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Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels
IJVSAH
Histopathological Changes of Splanchnic Organs Induced
by Fipronil Toxicity in White Leghorn Cockerels
1Dheeraj Adhikari and *2Seema Agarwal
1,2Department of Pathology, College of Veterinary & Animal Sciences, G.B. Pant University of Agriculture and Technology,
Pantnagar-263 145, Udham Singh Nagar (Uttarakhand) INDIA
Fipronil, introduced by Rhone-Plunac, is a member of phenyl pyrazoles which have herbicidal effects.
Metabolic studies have showed that Fipronil can accumulate in fatty tissues, fish, fibre or food
crops. Limited investigations have been carried on effect of Fipronil on animals and man. Therefore,
present study was designed to study the effect of Fipronil toxicity in gross and histopathological
parameters in White Leghorn Cockerels. Twenty, one-month old white leg horn male chickens were
randomly divided into four groups of 5 birds each. Different doses of Fipronil were administered orally
through feed at 1, 5 and 10 ppm levels for 100 days, daily. The tissue from liver, kidney, spleen, bursa
of fabricius, testes and intestine were collected. The gross and histopathological changes were
severe in group 3 in comparison to group 2 and 1. It may be concluded that even low dose of Fipronil
has adverse effect on birds. These ill effects are dependent on dose and duration of exposure of Fipronil.
Adequate measures should be taken to minimize the indiscriminate use of Fipronil, reducing poultry as
well as human exposure to it and its further environmental contamination.
Key words: Insecticides, Gross Parameters, Histopathological Parameters, Fipronil, White Leghorn Cockerels, Kidney,
Spleen, Bursa of Fabricius, Testes, Intestine
INTRODUCTION
The pesticides are classified as insecticides, fungicides,
weedicides, herbicides, nematodicides and rodenticides; of
which insecticides constitutes 77% of the total pesticides
used in different agricultural and animal husbandry practices
and in public health operations. About 50% of food
commodities are contaminated with pesticide residues in
India. Livestock and poultry are frequently exposed to
pesticide, drugs and environmental contaminants.
Through contaminated feed, water, air insecticides are
ingested and absorb in systemic circulation. They are
metabolized and excreted through the animal body.
However, some of the residue which remains inside body
gets deposited in the various body tissues and is
responsible for deleterious effect on various body organs.
Pesticides are present in air, soil and water which leave
their residue in food chain ((Ram et al., 1987; Kaushik et
al., 1991) causing deleterious effect on the health status of
man and animals including poultry. Prolonged exposure to
insecticides causes chronic neurological syndrome,
malignant tumours, immunosuppressive action,
teratogenic effect, abortion and decreased male fertility in
experimental animals (Nafstad et al., 1983; Meeker et al.,
2006; Yousef, 2010).
Fipronil was discovered and developed by Rhone-Poulenc
between 1985- 1987 and placed in the market in 1993. It is
the member of new and relatively small class of pesticides,
the phenyl pyrazoles, which are principally chemicals with a
herbicidal effect. (Rhone Poulenc, 1995). Chemically, it is a
(5-amino-1-[2,6-dichloro-4-(trifluoromethyl) phenyl]-4-[tri
fluoromethyl) sulfinyl]-1H-pyrzole). It was registered as a
pesticide in the United States in 1996 (Bobe et al., 1998).
Fipronil or its metabolite noncompetitively inhibits GABA-
induced ion influx by targeting the GABA-regulated chloride
channels in insects. (Cole et al., 1993) Fipronil binding
blocks the inhibitory action of GABA, leading to hyper
excitation, and in appropriate concentrations even death
(Bobe et al., 1998). Fipronil exhibits >500-fold selective
toxicity to insects over mammals mainly because of
differences in affinity in receptor binding between insect and
*Corresponding Author: Seema Agarwal, Department of
Pathology, College of Veterinary & Animal Sciences, G.B.
Pant University of Agriculture and Technology, Pantnagar-
263 145, Udham Singh Nagar (Uttarakhand) INDIA.
Email: seema_patho@rediffmail.com
Research Article
Vol. 6(1), pp. 062-068, July, 2020. © www.premierpublishers.org ISSN: 8991-0338
International Journal of Veterinary Science and Animal Husbandry
Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels
Adhikari and Agarwal 63
mammalian receptor (Cole et al., 1993; Grant et al., 1998;
Hainzl et al., 1998; Kamijima and Casida, 2000; Ratra et
al., 2001; Zhao et al.,2005). Fipronil binds more tightly to the
GABAA receptor in insects than mammals.
Fipronil is sold commercially under various trade names
including Icon, Regent, Ascend, Termidor, Chipko,
Goliath, Chipko Choice and Adonis for agriculture use. It is
available in a wide range of formulations including
dispersible granule (WG), micro granule (GR), flowable
solid (FS), soluble concentrate (SC) and ultra-low volume
(ULV). It is also sold as veterinary product for tick, mite and
flea control on pet and domestic stock under the trade
names Frontline and Top spot. (Rhone Poulenc, 1996).
