dc.description.abstract |
An experiment to assess the changes in hematology, serum biochemistry and DNA integrity in
three fish species exposed to metals was conducted under two phases i.e. acute and chronic
exposure. During phase I, the experimental fish species i.e. Catla catla, Cirrhinus mrigala and
Labeo rohita were exposed to 96-hr LC50 of cadmium (Cd), copper (Cu), nickel (Ni) and zinc
(Zn). During phase II, all the fishes were exposed to sub-lethal (1/5th, 1/4th and 1/3rd of LC50)
concentrations of the metals for 30-day. During acute exposure, hematological parameters such
as red blood cells (RBCs), hemoglobin (Hb), hematocrit (Hct), white blood cells (WBCs),
mean cell volume (MCV), mean cell hemoglobin (MCH) and mean cell hemoglobin
concentrations (MCHC), and serum biochemical parameters such as sodium (Na), potassium
(K), chloride (Cl), albumin (Alb), total protein (TP), urea, glucose, aspartate aminotransferase
(AST) and alanine aminotransferase (ALT) were examined by collecting the blood samples of
control and metals exposed fish after 24-, 48-, 72- and 96-hr. To assess the DNA integrity the
liver samples of both control and metals exposed fishes were collected at each of the four
sampling hours. RAPD-PCR technique was used to evaluate the effect of metals on DNA
integrity of fishes. During chronic exposure, the blood and liver samples were collected after
15- and 30-day of exposure to study all the above mentioned parameters. Metals exposure to
the experimental fish species at 96-hr LC50 (acute exposure) and sub-lethal concentrations
(chronic exposure) caused significant variability (p<0.01) in hematological parameters as
compared to control. Copper exposure to the fish species had more pronounced effects as it
resulted in significantly (p<0.01) lower RBCs, Hb, Hct and higher WBCs, MCV, MCH,
MCHC while Zn exposure showed least toxic effect towards hematological parameters as
compared to other metals. The overall tendencies of the fish species to respond the toxicity of
metals by changing their hematological parameters followed the order: C. catla>L. rohita>C.
mrigala. Metals-induced changes in hematological parameters of all the fish species became
more conspicuous along with the increase in metals concentration i.e. 1/5th<1/4th<1/3rd of LC50.
Exposure of metals to the fish for different time durations resulted in significantly variable
toxic effects on hematological parameters. Among all the exposure durations of metals, the 96-
hr exposure caused maximum negative effects on all the fish species. The 30-day metals
exposure caused more toxic effects on all the hematological parameters of fishes as compared
to 15-day metals exposure. Fishes also exhibited significant (p<0.01) variability in serum
biochemical parameters under the exposure of metals in both acute and chronic phases.
Significantly (p<0.01) lower level of serum Na, Cl, Alb and TP were observed in fishes under
the exposure of Cu as compared to other metals while K, urea, glucose, AST and ALT levels
were higher. However, least toxic effect on all above mentioned biochemical parameters were
noticed in Zn exposed fishes. Among fish species, C. catla appeared more sensitive to metals
toxicity as compared to L. rohita and C. mrigala. Metals-induced changes in serum
biochemical parameters of all the fish species increased concomitantly with the increase in
metals concentration i.e. 1/5th<1/4th<1/3rd of LC50. In both acute and chronic phases the toxic
effects of metals on the above mentioned serum biochemical parameters became more severe
with the increase in exposure duration. During both acute and chronic exposure of metals, the
highest DNA damage in terms of percent genomic DNA template stability (% GTS) was
observed in Cu exposed fish while the Zn exposure to fish resulted in lowest DNA damage.
Regarding the response of fish to the acute toxicity, C. catla appeared more sensitive to toxicity
of all the metals followed by L. rohita and C. mrigala. In response to chronic exposure of the
metals C. mrigala showed higher DNA damage than L. rohita and C. catla. One third of LC50
of all the metals caused higher DNA damage in terms of GTS (%) while 1/5th of LC50 caused
least DNA damage in all the fish species. There were distinct squared Euclidean distances
among metals treated and control fishes when the cluster method was applied. The results
derived from numerical analysis revealed maximum squared Euclidean distance between Cu
treated fishes and the control. In all the fish species, duration based DNA damage was observed
during acute exposure of metals while during chronic exposure the DNA damage was both
concentration and duration dependent. This study proposed that the occurrence of toxic metals
in aquatic environment has strong impact on hematology, serum biochemistry and DNA
integrity of the fishes. The observed changes in these parameters may provide valuable
information concerning environmental conditions and risk assessment of aquatic organisms. |
en_US |