Tissues were immediately washed in 1% saline
solution to remove the adhering mucus and blood and
soaked between the blotting papers. The tissue from the
control and exposed batches were taken out and preserved
in aqueous Bouin’s fluid for 24-48 hrs. This was followed
by successive dehydration in ascending grades of alcohol.
Tissues were cleared in xylene and embedded in paraffin
wax (at 58˚- 60˚ C.). The tissue was then processed
routinely and prepared into paraffin block cut at 6μm
thickness using microtome and stained with Haematoxyline
and Eosin by Luna (1968). Standard histopathological
procedures were followed for histopathological
investigations, Roberts, (1989). Observations were taken
under light microscope.
RESULTS AND DISCUSSION
Histopathological changes have been widely used as
biomarkers in the evaluation of the health of fish exposed
to contaminants, both in the laboratory (Thophon, et al.,
2003) and field studies (The, et al., 1997).
Histological studies revealed that the kidney sections from
control fishes showed normal histoarchitecture, kidney is
characterized by well built haemopoietic tissue, uriniferous
tubules and glomerulus with clear Bowman’s capsule
(Fig. 1). Kidney of fishes exposed to 0.0238ppm
dimethoate for 7,14 and 21 days resulted in the Loosening
of haemopoietic tissue, uriniferous tubules have lost their
original appearance, vacuolated cytoplasm. The cells
constituting the wall of uriniferous tubules have become
completely destroyed. The lumen of uriniferous tubules
has become greatly shrunken and deshaped. Expansion of
space has taken place inside the renal corpuscle (Fig. 2 &
3). Kidney of fishes exposed to 0.0238 ppm dimethoate
for 21 days resulted in loss of compactness of
haemopoietic tissue as its cells got scattered, uriniferous
tubules and glomeruli got deshaped and degenerated
(Fig. 4).
Fig. 1: Normal structure of Kidney showing well marked
glomeruli and haemopoetic cells and renal tubules (H&E,
450X)
Fig. 2: On Dimethoate treatment after 7 days structure of
Kidney shows enlargement in haemopoetic tissue,
vacuolation are observed (H&E, 450X)
Fig. 3 On Dimethoate treatment after 14 days of Kidney
shows cellular atrophy and shrinkage in lumen of
renal tubule (H&E, 450X)
Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 4
http://ijlssr.com IJLSSR © 2015 All rights are reserved Page 453
Fig.4 On Dimethoate treatment after 21 days of Kidney
shows cellular atrophy and shrinkage in lumen of renal
tubule (H&E, 450X)
Figure 1: Kidney structure of control fish showing well
built haemopoietic tissue, uriniferous tubules and
glomerulus with clear Bowman’s H & E, X 450.
Figure 2: Kidney of G.mullya exposed to dimethoate
(0.0238ppm) for 7 days showing damaged haemopoitic
tissue, uriniferous tubules, vacuolation and glomeruli H&E,
X 450.
Figure 3: After 14 days Kidney showing loosening of
haemopoietic tissue, clustering of cells, damaged
uriniferous tubules, vacuolation, narrowing of tubular
lumen and expansion of Bowman’s space H&E, X 450.
Figure 4: After 21 days Kidney showing showing severely
damaged haemopoietic tissue, and uriniferous tubules H&E,
X 450.
Similar results have been reported by Cengiz, (2006) in
Cyprinus carpio after acute exposure to deltamethrin. Bilal
Ahmad (2011) reported the lesions in these vital organs
might have resulted in physiologic and metabolic
deregulations, which further led to behavioral alterations
and growth impairment.
CONCLUSION
The lesions in the vital organ might have resulted in
physiologic and metabolic dysregulations, which further led
to behavioral alterations and growth impairment. In the long
run, therefore, dimethoate exposures to even sub lethal
concentrations may pose serious threat to fish health and
affect their population. Dimethoate used to protect many
fruits, vegetables and field crops against disease, hence
farmer come direct contact it and may affect their health.