Fipronil is classified as a WHO Class II moderately hazardous
pesticide. The U.S. EPA classified Fipronil as “Group C –
possible human carcinogen” based on “increase in thyroid
follicular cell tumours in both sexes of the rat”. There was no
report regarding effect of Fipronil on the white leghorn
chicken involving histopathological parameters. Therefore,
present investigation was planned to study the effect of
Fipronil at different dose rate on gross and histopathological
parameters in white leghorn chickens.
MATERIALS AND METHODS
Twenty white leg horn male chickens of one-month old
weighing about 150 to 200 gms were procured and kept at
Instructional Poultry Farm Nagla, Pantnagar. The birds in
poultry shed in deep litter system under standard
management conditions and were randomly divided into
four groups of 5 birds each. After one week of adaptation
period, different doses of Fipronil were administered orally
through feed at 1, 5 and 10 ppm levels to groups G1, G2
and G3 respectively for 100 days daily. The birds of group
“C” served as control.
The birds were euthanized at 100 days. The tissue pieces
from liver, kidney, spleen, bursa of fabricius, testes, and
intestine was collected in 10% formal saline solution.
Formalin fixed tissue were dehydrated in increasing
strength of alcohol, cleared in xylene and embedded in
paraffin blocks. Paraffin embedded sections were cut at 4-
5 micrometer thickness and stained with hematoxylin and
eosin following the procedure of Culling (1975) and Lillie
(1976).
RESULT
Pathological changes
1. Gross pathology
On post-mortem examination the experimental birds from
group G1 revealed mild lesions. However, birds from
group G2 and G3 severe congestion of intestine, liver,
kidney and lung. Degeneration and necrosis of spleen,
bursa, liver, and testis was highly appreciated in G2 and
G3.
2. Histopathology
The tissue samples of kidneys, liver, spleen, intestine,
testes and bursa of Fabricius from the sacrificed birds were
collected for histopathological examination.
Kidney
Mild degeneration of tubular epithelium and glomerular tuft
was seen in group G1. Degeneration of tubular epithelium,
glomerular tuft and interstitial haemorrhage was seen in
group G2. Severe necrosis of tubular epithelium,
glomerular tuft, severe interstitial haemorrhage and cystic
dilatation of tubules was seen in group G3. Changes
observed in kidney of group G1, G2 and G3 at the end of
study are shown in Plate No. 4.1, 4.2 and 4.3 respectively.
Liver
Various stage of degeneration, distortion of hepatic cord
and dilatation of hepatic sinusoids was seen in Hepatocyte
of liver of group G1. Degeneration, necrosis of hepatocyte,
distortion of hepatic cord with haemorrhage was seen in
liver of group G2. Extensive degeneration of hepatocyte,
dilatation of hepatic sinusoids with extensive haemorrhage
was seen in liver of group G3. Changes observed in liver
of group G1, G2 and G3 at the end of study are shown in
Plate No. 4.4, 4.5 and 4.6 respectively.
Spleen
Mild necrosis and paucity of cells was seen in spleen of
group G1. Necrosis and paucity of cells with severe
haemorrhage was seen in spleen of group G2. Severe
necrosis and rarefaction of lymphoid cells with extensive
haemorrhage was seen in spleen of group G3. Changes
observed in spleen of group G1, G2 and G3 at the end of
study are shown in Plate No. 4.7, 4.8and 4.9 respectively.
Intestine
Mild desquamation and disruption of villi was seen in the
intestine of group G1. Depletion of villi with congestion of
mucosa was seen in the intestine of group G2. Severe
disruption of villi and desquamation of epithelium was seen
in intestine of group G3. Changes observed in intestine of
group G3 at the end of study are shown in Plate No. 4.10
and 4.11 at different magnification.
Testis
Mild degeneration of seminiferus tubules of testis was
seen group G1. Degeneration and necrosis of
seminiferous tubules of testis was seen in group G2.
Severe degeneration and necrosis of seminiferous tubules
Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels
Int. J. Vet. Sci. Anim. Husb. 64
of testis was seen in group G3. Changes observed in
seminiferus tubules of testis of group G2 and G3 at the end
of study are shown in Plate No. 4.12 and 4.13 respectively.
Bursa of Fabricius
Mild degeneration of lymphocyte in lymphoid follicles of
bursa of Fabricius was seen in group G1. Degeneration
and depletion of lymphocyte in lymphoid follicles bursa of
Fabricius was seen in group G2. Severe degeneration and
necrosis of lymphocyte in lymphoid follicle of bursa of
Fabricius was observed in group G3. Changes observed
in bursa of Fabricius of group G1, G2 and G3 at the end of
study are shown in Plate No. 4.14, 4.15 and 4.16
respectively.
