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HISTOLOGICAL STUDIES OF
LIVER OF MAJOR CARPS FROM
KEENJHAR LAKE.
Hi st ol ogy i s an i mpor t ant f i el d of f i sh
heal t h t hat can of t en det ect subt l e
condi t i ons or ear l y si gns of di sease not
easi l y r ecogni zed on gr oss exami nat i on.
Changes i n t he cel l ul ar l evel i n t he f unct i on
of key or gans ar e t he f i r st i ndi cat i ons of
mal adj ust ment t o st r essor s t hat may
event ual l y l ead t o poor heal t h or di sease.
A hi st ol ogi cal i nvest i gat i on r el at ed t o
upt ake of heavy met al pol l ut i on on t he
t i ssues of exposed f i sh coul d pr ovi de
val uabl e i nf or mat i on, and f or pr edi ct i ng human
heal t h r i sks.
An est abl i shed and compr ehensi ve dat abase of
f i sh hi st ol ogy coul d become an i nt egr al par t
of envi r onment al i mpact assessment s and coul d
Importance of Histology
Aims and Objectives
 Hi st ol ogi cal anal ysi s appear s t o be a
ver y sensi t i ve par amet er and i s cr uci al
i n det er mi ni ng cel l ul ar changes t hat may
occur i n t ar get or gans such as l i ver t o
r ef l ect i ng t he heal t h of an ent i r e
aquat i c ecosyst em.
 Shor t and l ong t er m exposur e per i ods may
si gni f i cant l y i nf l uence t he hi st ol ogi cal
damage and al t er at i ons caused by
exposur e t o heavy met al s.
 Heavy met al s (HMs) pol l ut i on i s of gr eat
concer n and i t s has har m f ul l ef f ect s on
aquat i c ani mal s, t o i nvest i gat e t he
Fi sh sampl es wer e col l ect ed at t he t hr ee
sampl i ng si t es f r om Keenj har Lake, i n
l i ve and mor i bund condi t i ons at t he f i sh
l andi ng cent er s.
Li ver sampl es wer e f i xed i n Boui ns’s
f i xat i ve f or 30 hour s. Than t he t i ssues
wer e decal ci f i ed t o r emove br i t t l eness
caused f r om aci di t y of f i xat i ve f or 14
hour s.
Ti ssues wer e kept under t he r uni ni ng t ap
wat er f or 2 hour s, af t er t hat t he t i ssues
wer e dehydr at ed f r om f ol l owi ng ser i es of
Material and Methods
Fi sh speci es Lead Cadmi um Ni ckel Zi nc
C. cat l a H.
0.881
0.003
0.851 0.0
09
0.91 0.
0095
0.884 0
.0095
L. rohi t a H.
0.867
0.009
0.835 0.0
085
0.946
0.0067
0.922 0
.0076
C. mri gal a H.
0.697
0.007
0.881 0.0
078
0.802
0.0078
0.841 0
.0085
Fish species Keenjhar Lake
Cirrihinus mrigala (Hamilton)
Tumor
Reduction of hepatocytes
Disrupted hepatic alignment
Necrosis
Leukocytes infiltration
Hyperemia
Cirrhosis
Aneurism
Hepatocytes vaculation
Hepatocytes with pyknotic nucleus
Hemorrhage
Labeo rohita (Hamilton)
Reduction of hepatocytes
Disrupted hepatic alignment
Necrosis
Leukocytes infiltration
Cirrhosis
Aneurism
Hepatocytes vaculation
Hepatocytes with pyknotic nucleus
Hyperemia
Catla catla (Hamilton)
Reduction of hepatocytes
Tumor
Disrupted hepatic alignment
Hyperemia
Hepatocytes vaculation
Cirrhosis
Cytolysis
Hepatocytes with pyknotic nucleus
Aneurysm
Conclusion
L. rohi t a, C. mri gal a and C. cat l a H. were sel ect ed f or
hi st ol ogi cal exami nat i on due t o t hei r popul ari t y as
f ood f i sh rel i shed t hroughout Asi a. Usual l y, t hese
speci es are cul t ured i n ponds and dhands (smal l
st andi ng wat er bodi es), owi ng t o f ast growt h-rat e and
hi gh economi cal val ue.
I t i s concl uded t hat t he hi st ol ogi cal di st ort i on
i ncreases wi t h t he i ncrease i n t oxi c i nf l ux. Lake
Keenj har has a l ow cont ent of wat erborne t oxi cant s;
however, hi st ol ogi cal anomal i es do occur, i f measures
are not i mpl ement ed t o mi ni mi ze t he exposure t o hi gh
l evel s of t oxi cant s, Lake Keenj har wi l l become
dyst rophi c, and t he l ocal popul at i on wi l l f ace soci o-
economi c di sast er.
Among t he f i sh speci es exami ned i n t he present st udy, C.
Measures must be t aken t o mi ni mi ze t he
cont ent of wat erborne t oxi cant s, t o prevent
or mi ni mi ze t he del et eri ous ef f ect s of
t oxi cant s on aquat i c organi sms and
consequent adverse ef f ect s on consumers,
especi al l y t hose l i vi ng i n t he vi ci ni t y of
Lake Keenj har. I t wi l l be i mport ant t o
moni t or t he met al s burden i n sedi ment s and
associ at ed bi ot a of Lake Keenj har.