REFERENCES
[1] APHA AWWA and WPCF (2005) Standard methods for the
examination of water and wastewater. 21st
Edn.Washington
DC USA.
[2] Bilal Ahmad, Qureshi.T.A., Susan Manohar, Pinky Kaur,
Rumysa Khaliq (2011) Effect of Cadmium Chloride on the
Histoarchitecture of Liver and Kidney of a freshwater
Catfish, Clarias Batrachus. International J. of Environ. Sci.
2(2),531-537.
[3] Bondarenko, S., Gan, J., Haver D.L. and Kabashima, J.N.
(2004) Persistence of selected organophosphate and
carbamate insecticides in waters from a coastal watershed,
Environmen. Toxicol. and chemistry, 23(11); 2649-2654.
[4] Cengiz Elif. (2006) Gill and kidney histopathology in the
freshwater fish, Cyprinus carpio after acute exposure to
deltamethrin. Environmental Toxicology and Pharmacology,
22 (2); 200-204.
[5] Finney, D.J., (1971) ‘Probit analysis’ Third edition,
Cambridge University, Press.
[6] Luna L.C (1968), manual of histologic staining methods.
Armed Forces Institute of Pathology, 3 rd Ed. McGraw Hill
Book Company, New York.
[7] Muhammad Ismail, Rahat Ali., Tayyaba Ali, Usman
Waheed, and Khan, Q.M. (2009) Evaluation of acute toxicity
of profenofos and its effect on behavior pattern of fingling
common carp (Cyprinus carpio. L.) Bull. Environ. Contam.
Toxicol., 82; 569-573.
[8] Reuber, M. D. (1984) Dimethoate, Environment Res.34:193.
[9] Robert, R.J. (1989) Fish pathology (2’nd edition), London,
Billier, Tindall. 11, 453.
[10]Saika, D. K., Mathur, R. P. and Srivastava, S. K (1988),
heavy metal in water and sediments of upper Ganga. Indian
Journal of Environmental Helath, 31(1); 1117.
[11]Sasaki, Y., Izumiyama, F., Nishidate, E., Ishibashi, S., Tsuda,
S., Matsusaka, N., Asano, N., Saotome, K., Sofuni, T. and
Hayashi, M. (1997) Detection of genotoxicity of polluted sea
water using shellfish and the alkaline single-cell gel
electrophoresis (SCE) assay: A preliminary study.Mutation.
Res. 393; 133-139.
[12]Sprague, J.B., (1973) The ABC’s of pollutant bioassay using
fish. In biological methods for the assessment of water
quality, Am. Soc. Test. Mater. Tech. Publ., 528, 6-36.
[13]Teh, S. J., Adams, S.M. and Hinton, D.E. (1997)
Histopathological biomarkers in feral fresh water fish
populations exposed to different types of contaminant stress.
Aquatic Toxicol., 37:51-70.
[14]Thophon, S., Kruatrachue, M., Upathan, E.S., Pokethitiyook,
P., Sahaphong, S. and Jarikhuan S. (2003) Histopathological
alteraions of white sea bass, Lates calcarifer in acute and
subchronic, Environ. Poll., 121: 307-320.
[15]WHO/IPCS (1996) Principles and methods for assessing
direct immune toxicity associated with exposure to
chemicals. Environ. Health Criteria 180: 110-112.