DISCUSSION
In tissue samples of liver and kidney the degenerative and
necrotic changes were severe in G3 group in comparison
to G2 group. Likewise, severe changes were reported in
tissue samples of intestine, testis, spleen and Bursa of
Fabricius in G3 group in comparison to G2 group. The
histopathological changes were mild in G1 group in
comparison to G2 group. These findings were consistent
with the studies by other scientists demonstrating toxic
effects of the pesticides. Peters conducted short term
repeated dose on using Sprague Dwaley CD rats at 0, 25,
50, 100, 200 and 400 ppm Fipronil in the diet for 4 weeks.
Study showed enlargement of the liver in some rats, mainly
at 200 and 400 ppm, with generalised minimal hepatocyte
enlargement in groups from 100 ppm. At the microscopic
level, thyroid follicular hypertrophy (generally minimal, but
moderate in some males at 200 and 400 ppm) was found
in most treated animals at all doses, and not in controls.
Peters et al. (1990)
A subchronic study was performed by Holmes (1991b) on
rats using Fipronil in the diet at 0, 5, 30 or 300 ppm for 13
weeks. Fatty vacuolation of the liver was seen in all
groups, including controls, but with the exception of an
increased incidence of periacinar vacuolation in 300 ppm
males, was not considered treatment-related. Increased
incidence of follicular cell hypertrophy and hyperplasia was
seen in both sexes at 300 ppm.
In another study Holmes (1991c) administered Fipronil in
gelatin capsules to groups of Beagle dogs (4/sex/group) at
doses of 0.5, 2.0 and 10 mg/kg bw/d for 13 weeks.
Microscopically, follicular and perifollicular atrophy of the
mesenteric lymph nodes were observed in one dog at 10
mg/kg bw/d, and cortical atrophy of the thymus in another.
Broadmeadew (1993) conducted a study on Charles River
CD-1 strain mice (72/sex/group) using Fipronil (purity
95.4%) in the diet at levels of 0, 0.1, 0.5, 10 or 30 ppm,
equal to (males/females) 0/0, 0.01/0.01, 0.05/0.06, 1.2/1.2,
3.4/3.6 mg/kg bw/day. Twenty/sex/group was treated for
53 weeks (toxicity phase) and 52/sex/group for 78 weeks
(oncogenicity phase). Statistically, a significant increase in
the incidence of periacinar microvesicular vacuolation was
found in the livers of males treated at 10 or 30 ppm in both
the toxicity and oncogenicity phases. In the oncogenicity
phase, male mice treated at ≥10 ppm showed an
increased incidence of chronic degenerative changes in
the liver, including necrosis of occasional cells and
apoptosis, increased ploidy, hypertrophy and
degeneration of periacinar hepatocytes, chronic
inflammation and bile stasis. Male mice in the oncogenicity
phase receiving 30 ppm showed a higher (but not
statistically significant) incidence of malignant
hepatocellular tumours. One hepatocellular carcinoma
was also found in a 30 ppm mouse in the toxicity phase of
the study.
Aughton (1993) performed chronic study on CD rats
using Fipronil in the diet at levels of 0, 0.5, 1.5, 30 or
300 ppm. Study showed that in rats treated for 1 year
and assigned to the reversibility period, six (4/15 from
the 300 ppm group) had follicular cell tumours. When all
rats assigned to the oncogenicity phase were
considered together (irrespective of time of death), there
was a significant increase in benign follicular cell
adenomas for males (12/50) and females (8/50)
receiving 300 ppm, and for males receiving 30 (3/50) or
1.5 (5/50) ppm. The incidence of increased follicular cell
carcinomas was seen in male (5/50) and female (2/50)
rats receiving 300 ppm compared with controls.
Fipronil (95.4% purity) was administered to two
generations of Charles River CD strain rats by (King,
1992) at dietary levels of 0, 3, 30 or 300 ppm,
respectively equal to (males/females) 0/0, 0.25/0.27,
2.5/2.7 and 26/28 mg/kg bw/day. Livers of 300 ppm
females showed increased centriacinar fatty
vacuolation. Thyroids of 30 ppm males and of both
males and females receiving 300 ppm showed follicular
epithelial hypertrophy.
From the present study, it may be concluded that even
a low dose of Fipronil has adverse effects on gross and
histopathological features of different splanchnic organs
of white leghorn cockerels. Thereby, it has been
suggested that Fipronil at different toxic levels can
damage the general health of birds. It can also affect the
immune status of the birds due to its ill effects on
immunological organs. These ill effects depend on dose
and duration of Fipronil. Therefore, it is suggested that
adequate measures should be taken to minimize the
indiscriminate use of Fipronil to reduce further
environmental contamination and the health hazard to
poultry as well as humans.
Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels
Adhikari and Agarwal 65
Plate. 4.1- Microphotograph of kidney showing mild
degeneration of tubular epithelium and glomerular tuft in group
G1 (H&E 200x).
Plate. 4.2-Microphotograph of kidney showing
degeneration of tubular epithelium and glomerular tuft,
interstitial haemorrhage in group G2 (H&E 200x).