Thank
s

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Latif presentation

  • 1.
  • 2. HISTOLOGICAL STUDIES OF LIVER OF MAJOR CARPS FROM KEENJHAR LAKE.
  • 3. Hi st ol ogy i s an i mpor t ant f i el d of f i sh heal t h t hat can of t en det ect subt l e condi t i ons or ear l y si gns of di sease not easi l y r ecogni zed on gr oss exami nat i on. Changes i n t he cel l ul ar l evel i n t he f unct i on of key or gans ar e t he f i r st i ndi cat i ons of mal adj ust ment t o st r essor s t hat may event ual l y l ead t o poor heal t h or di sease. A hi st ol ogi cal i nvest i gat i on r el at ed t o upt ake of heavy met al pol l ut i on on t he t i ssues of exposed f i sh coul d pr ovi de val uabl e i nf or mat i on, and f or pr edi ct i ng human heal t h r i sks. An est abl i shed and compr ehensi ve dat abase of f i sh hi st ol ogy coul d become an i nt egr al par t of envi r onment al i mpact assessment s and coul d Importance of Histology
  • 4. Aims and Objectives  Hi st ol ogi cal anal ysi s appear s t o be a ver y sensi t i ve par amet er and i s cr uci al i n det er mi ni ng cel l ul ar changes t hat may occur i n t ar get or gans such as l i ver t o r ef l ect i ng t he heal t h of an ent i r e aquat i c ecosyst em.  Shor t and l ong t er m exposur e per i ods may si gni f i cant l y i nf l uence t he hi st ol ogi cal damage and al t er at i ons caused by exposur e t o heavy met al s.  Heavy met al s (HMs) pol l ut i on i s of gr eat concer n and i t s has har m f ul l ef f ect s on aquat i c ani mal s, t o i nvest i gat e t he
  • 5. Fi sh sampl es wer e col l ect ed at t he t hr ee sampl i ng si t es f r om Keenj har Lake, i n l i ve and mor i bund condi t i ons at t he f i sh l andi ng cent er s. Li ver sampl es wer e f i xed i n Boui ns’s f i xat i ve f or 30 hour s. Than t he t i ssues wer e decal ci f i ed t o r emove br i t t l eness caused f r om aci di t y of f i xat i ve f or 14 hour s. Ti ssues wer e kept under t he r uni ni ng t ap wat er f or 2 hour s, af t er t hat t he t i ssues wer e dehydr at ed f r om f ol l owi ng ser i es of Material and Methods
  • 6. Fi sh speci es Lead Cadmi um Ni ckel Zi nc C. cat l a H. 0.881 0.003 0.851 0.0 09 0.91 0. 0095 0.884 0 .0095 L. rohi t a H. 0.867 0.009 0.835 0.0 085 0.946 0.0067 0.922 0 .0076 C. mri gal a H. 0.697 0.007 0.881 0.0 078 0.802 0.0078 0.841 0 .0085
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  • 16. Fish species Keenjhar Lake Cirrihinus mrigala (Hamilton) Tumor Reduction of hepatocytes Disrupted hepatic alignment Necrosis Leukocytes infiltration Hyperemia Cirrhosis Aneurism Hepatocytes vaculation Hepatocytes with pyknotic nucleus Hemorrhage Labeo rohita (Hamilton) Reduction of hepatocytes Disrupted hepatic alignment Necrosis Leukocytes infiltration Cirrhosis Aneurism Hepatocytes vaculation Hepatocytes with pyknotic nucleus Hyperemia Catla catla (Hamilton) Reduction of hepatocytes Tumor Disrupted hepatic alignment Hyperemia Hepatocytes vaculation Cirrhosis Cytolysis Hepatocytes with pyknotic nucleus Aneurysm
  • 17. Conclusion L. rohi t a, C. mri gal a and C. cat l a H. were sel ect ed f or hi st ol ogi cal exami nat i on due t o t hei r popul ari t y as f ood f i sh rel i shed t hroughout Asi a. Usual l y, t hese speci es are cul t ured i n ponds and dhands (smal l st andi ng wat er bodi es), owi ng t o f ast growt h-rat e and hi gh economi cal val ue. I t i s concl uded t hat t he hi st ol ogi cal di st ort i on i ncreases wi t h t he i ncrease i n t oxi c i nf l ux. Lake Keenj har has a l ow cont ent of wat erborne t oxi cant s; however, hi st ol ogi cal anomal i es do occur, i f measures are not i mpl ement ed t o mi ni mi ze t he exposure t o hi gh l evel s of t oxi cant s, Lake Keenj har wi l l become dyst rophi c, and t he l ocal popul at i on wi l l f ace soci o- economi c di sast er. Among t he f i sh speci es exami ned i n t he present st udy, C.
  • 18. Measures must be t aken t o mi ni mi ze t he cont ent of wat erborne t oxi cant s, t o prevent or mi ni mi ze t he del et eri ous ef f ect s of t oxi cant s on aquat i c organi sms and consequent adverse ef f ect s on consumers, especi al l y t hose l i vi ng i n t he vi ci ni t y of Lake Keenj har. I t wi l l be i mport ant t o moni t or t he met al s burden i n sedi ment s and associ at ed bi ot a of Lake Keenj har.