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INVESTIGATION ON THE TOXIC
EFFECTS OF LEAD NITRATE ON THE
FINGERLINGS OF Cyprinus Carpio
BY
Mr. KARTHIK.H.P
(PS183256)
Guide:
Dr. B.S Ramesh M.Sc., Ph.D
Head of the Department
P.G Department of Zoology
INTRODUCTION
 Industrial effluents contain suspended solids, pesticides, organic, inorganic and
various metal compounds which are major source of water pollution
 Discharge of heavy metals into river or any aquatic environment can change
both aquatic species diversity and ecosystem due to their toxicity and
accumulative behaviour
 The consequence of heavy metals pollution can be hazardous to man through
his food.
 The massive disposal of quantities of metal waste at land fills can lead to metal
pollution of ground and surface water
 Massive increases of humans population as leads to an exponential in
technology and industrial advantages all around world.
Conti……
 Fishes have been used in indicator for contamination of aquatic environment
for several years.
 Fishes act as the last link in the food chain in the aquatic environment they
may negatively influence the food safety when they get exposed to
contamination environment.
 Early detection of sub lethal effects of a chemical may be a basic element is
decoding about biodegradation and revitalization method at polluted site
 Fish live in a wide range of habitats are being altered by anthropogenic
influences.
SCOPE AND OBJECTIVES
 To evaluate the toxicity (LC50 ) of lead nitrate on fingerlings of
Common carp (Cyprinus carpio).
 To record the impact of lead nitrate on the behavioural changes of
Common carp (Cyprinus carpio).
 To determine the effect of lead nitrate on biochemical aspects in
specific organ tissue (i.e., gills, muscle and liver) of Common carp
(Cyprinus carpio).
 To assess the possible adverse effect of lead nitrate on the histology of
some organs (i.e., gills and muscle) in Common carp (Cyprinus carpio).
TEST ANIMALS :
 In present toxicological study the fingerlings of Common carp (Cyprinus
carpio) fish were selected as an experimental animal
Fingerlings (8± 1cms, 25± 1grams) of Cyprinus carp were collected from
the fisheries department, Bhadra reservoir project, Sivamogga,
Karnataka.
Plate 1 : Cyprinus carp
TOXICANT
Plate 2: Lead Nitrate
METHOD
 Bioassay Protocol:
 LC50-96h Determination
 Study of Behavioural Response
 Biochemical Analysis
 Estimation of Glucose by Anthrone method
 Estimation of Glycogen by Kemp's method
 Estimation Of Protein by Lowery's method
 Histology Analysis
Metal Exposure period in
Hours
Method LC50 Value
Lead nitrate 96 Graphical 3.7g/ L
LC50 value for lead nitrate metal exposure to fingerlings of Cyprinus carpio
Dose response showing mortality against lead nitrate concentration (g/L) for
fingerlings of cyprinus carpio
Toxicity Studies
BEHAVIOURAL STUDIES
Characteristics Concentration in Grams
2 2.5 3 3.5 3.7
Swimming ++ ++ + + +
Colour - + ++ ++ +++
Intermittent swarming - + + + ++
Jerky movement - + + + ++
Opercular movement ++ + + + -
Surfacing and air
gulping
+ + ++ ++ +++
(-) = Absent (++) = Moderate
(+) = Low (+++) = High Characteristics
Behavioural characteristics of Cyprinus carpio exposed to
lead Nitrate
GLUCOSE
The variation of glucose content in control and exposed
fish, trials represented in Glucose content (mg/g) in the gills and
muscle tissue was estimated after exposing the fingerlings for
96hrs (LC50 value of lead nitrate 3.7g/L ). In that the exposed
muscle found to have (0.168mg/g) and gills (0.107mg/g),
showed increased in glucose level as contrast to the controlled
fingerling muscle (0.135mg/g) and gills (0.085mg/g).
BIOCHEMICAL CHANGES IN FISH
Sl. No Tissue Sample Result
Control(mg/g) Exposed(mg/g)
1 Muscle 0.135 0.168
2 Gills 0.085 0.107
Glucose content in tissue of fingerlings Cyprinus carpio exposed to lethal
concentration (96hrs) of lead nitrate
Glucose content in the tissue of the cyprinus carpio fingerlings
GLYCOGEN
 Glycogen content (mg/g) in the gills and muscle tissue
was estimated after exposing the fingerlings for 96 hrs
(LC50 value of lead nitrate 3.7g/L) was represented in. In
that the exposed muscle (0.29mg/g) and gills (0.34mg/g),
showed decrease in glycogen level as compared to the
controlled fingerling muscle (0.36mg/g) and gills
(0.42mg/g).