Plate. 4.3-Microphotograph of kidney showing severe
necrosis of tubular epithelium, glomerular tuft, severe
interstitial haemorrhage and cystic dilatation of tubules in
group G3 (H&E 200x).
Plate 4.4- Microphotograph of liver showing hepatocytes
at various stages of degeneration, distortion of hepatic
cords and dilatation of hepatic sinusoids in group G1 (H&E
400x).
Plate 4.5 - Microphotograph of liver showing degeneration
and necrosis of hepatocytes, distortion of hepatic cords
with haemorrhage in group G2 (H&E 400x).
Plate 4.6- Microphotograph of liver showing extensive
degeneration of hepatocytes, dilatation of hepatic
sinusoids with extensive haemorrhage in group G3 (H&E
400x).
Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels
Int. J. Vet. Sci. Anim. Husb. 66
Plate 4.7- Microphotograph of spleen showing mild
necrosis and paucity of cells in group G1 (H&E 100x).
Plate 4.8- Microphotograph of spleen showing necrosis
and paucity of cells with severe haemorrhage in group G2
(H&E 100x).
Plate 4.9- Microphotograph of spleen showing severe
necrosis and rarefaction of lymphoid cells with extensive
haemorrhage in group G3 (H&E 100x).
Plate 4.10- Microphotograph of intestine showing
disruption of villi and desquamation of villus epithelium in
group G2 (H&E 100x).
Plate 4.11- Microphotograph of intestine showing severe
disruption of villi and desquamation of epithelium in group
G3 (H&E 200x).
Plate 4.12- Microphotograph of testis showing
degeneration and necrosis of seminiferous tubules in
group G2 (H&E 100x).
Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels
Adhikari and Agarwal 67
Plate 4.13- Microphotograph of testis showing severe
degeneration and necrosis of seminiferous tubules in
group G3 (H&E 100x).
Plate 4.14- Microphotograph of bursa of Fabricius showing
mild degeneration of lymphocytes in lymphoid follicles of
in group G1 (H&E 200x).
Plate 4.15- Microphotograph of bursa of Fabricius showing
degeneration and depletion of lymphocytes in lymphoid
follicles in group G2 (H&E 200x).
Plate 4.16- Microphotograph of bursa of Fabricius showing
extensive degeneration and necrosis of lymphoid follicle in
group G3 (H&E 200x).
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Holmes P.1991."Toxicity study by dietary administration to
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Accepted 9 April 2020
Citation: Adhikari D, Agarwal S (2020). Histopathological
Changes of Splanchnic Organs Induced by Fipronil
Toxicity in White Leghorn Cockerels. International Journal
of Veterinary Science and Animal Husbandry 6(1): 062-
068
Copyright: © 2020 Adhikari and Agarwal. This is an open-
access article distributed under the terms of the Creative
Commons Attribution License, which permits unrestricted
use, distribution, and reproduction in any medium,
provided the original author and source are cited.

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Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels

  • 1. Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels IJVSAH Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels 1Dheeraj Adhikari and *2Seema Agarwal 1,2Department of Pathology, College of Veterinary & Animal Sciences, G.B. Pant University of Agriculture and Technology, Pantnagar-263 145, Udham Singh Nagar (Uttarakhand) INDIA Fipronil, introduced by Rhone-Plunac, is a member of phenyl pyrazoles which have herbicidal effects. Metabolic studies have showed that Fipronil can accumulate in fatty tissues, fish, fibre or food crops. Limited investigations have been carried on effect of Fipronil on animals and man. Therefore, present study was designed to study the effect of Fipronil toxicity in gross and histopathological parameters in White Leghorn Cockerels. Twenty, one-month old white leg horn male chickens were randomly divided into four groups of 5 birds each. Different doses of Fipronil were administered orally through feed at 1, 5 and 10 ppm levels for 100 days, daily. The tissue from liver, kidney, spleen, bursa of fabricius, testes and intestine were collected. The gross and histopathological changes were severe in group 3 in comparison to group 2 and 1. It may be concluded that even low dose of Fipronil has adverse effect on birds. These ill effects are dependent on dose and duration of exposure of Fipronil. Adequate measures should be taken to minimize the indiscriminate use of Fipronil, reducing poultry as well as human exposure to it and its further environmental contamination. Key words: Insecticides, Gross Parameters, Histopathological Parameters, Fipronil, White Leghorn Cockerels, Kidney, Spleen, Bursa of Fabricius, Testes, Intestine INTRODUCTION The pesticides are classified as insecticides, fungicides, weedicides, herbicides, nematodicides and rodenticides; of which insecticides constitutes 77% of the total pesticides used