Source of Financial Support: UGC (WRO) Pune
Conflict of interest: Nil

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Histopathological Impact of Dimethoate on the Kidney of Freshwater Fish, Garra mullya (Sykes)

  • 1. Int. J. Life. Sci. Scienti. Res., 2(4): 451-453 (ISSN: 2455-1716) Impact Factor 2.4 JULY-2016 http://ijlssr.com IJLSSR © 2015 All rights are reserved Page 451 Histopathological Impact of Dimethoate on the Kidney of Freshwater Fish, Garra mullya (Sykes) Borane VR* Department of Zoology Jijamata Arts, Science and Commerce College, Nandurbar, Maharashtra, India * Address for Correspondence: Dr. Borane V. R, Head cum Associate Professor, Department of Zoology, Jijamata Arts, Sci. and Comm. College, Nandurbar, India Received: 12 May 2016/Revised: 28 May 2016/Accepted: 16 June 2016 ABSTRACT- The present investigation was carried out to the effect of dimethoate on histopathological changes in kidney of freshwater fish, Garra mullya. Fishes was exposed to sub lethal concentration of dimethoate (0.0238ppm of 96hrs.) for 7, 14, 21 days. Fishes exposed to dimethoate were characterized by loosening of haemopoietic tissue, uriniferous tubules have lost their original appearance, vacuolated cytoplasm, degeneration in the epithelial cells of renal tubule, narrowing of the tubular lumen and damaged glomeruli. The lesions in the vital organ might have resulted in physiological and metabolical dysregulations. In chronic treatment of dimethoate exposure may pose serious threat to fish health and affect their population. Key-words- Dimethoate, Histopathology, Kidney, Garra mullya -------------------------------------------------IJLSSR----------------------------------------------- INTRODUCTION The availability of adequate water supply in terms of both quantity and quality is essential for human existence. However, our exploitation of water resources to fulfill the growing need of man has exerted tremendous pressure, thereby deteriorating its quality substantially. Hence, conservation of water has become of utmost importance. The water pollution is thus no longer considered to be an aesthetic problem, but a serious economic and public health problem as well. Unfortunately, raw or inadequately treated sewage of millions of people still flow into our lakes and rivers, creating several kinds of disorders. The release of discharge of large number of pollutants, especially heavy metals and pesticides, pose a threat to human life (Saikia, 1988). Pollution of aquatic environment by heavy metals is an extremely important and serious problem and has attracted the attention of the scientists all over the world. Pesticides are occasionally used indiscriminately in large amounts causing environmental pollution and potential health hazards. Access this article online Quick Response Code: Website: www.ijlssr.com DOI: 10.21276/ijlssr.2016.2.4.20 Dimethoate is systemic insecticides produced by reacting salts of Dimethyldithio-phosphoric acid with N-methylchloroaecetamide, in aqueous medium in the presence of some organic solvents is widely used against a broad range of insects and mites and is also used for indoor control of houseflies. The extensive use of DM poses a health hazard to animals and humans because of its persistence in soil and crops (WHO/IPCS, 1996). One of the major agricultural chemical groups is pesticide which play important role in increasing agricultural productivity through controlling pest. But on the other hand, they cause much damage to the non-target organisms both in terrestrial and aquatic environment. Fishes are accumulating pollutants directly from contaminated water and indirectly via food chain (Sasaki, et al., 1997). The runoff from treated areas enters the river and aquaculture ponds that are supplied by rivers and adversely affect the quality of water surfaces and creates hazards for aquatic life resulting in serious damage to non-target species, including fishes (Bondarenko, et al., 2004). Histopathology deals with the study of pathological changes induced in the microscopically structure of body tissue. Any alteration in normal structure of tissue indicates presence of disease or the effect of toxic substances like heavy metal and pesticides. Sprague, (1973) described histopathology as important tool for evaluating the action of any toxicant at tissue level. Histopathology provides data concerning tissue damage. Histopathological alterations can be used as indicators for the effect of various anthropogenic pollutants on organisms and are a reflection of overall health of the entire population in the ecosystem. These Research Article (Open access)