 Glycogen content in the tissue of Cyprinus carpio fingerling
exposed to lethal concentration (96h) of lead nitrate
Sl. No Tissue Sample Result
Control(mg/g) Exposed(mg/g)
1 Muscle 0.36 0.29
2 Gills 0.42 0.34
Glycogen content in the Tissue of the cyprinus carpio fingerlings
PROTEIN
 The variation of protein content in fish control and exposed trails
represented in Protein content (mg/g) in the muscle and gills tissue
was estimated after exposing the fingerlings for 96hrs (LC50 value of
lead nitrate 3.7g/l). In exposed fishes, muscle (4.1mg/g) and gills
(5.2mg/gm), showed decrease in protein level as contrast to the
controlled fingerling muscle (5.5mg/g) and gills (6.2mg/g).
 Protein content in the tissue of Cyprinus carpio fingerlings exposed to
lethal concentration (96hrs) of lead nitrate
Sl. No Tissue Sample Result
Control(mg/g) Exposed(mg/g)
1 Muscle 5.5 4.1
2 Gills 6.2 5.2
Protein content in the tissue of the cyprinus carpio fingerlings
HISTOLOGICAL ANALYSIS
Plate.4 : Gills of Cyprinus carpio in
control shows no changes (control)
Plate.5 : Gills of Cyprinus carpio exposed
shows desquamation of epithelial lining
Gills
Plate.6 : Muscle of Cyprinus carpio
showed no changes (Control)
Plate.7 : Muscle of Cyprinus carpio exposed
shows Muscle bundle degeneration
Muscle
CONCLUSION
 Overall, the study has shown that the lead nitrate metal is toxic to Cyprinus
carpio.
 Fishes exposed to acute lethal concentrations of the metal resulted in
significant behavioural, biochemical and histopathological alterations.
 These changes suggest that the treated fish are faced with serious metabolic
crisis.
 The random destruction and structural alterations in gills, liver and muscle
in the exposed fishes are indicative of stress mediated production.
 The results clearly indicate that the addition of metal to the water body may
be threat to aquatic flora and fauna
Thank You

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Karthik ppt

  • 1. INVESTIGATION ON THE TOXIC EFFECTS OF LEAD NITRATE ON THE FINGERLINGS OF Cyprinus Carpio BY Mr. KARTHIK.H.P (PS183256) Guide: Dr. B.S Ramesh M.Sc., Ph.D Head of the Department P.G Department of Zoology
  • 2. INTRODUCTION  Industrial effluents contain suspended solids, pesticides, organic, inorganic and various metal compounds which are major source of water pollution  Discharge of heavy metals into river or any aquatic environment can change both aquatic species diversity and ecosystem due to their toxicity and accumulative behaviour  The consequence of heavy metals pollution can be hazardous to man through his food.  The massive disposal of quantities of metal waste at land fills can lead to metal pollution of ground and surface water  Massive increases of humans population as leads to an exponential in technology and industrial advantages all around world. Conti……
  • 3.  Fishes have been used in indicator for contamination of aquatic environment for several years.  Fishes act as the last link in the food chain in the aquatic environment they may negatively influence the food safety when they get exposed to contamination environment.  Early detection of sub lethal effects of a chemical may be a basic element is decoding about biodegradation and revitalization method at polluted site  Fish live in a wide range of habitats are being altered by anthropogenic influences.
  • 4. SCOPE AND OBJECTIVES  To evaluate the toxicity (LC50 ) of lead nitrate on fingerlings of Common carp (Cyprinus carpio).  To record the impact of lead nitrate on the behavioural changes of Common carp (Cyprinus carpio).  To determine the effect of lead nitrate on biochemical aspects in specific organ tissue (i.e., gills, muscle and liver) of Common carp (Cyprinus carpio).  To assess the possible adverse effect of lead nitrate on the histology of some organs (i.e., gills and muscle) in Common carp (Cyprinus carpio).
  • 5.
  • 6. TEST ANIMALS :  In present toxicological study the fingerlings of Common carp (Cyprinus carpio) fish were selected as an experimental animal Fingerlings (8± 1cms, 25± 1grams) of Cyprinus carp were collected from the fisheries department, Bhadra reservoir project, Sivamogga, Karnataka. Plate 1 : Cyprinus carp
  • 8. METHOD  Bioassay Protocol:  LC50-96h Determination  Study of Behavioural Response  Biochemical Analysis  Estimation of Glucose by Anthrone method  Estimation of Glycogen by Kemp's method  Estimation Of Protein by Lowery's method  Histology Analysis
  • 9.