in different agricultural and animal husbandry practices and in public health operations. About 50% of food commodities are contaminated with pesticide residues in India. Livestock and poultry are frequently exposed to pesticide, drugs and environmental contaminants. Through contaminated feed, water, air insecticides are ingested and absorb in systemic circulation. They are metabolized and excreted through the animal body. However, some of the residue which remains inside body gets deposited in the various body tissues and is responsible for deleterious effect on various body organs. Pesticides are present in air, soil and water which leave their residue in food chain ((Ram et al., 1987; Kaushik et al., 1991) causing deleterious effect on the health status of man and animals including poultry. Prolonged exposure to insecticides causes chronic neurological syndrome, malignant tumours, immunosuppressive action, teratogenic effect, abortion and decreased male fertility in experimental animals (Nafstad et al., 1983; Meeker et al., 2006; Yousef, 2010). Fipronil was discovered and developed by Rhone-Poulenc between 1985- 1987 and placed in the market in 1993. It is the member of new and relatively small class of pesticides, the phenyl pyrazoles, which are principally chemicals with a herbicidal effect. (Rhone Poulenc, 1995). Chemically, it is a (5-amino-1-[2,6-dichloro-4-(trifluoromethyl) phenyl]-4-[tri fluoromethyl) sulfinyl]-1H-pyrzole). It was registered as a pesticide in the United States in 1996 (Bobe et al., 1998). Fipronil or its metabolite noncompetitively inhibits GABA- induced ion influx by targeting the GABA-regulated chloride channels in insects. (Cole et al., 1993) Fipronil binding blocks the inhibitory action of GABA, leading to hyper excitation, and in appropriate concentrations even death (Bobe et al., 1998). Fipronil exhibits >500-fold selective toxicity to insects over mammals mainly because of differences in affinity in receptor binding between insect and *Corresponding Author: Seema Agarwal, Department of Pathology, College of Veterinary & Animal Sciences, G.B. Pant University of Agriculture and Technology, Pantnagar- 263 145, Udham Singh Nagar (Uttarakhand) INDIA. Email: seema_patho@rediffmail.com Research Article Vol. 6(1), pp. 062-068, July, 2020. © www.premierpublishers.org ISSN: 8991-0338 International Journal of Veterinary Science and Animal Husbandry
  • 2. Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels Adhikari and Agarwal 63 mammalian receptor (Cole et al., 1993; Grant et al., 1998; Hainzl et al., 1998; Kamijima and Casida, 2000; Ratra et al., 2001; Zhao et al.,2005). Fipronil binds more tightly to the GABAA receptor in insects than mammals. Fipronil is sold commercially under various trade names including Icon, Regent, Ascend, Termidor, Chipko, Goliath, Chipko Choice and Adonis for agriculture use. It is available in a wide range of formulations including dispersible granule (WG), micro granule (GR), flowable solid (FS), soluble concentrate (SC) and ultra-low volume (ULV). It is also sold as veterinary product for tick, mite and flea control on pet and domestic stock under the trade names Frontline and Top spot. (Rhone Poulenc, 1996). Fipronil is classified as a WHO Class II moderately hazardous pesticide. The U.S. EPA classified Fipronil as “Group C – possible human carcinogen” based on “increase in thyroid follicular cell tumours in both sexes of the rat”. There was no report regarding effect of Fipronil on the white leghorn chicken involving histopathological parameters. Therefore, present investigation was planned to study the effect of Fipronil at different dose rate on gross and histopathological parameters in white leghorn chickens. MATERIALS AND METHODS Twenty white leg horn male chickens of one-month old weighing about 150 to 200 gms were procured and kept at Instructional Poultry Farm Nagla, Pantnagar. The birds in poultry shed in deep litter system under standard management conditions and were randomly divided into four groups of 5 birds each. After one week of adaptation period, different doses of Fipronil were administered orally through feed at 1, 5 and 10 ppm levels to groups G1, G2 and G3 respectively for 100 days daily. The birds of group “C” served as control. The birds were euthanized at 100 days. The tissue pieces from liver, kidney, spleen, bursa of fabricius, testes, and intestine was collected in 10% formal saline solution. Formalin fixed tissue were dehydrated in increasing strength of alcohol, cleared in xylene and embedded in paraffin blocks. Paraffin embedded sections were cut at 4- 5 micrometer thickness and stained with hematoxylin and eosin following the procedure of Culling (1975) and Lillie (1976). RESULT Pathological changes 1. Gross pathology On post-mortem examination the experimental birds from group G1 revealed mild lesions. However, birds from group G2 and G3 severe congestion of intestine, liver, kidney and lung. Degeneration and necrosis of spleen, bursa, liver, and testis was highly appreciated in G2 and G3. 