  • 2. Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 4 http://ijlssr.com IJLSSR © 2015 All rights are reserved Page 452 histopathological biomarkers are closely related to the other biomarkers of stress since many pollutants have to undergo metabolic activation in order to be able to provoke cellular change in the affected organism (Muhammad Ismail, et al., 2009). The present study was under taken to analyze the impact of chronic concentration of dimethoate in liver of fish, Garra mullya. MATERIALS AND METHODS Healthy adult fish, Garra mullya were collected from local river Shivan Dist. Nandurbar, India in the month of December, 2015. Fishes were washed with 0.1% of potassium per magnate (KMnO4) solution to avoid dermal infection. They were then rinsed in water and acclimatized to the laboratory conditions in the department of Zoology for two weeks in 500 l. capacity glass aquaria. Dead fish were removed immediately that such mortality may deplete dissolved oxygen with resultant effect on other fishes. During acclimatization fishes were fed with pieces of live earthworm on alternate days. Water also changed once in every day. The experiment was conducted natural and photoperiod of temperature 25·1 ± 3·20 C. Water quality was measure as per by APHA (2005), Conductivity- 0.64 ± 0.3, Dissolved O2 - 6.3±1.1 (ml/L), pH- 8.60 ± 0.3, Acidity- 2.5± 0.1, Alkalinity- 44.1 ± 0.5, Total hardness- 67.5 ± 0.3. LC50 of dimethoate for 96 hours was determined by probit analysis method (Finney, 1971). The animals were dissected and kidney tissues carefully removed. Tissues were immediately washed in 1% saline solution to remove the adhering mucus and blood and soaked between the blotting papers. The tissue from the control and exposed batches were taken out and preserved in aqueous Bouin’s fluid for 24-48 hrs. This was followed by successive dehydration in ascending grades of alcohol. Tissues were cleared in xylene and embedded in paraffin wax (at 58˚- 60˚ C.). The tissue was then processed routinely and prepared into paraffin block cut at 6μm thickness using microtome and stained with Haematoxyline and Eosin by Luna (1968). Standard histopathological procedures were followed for histopathological investigations, Roberts, (1989). Observations were taken under light microscope. RESULTS AND DISCUSSION Histopathological changes have been widely used as biomarkers in the evaluation of the health of fish exposed to contaminants, both in the laboratory (Thophon, et al., 2003) and field studies (The, et al., 1997). Histological studies revealed that the kidney sections from control fishes showed normal histoarchitecture, kidney is characterized by well built haemopoietic tissue, uriniferous tubules and glomerulus with clear Bowman’s capsule (Fig. 1). Kidney of fishes exposed to 0.0238ppm dimethoate for 7,14 and 21 days resulted in the Loosening of haemopoietic tissue, uriniferous tubules have lost their original appearance, vacuolated cytoplasm. The cells constituting the wall of uriniferous tubules have become completely destroyed. The lumen of uriniferous tubules has become greatly shrunken and deshaped. Expansion of space has taken place inside the renal corpuscle (Fig. 2 & 3). Kidney of fishes exposed to 0.0238 ppm dimethoate for 21 days resulted in loss of compactness of haemopoietic tissue as its cells got scattered, uriniferous tubules and glomeruli got deshaped and degenerated (Fig. 4). Fig. 1: Normal structure of Kidney showing well marked glomeruli and haemopoetic cells and renal tubules (H&E, 450X) Fig. 2: On Dimethoate treatment after 7 days structure of Kidney shows enlargement in haemopoetic tissue, vacuolation are observed (H&E, 450X) Fig. 3 On Dimethoate treatment after 14 days of Kidney shows cellular atrophy and shrinkage in lumen of renal tubule (H&E, 450X)