  • 10. Metal Exposure period in Hours Method LC50 Value Lead nitrate 96 Graphical 3.7g/ L LC50 value for lead nitrate metal exposure to fingerlings of Cyprinus carpio Dose response showing mortality against lead nitrate concentration (g/L) for fingerlings of cyprinus carpio Toxicity Studies
  • 11. BEHAVIOURAL STUDIES Characteristics Concentration in Grams 2 2.5 3 3.5 3.7 Swimming ++ ++ + + + Colour - + ++ ++ +++ Intermittent swarming - + + + ++ Jerky movement - + + + ++ Opercular movement ++ + + + - Surfacing and air gulping + + ++ ++ +++ (-) = Absent (++) = Moderate (+) = Low (+++) = High Characteristics Behavioural characteristics of Cyprinus carpio exposed to lead Nitrate
  • 12. GLUCOSE The variation of glucose content in control and exposed fish, trials represented in Glucose content (mg/g) in the gills and muscle tissue was estimated after exposing the fingerlings for 96hrs (LC50 value of lead nitrate 3.7g/L ). In that the exposed muscle found to have (0.168mg/g) and gills (0.107mg/g), showed increased in glucose level as contrast to the controlled fingerling muscle (0.135mg/g) and gills (0.085mg/g).
  • 13. BIOCHEMICAL CHANGES IN FISH Sl. No Tissue Sample Result Control(mg/g) Exposed(mg/g) 1 Muscle 0.135 0.168 2 Gills 0.085 0.107 Glucose content in tissue of fingerlings Cyprinus carpio exposed to lethal concentration (96hrs) of lead nitrate Glucose content in the tissue of the cyprinus carpio fingerlings
  • 14. GLYCOGEN  Glycogen content (mg/g) in the gills and muscle tissue was estimated after exposing the fingerlings for 96 hrs (LC50 value of lead nitrate 3.7g/L) was represented in. In that the exposed muscle (0.29mg/g) and gills (0.34mg/g), showed decrease in glycogen level as compared to the controlled fingerling muscle (0.36mg/g) and gills (0.42mg/g).
  • 15.  Glycogen content in the tissue of Cyprinus carpio fingerling exposed to lethal concentration (96h) of lead nitrate Sl. No Tissue Sample Result Control(mg/g) Exposed(mg/g) 1 Muscle 0.36 0.29 2 Gills 0.42 0.34 Glycogen content in the Tissue of the cyprinus carpio fingerlings
  • 16. PROTEIN  The variation of protein content in fish control and exposed trails represented in Protein content (mg/g) in the muscle and gills tissue was estimated after exposing the fingerlings for 96hrs (LC50 value of lead nitrate 3.7g/l). In exposed fishes, muscle (4.1mg/g) and gills (5.2mg/gm), showed decrease in protein level as contrast to the controlled fingerling muscle (5.5mg/g) and gills (6.2mg/g).
  • 17.  Protein content in the tissue of Cyprinus carpio fingerlings exposed to lethal concentration (96hrs) of lead nitrate Sl. No Tissue Sample Result Control(mg/g) Exposed(mg/g) 1 Muscle 5.5 4.1 2 Gills 6.2 5.2 Protein content in the tissue of the cyprinus carpio fingerlings
  • 18. HISTOLOGICAL ANALYSIS Plate.4 : Gills of Cyprinus carpio in control shows no changes (control) Plate.5 : Gills of Cyprinus carpio exposed shows desquamation of epithelial lining Gills
  • 19. Plate.6 : Muscle of Cyprinus carpio showed no changes (Control) Plate.7 : Muscle of Cyprinus carpio exposed shows Muscle bundle degeneration Muscle
  • 20. CONCLUSION  Overall, the study has shown that the lead nitrate metal is toxic to Cyprinus carpio.  Fishes exposed to acute lethal concentrations of the metal resulted in significant behavioural, biochemical and histopathological alterations.  These changes suggest that the treated fish are faced with serious metabolic crisis.  The random destruction and structural alterations in gills, liver and muscle in the exposed fishes are indicative of stress mediated production.  The results clearly indicate that the addition of metal to the water body may be threat to aquatic flora and fauna