2. Histopathology The tissue samples of kidneys, liver, spleen, intestine, testes and bursa of Fabricius from the sacrificed birds were collected for histopathological examination. Kidney Mild degeneration of tubular epithelium and glomerular tuft was seen in group G1. Degeneration of tubular epithelium, glomerular tuft and interstitial haemorrhage was seen in group G2. Severe necrosis of tubular epithelium, glomerular tuft, severe interstitial haemorrhage and cystic dilatation of tubules was seen in group G3. Changes observed in kidney of group G1, G2 and G3 at the end of study are shown in Plate No. 4.1, 4.2 and 4.3 respectively. Liver Various stage of degeneration, distortion of hepatic cord and dilatation of hepatic sinusoids was seen in Hepatocyte of liver of group G1. Degeneration, necrosis of hepatocyte, distortion of hepatic cord with haemorrhage was seen in liver of group G2. Extensive degeneration of hepatocyte, dilatation of hepatic sinusoids with extensive haemorrhage was seen in liver of group G3. Changes observed in liver of group G1, G2 and G3 at the end of study are shown in Plate No. 4.4, 4.5 and 4.6 respectively. Spleen Mild necrosis and paucity of cells was seen in spleen of group G1. Necrosis and paucity of cells with severe haemorrhage was seen in spleen of group G2. Severe necrosis and rarefaction of lymphoid cells with extensive haemorrhage was seen in spleen of group G3. Changes observed in spleen of group G1, G2 and G3 at the end of study are shown in Plate No. 4.7, 4.8and 4.9 respectively. Intestine Mild desquamation and disruption of villi was seen in the intestine of group G1. Depletion of villi with congestion of mucosa was seen in the intestine of group G2. Severe disruption of villi and desquamation of epithelium was seen in intestine of group G3. Changes observed in intestine of group G3 at the end of study are shown in Plate No. 4.10 and 4.11 at different magnification. Testis Mild degeneration of seminiferus tubules of testis was seen group G1. Degeneration and necrosis of seminiferous tubules of testis was seen in group G2. Severe degeneration and necrosis of seminiferous tubules
  • 3. Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels Int. J. Vet. Sci. Anim. Husb. 64 of testis was seen in group G3. Changes observed in seminiferus tubules of testis of group G2 and G3 at the end of study are shown in Plate No. 4.12 and 4.13 respectively. Bursa of Fabricius Mild degeneration of lymphocyte in lymphoid follicles of bursa of Fabricius was seen in group G1. Degeneration and depletion of lymphocyte in lymphoid follicles bursa of Fabricius was seen in group G2. Severe degeneration and necrosis of lymphocyte in lymphoid follicle of bursa of Fabricius was observed in group G3. Changes observed in bursa of Fabricius of group G1, G2 and G3 at the end of study are shown in Plate No. 4.14, 4.15 and 4.16 respectively. DISCUSSION In tissue samples of liver and kidney the degenerative and necrotic changes were severe in G3 group in comparison to G2 group. Likewise, severe changes were reported in tissue samples of intestine, testis, spleen and Bursa of Fabricius in G3 group in comparison to G2 group. The histopathological changes were mild in G1 group in comparison to G2 group. These findings were consistent with the studies by other scientists demonstrating toxic effects of the pesticides. Peters conducted short term repeated dose on using Sprague Dwaley CD rats at 0, 25, 50, 100, 200 and 400 ppm Fipronil in the diet for 4 weeks. Study showed enlargement of the liver in some rats, mainly at 200 and 400 ppm, with generalised minimal hepatocyte enlargement in groups from 100 ppm. At the microscopic level, thyroid follicular hypertrophy (generally minimal, but moderate in some males at 200 and 400 ppm) was found in most treated animals at all doses, and not in controls. Peters et al. (1990) A subchronic study was performed by Holmes (1991b) on rats using Fipronil in the diet at 0, 5, 30 or 300 ppm for 13 weeks. Fatty vacuolation of the liver was seen in all groups, including controls, but with the exception of an increased incidence of periacinar vacuolation in 300 ppm males, was not considered treatment-related. Increased incidence of follicular cell hypertrophy and hyperplasia was seen in both sexes at 300 ppm. In another study Holmes (1991c) administered Fipronil in gelatin capsules to groups of Beagle dogs (4/sex/group) at doses of 0.5, 2.0 and 10 mg/kg bw/d for 13 weeks. Microscopically, follicular and perifollicular atrophy of the mesenteric lymph nodes were observed in one dog at 10 mg/kg bw/d, and cortical