  • 3. Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 4 http://ijlssr.com IJLSSR © 2015 All rights are reserved Page 453 Fig.4 On Dimethoate treatment after 21 days of Kidney shows cellular atrophy and shrinkage in lumen of renal tubule (H&E, 450X) Figure 1: Kidney structure of control fish showing well built haemopoietic tissue, uriniferous tubules and glomerulus with clear Bowman’s H & E, X 450. Figure 2: Kidney of G.mullya exposed to dimethoate (0.0238ppm) for 7 days showing damaged haemopoitic tissue, uriniferous tubules, vacuolation and glomeruli H&E, X 450. Figure 3: After 14 days Kidney showing loosening of haemopoietic tissue, clustering of cells, damaged uriniferous tubules, vacuolation, narrowing of tubular lumen and expansion of Bowman’s space H&E, X 450. Figure 4: After 21 days Kidney showing showing severely damaged haemopoietic tissue, and uriniferous tubules H&E, X 450. Similar results have been reported by Cengiz, (2006) in Cyprinus carpio after acute exposure to deltamethrin. Bilal Ahmad (2011) reported the lesions in these vital organs might have resulted in physiologic and metabolic deregulations, which further led to behavioral alterations and growth impairment. CONCLUSION The lesions in the vital organ might have resulted in physiologic and metabolic dysregulations, which further led to behavioral alterations and growth impairment. In the long run, therefore, dimethoate exposures to even sub lethal concentrations may pose serious threat to fish health and affect their population. Dimethoate used to protect many fruits, vegetables and field crops against disease, hence farmer come direct contact it and may affect their health. REFERENCES [1] APHA AWWA and WPCF (2005) Standard methods for the examination of water and wastewater. 21st Edn.Washington DC USA. [2] Bilal Ahmad, Qureshi.T.A., Susan Manohar, Pinky Kaur, Rumysa Khaliq (2011) Effect of Cadmium Chloride on the Histoarchitecture of Liver and Kidney of a freshwater Catfish, Clarias Batrachus. International J. of Environ. Sci. 2(2),531-537. [3] Bondarenko, S., Gan, J., Haver D.L. and Kabashima, J.N. (2004) Persistence of selected organophosphate and carbamate insecticides in waters from a coastal watershed, Environmen. Toxicol. and chemistry, 23(11); 2649-2654. [4] Cengiz Elif. (2006) Gill and kidney histopathology in the freshwater fish, Cyprinus carpio after acute exposure to deltamethrin. Environmental Toxicology and Pharmacology, 22 (2); 200-204. [5] Finney, D.J., (1971) ‘Probit analysis’ Third edition, Cambridge University, Press. [6] Luna L.C (1968), manual of histologic staining methods. Armed Forces Institute of Pathology, 3 rd Ed. McGraw Hill Book Company, New York. [7] Muhammad Ismail, Rahat Ali., Tayyaba Ali, Usman Waheed, and Khan, Q.M. (2009) Evaluation of acute toxicity of profenofos and its effect on behavior pattern of fingling common carp (Cyprinus carpio. L.) Bull. Environ. Contam. Toxicol., 82; 569-573. [8] Reuber, M. D. (1984) Dimethoate, Environment Res.34:193. [9] Robert, R.J. (1989) Fish pathology (2’nd edition), London, Billier, Tindall. 11, 453. [10]Saika, D. K., Mathur, R. P. and Srivastava, S. K (1988), heavy metal in water and sediments of upper Ganga. Indian Journal of Environmental Helath, 31(1); 1117. [11]Sasaki, Y., Izumiyama, F., Nishidate, E., Ishibashi, S., Tsuda, S., Matsusaka, N., Asano, N., Saotome, K., Sofuni, T. and Hayashi, M. (1997) Detection of genotoxicity of polluted sea water using shellfish and the alkaline single-cell gel electrophoresis (SCE) assay: A preliminary study.Mutation. Res. 393; 133-139. [12]Sprague, J.B., (1973) The ABC’s of pollutant bioassay using fish. In biological methods for the assessment of water quality, Am. Soc. Test. Mater. Tech. Publ., 528, 6-36. [13]Teh, S. J., Adams, S.M. and Hinton, D.E. (1997) Histopathological biomarkers in feral fresh water fish populations exposed to different types of contaminant stress. Aquatic Toxicol., 37:51-70. [14]Thophon, S., Kruatrachue, M., Upathan, E.S., Pokethitiyook, P., Sahaphong, S. and Jarikhuan S. (2003) Histopathological alteraions of white sea bass, Lates calcarifer in acute and subchronic, Environ. Poll., 121: 307-320. [15]WHO/IPCS (1996) Principles and methods for assessing direct immune toxicity associated with exposure to chemicals. Environ. Health Criteria 180: 110-112. Source of Financial Support: UGC (WRO) Pune Conflict of interest: Nil