atrophy of the thymus in another. Broadmeadew (1993) conducted a study on Charles River CD-1 strain mice (72/sex/group) using Fipronil (purity 95.4%) in the diet at levels of 0, 0.1, 0.5, 10 or 30 ppm, equal to (males/females) 0/0, 0.01/0.01, 0.05/0.06, 1.2/1.2, 3.4/3.6 mg/kg bw/day. Twenty/sex/group was treated for 53 weeks (toxicity phase) and 52/sex/group for 78 weeks (oncogenicity phase). Statistically, a significant increase in the incidence of periacinar microvesicular vacuolation was found in the livers of males treated at 10 or 30 ppm in both the toxicity and oncogenicity phases. In the oncogenicity phase, male mice treated at ≥10 ppm showed an increased incidence of chronic degenerative changes in the liver, including necrosis of occasional cells and apoptosis, increased ploidy, hypertrophy and degeneration of periacinar hepatocytes, chronic inflammation and bile stasis. Male mice in the oncogenicity phase receiving 30 ppm showed a higher (but not statistically significant) incidence of malignant hepatocellular tumours. One hepatocellular carcinoma was also found in a 30 ppm mouse in the toxicity phase of the study. Aughton (1993) performed chronic study on CD rats using Fipronil in the diet at levels of 0, 0.5, 1.5, 30 or 300 ppm. Study showed that in rats treated for 1 year and assigned to the reversibility period, six (4/15 from the 300 ppm group) had follicular cell tumours. When all rats assigned to the oncogenicity phase were considered together (irrespective of time of death), there was a significant increase in benign follicular cell adenomas for males (12/50) and females (8/50) receiving 300 ppm, and for males receiving 30 (3/50) or 1.5 (5/50) ppm. The incidence of increased follicular cell carcinomas was seen in male (5/50) and female (2/50) rats receiving 300 ppm compared with controls. Fipronil (95.4% purity) was administered to two generations of Charles River CD strain rats by (King, 1992) at dietary levels of 0, 3, 30 or 300 ppm, respectively equal to (males/females) 0/0, 0.25/0.27, 2.5/2.7 and 26/28 mg/kg bw/day. Livers of 300 ppm females showed increased centriacinar fatty vacuolation. Thyroids of 30 ppm males and of both males and females receiving 300 ppm showed follicular epithelial hypertrophy. From the present study, it may be concluded that even a low dose of Fipronil has adverse effects on gross and histopathological features of different splanchnic organs of white leghorn cockerels. Thereby, it has been suggested that Fipronil at different toxic levels can damage the general health of birds. It can also affect the immune status of the birds due to its ill effects on immunological organs. These ill effects depend on dose and duration of Fipronil. Therefore, it is suggested that adequate measures should be taken to minimize the indiscriminate use of Fipronil to reduce further environmental contamination and the health hazard to poultry as well as humans.
  • 4. Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels Adhikari and Agarwal 65 Plate. 4.1- Microphotograph of kidney showing mild degeneration of tubular epithelium and glomerular tuft in group G1 (H&E 200x). Plate. 4.2-Microphotograph of kidney showing degeneration of tubular epithelium and glomerular tuft, interstitial haemorrhage in group G2 (H&E 200x). Plate. 4.3-Microphotograph of kidney showing severe necrosis of tubular epithelium, glomerular tuft, severe interstitial haemorrhage and cystic dilatation of tubules in group G3 (H&E 200x). Plate 4.4- Microphotograph of liver showing hepatocytes at various stages of degeneration, distortion of hepatic cords and dilatation of hepatic sinusoids in group G1 (H&E 400x). Plate 4.5 - Microphotograph of liver showing degeneration and necrosis of hepatocytes, distortion of hepatic cords with haemorrhage in group G2 (H&E 400x). Plate 4.6- Microphotograph of liver showing extensive degeneration of hepatocytes, dilatation of hepatic sinusoids with extensive haemorrhage in group G3 (H&E 400x).
  • 5. Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels Int. J. Vet. Sci. Anim. Husb. 66 Plate 4.7- Microphotograph of spleen showing mild necrosis and paucity of cells in group G1 (H&E 100x). Plate 4.8- Microphotograph of spleen showing necrosis and paucity of cells with severe haemorrhage in group G2 (H&E 100x). Plate 4.9- Microphotograph of spleen showing severe necrosis and rarefaction of lymphoid cells with extensive haemorrhage in group G3 (H&E 100x). Plate 4.10- Microphotograph of intestine showing disruption of villi and desquamation of villus epithelium in group G2 (H&E 100x). Plate 4.11- Microphotograph of intestine showing severe disruption of villi and desquamation of epithelium in group G3 (H&E 200x). Plate 4.12- Microphotograph of testis showing degeneration and necrosis of seminiferous tubules in group G2 (H&E 100x).
  • 6. Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels Adhikari and Agarwal 67 Plate 4.13- Microphotograph of testis showing severe degeneration and necrosis of seminiferous tubules in group G3 (H&E 100x). Plate 4.14- Microphotograph of bursa of Fabricius showing mild degeneration of lymphocytes in lymphoid follicles of in group G1 (H&E 200x). Plate 4.15- Microphotograph of bursa of Fabricius showing degeneration and depletion of lymphocytes in lymphoid follicles in group G2 (H&E 200x). Plate 4.16- Microphotograph of bursa of Fabricius showing extensive degeneration and necrosis of lymphoid follicle in group G3 (H&E 200x). REFERENCES Aughton P. 1993. "Combined oncogenicity and toxicity study by dietary administration to CD rats for 104 week reversibility period on completion of 52 weeks of treatment. Review of Mammalian Toxicology and Metabolism/Toxicokinetics of Fipronil." Australian Pesticide and Veterinary Medicine Authority, Office of Chemical Safety and Environment Health, Australia, 113-115. Bobe A, Meallier P, Copper J and Coste CM. 1998. "Kinetic and mechanism of abiotic degradation of Fipronil." J. Agric. Food Chem. 46, no. 28: 34-39. Broadmeadow A. 1993. "Oncogenicity study by dietary administration to CD-1 mice for 78 weeks. Review of Mammalian Toxicology and Metabolism/Toxicokinetics of Fipronil." Australian Pesticide and Veterinary Medicine Authority, Office of Chemical Safety and Environment Health, Australia, 112-113. Cole LM, R Nicholson, and JE Casida. 1993. "Action of phenylpyrazole insecticide at the GABA-gated chloride channel." Pestic. Biochem. Physiol. 46: 47-54. Culling CFA.1975. “Handbook of Histology and Histochemical Technique.” 212-220. London: Butterworhs. Grant DB, J R Bloomquist, HH. Ayad, and AE Chalmers. 1990. "A comparison of mammal and insect: GABA receptor chloride channel." Pest. Sci. 30: 355-356. Hainzl D, LM Cole, and JE Casida. 1998. "Mechanism for selective toxicity of Fipronil insecticide and its sulphone metabolite and desulfinyl photoproduct." Chem. Res. Toxicol11: 1529-1535. Holmes P.1991. "Toxicity study by oral (capsule) administration to beagle dogs for 13 weeks. Review of Mammalian Toxicology and Metabolism/Toxicokinetics of Fipronil." Australian Pesticide and Veterinary Medicine Authority, Office of Chemical Safety and Environment Health, Australia, 111-112.
  • 7. Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels Int. J. Vet. Sci. Anim. Husb. 68 Holmes P.1991."Toxicity study by dietary administration to CD rats for 13 weeks. Review of Mammalian Toxicology and Metabolism/Toxicokinetics of Fipronil." Australian Pesticide and Veterinary Medicine Authority, Office of Chemical Safety and Environment, 110-111. Kamijima M, and JE Casida. 2000. "Regional modification of [3H]ethynyl-bicyclo-orthobenzoate binding in mouse GABEA receptor by endosulphan, Fipronil and avermectin B1a." Toxicol. Appl. Pharmacol., no. 160: 188-194. Kaushik CP, Agarwal HC, and MKK Pillai. 1991. "Dry or aerial fallout of OCs insecticides residue in Delhi." Indian Environ. Pollution, no. 71: 83-86. King VC. 1992. "Reproductive performance study in rats treated continuously through two successive generations. Review of Mammalian Toxicology and Metabolism/Toxicokinetics of Fipronil." Australian Pesticide and Veterinary Medicine Authority, Office of Chemical Safety and Environment Health, Australia, 117-118. Lillie RD. 1976. "Histopathological Techniques in Practical Histochemistry." Newyork: Mc Graw Hill. Meeker, J. D., Ryan, L., Barr, D. B. and Hauser, R. 2006. Exposure to non-persistent insecticides and male reproductive hormones. Epidemiology. 17: 61–68. Nafstad, I., Berge, G., Sannes, E. and Lyngest, A. 1983. Teratogenic effect of organophosphorus, fenchlorphos, compound in rabbits. Acta. Veterinaria. Scandinavica. 24 (3): 295–304. Peters DH, Stuart V, Crook D, Gibson WA, Gopinath C and Hadley J. 1990. “Toxicity to rat by dietary administration for 4 weeks. Review of Mammalian Toxicology and Metabolism/Toxicokinetics of Fipronil.” Australian Pesticide and Veterinary Medicine Authority, Office of Chemical Safety and Environment Health, Australia. Ram S, VJ Shivankar and BD Patial.1987. "Evaluation of endosulfan in fodder cowpea." J. Entom. Res., no. 10: 40-43. Rhone-poulenc.1995. Atelier international Fipronil/lute antiacridienne. Lyon, France: Rhone-Poulenc Agrochimie, Rhone-Poulnec. 1996. ‘Fipronil’ worldwide technical bulletin. Lyon, France: Rhone-Poulnec, Agrochimie, Yousef, M. I. 2010. Vitamin E modulates reproductive toxicity of pyrethroid lambda-cyhalothrin in male rabbits. Food Chem. Toxicol. 48 (5):1152–1159. Zhao X, JZ Yeh, VL Salgado and T Narahashi. 2005. “Sulfone metabolite of Fipronil blocks GABA- and glutamate activated chloride channels in mammalian and insect neurons.” Toxicol Sci, no. 84: 401- 402. Accepted 9 April 2020 Citation: Adhikari D, Agarwal S (2020). Histopathological Changes of Splanchnic Organs Induced by Fipronil Toxicity in White Leghorn Cockerels. International Journal of Veterinary Science and Animal Husbandry 6(1): 062- 068 Copyright: © 2020 Adhikari and Agarwal. This is an open- access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are cited.