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Effect of Zinc Chloride (LC-50) on physicochemical parameters of water
upon exposure to Ophiocephalus punctatus
Keywords:
Zinc, Physico-chemical parameter, Ophiocephalus punctatus.
007-012 | JRAS | 2012 | Vol 1 | No 1
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Authors:
Swapan S. Bacher and
Arun M. Chilke.
Institution:
Division of Toxicology and
Biomonitoring, Department
of Zoology, Shree Shivaji
Arts, Commerce and Science
College, Rajura-442805
(India).
Corresponding author:
Arun M. Chilke.
Email:
achilke.2011@rediffmail.com
Web Address:
http://ficuspublishers.com/
documents/AS0007.pdf
Dates:
Received: 05 Mar 2012 /Accepted: 15 Mar 2012 /Published: 04 Apr 2012
Article Citation:
Swapan S. Bacher and Arun M. Chilke.
Effect of Zinc Chloride (LC-50) on physicochemical parameters of water upon exposure
to Ophiocephalus punctatus.
Journal of Research in Animal Sciences (2012) 1: 007-012
An International Online Open Access
Publication group
Original Research
JournalofResearchinAnimalSciences
Journal of Research in Animal Sciences
ABSTRACT:
Zinc is an essential element and cause deleterious effect at high
concentration to both the animals and plants. In the present study, we observed that
the Zinc chloride at lethal concentration fifty alters the behavior of fish which also
change the physico-chemical properties of water. It was observed that the Zinc
chloride steadily increased the pH, conductivity, free carbon dioxide and total
alkalinity of water from 24 to 96 hrs, whereas the dissolved oxygen concentration in
water was gradually decreased. It is concluded that the increase in pH, conductivity,
free carbon dioxide and total alkalinity of water and decrease in oxygen could be due
to increase in the metabolic processes of Ophiocephalus punctatus upon exposure to
zinc chloride at lethal concentration 44.25 mg/l.
Journal of Research in
Animal Sciences
An International Open Access Online
Research Journal
INTROCUTION:
Heavy metals accumulate in the aquatic
organism through various sources like sediments, soil
erosion and runoff, air depositions of dust, aerosol, and
discharge of waste water (Labonne et al., 2001; Goodwin
et al., 2003). But majority of aquatic ecosystems are
greatly affected by the industrial waste containing variety
of heavy metals. Heavy metals from industries not only
disturb the aquatic environment but leads to
environmental health hazards (Shukla et al., 2007; Gupta
and Srivastava, 2006; Agtas et al., 2007; Yoon et al.,
2008).
Zinc is a common trace metal essential in minute
quantities for mammal and fish (Frieden, 1972 and
Holcombe et. al., 1979), and is generally regarded as one
of the less hazardous element, though its toxicity may be
enhanced by the presence of other heavy metals like
cadmium, copper and ferrous etc. However small
quantities of zinc are required for normal development
and metabolism of organisms, if levels exceed the
physiological requirements, zinc can act as a toxicant.
Exposure to excess zinc has been reported to bring about
biochemical as well as histological changes in various
organs of fishes (Agrawal and Srivastava, 2003;
Srivastava and Verma, 2009). Indeed, much work is
available on the effect of zinc on various aspects of
animal behavior, histopathology, biochemical and
histochemical variation etc. But very little work has
been done with respect to effect of heavy metal on
physicochemical change of water (Bacher and Chilke,
2012) upon exposure to fish in general. In the present
work the attempt was made to fill out the lacunae by
correlating the effect of zinc on alteration of
physicochemical properties of water upon exposure to
Ophiocephalus puctatus.
MATERIALS AND METHODS:
Healthy fingerlings of Ophiocephalus puctatus
measuring the size 12-15cm were purchased from
fisherman of Mulchera (District-Gadchiroli). It was
carried to the laboratory in hygienic condition and
acclimatized for fifteen days. During this period of
acclimatization fish were fed with boiled eggs and rice
bran. Zinc LC-50 for 96 hrs was carried out thrice to
confirm exact dose of LC-50. Then the fish were divided
into six groups. Each group was contained twenty fish
each. Later all these fish were exposed to lethal
concentration of Zinc for 24, 48, 72 and 96 hrs. The
estimation of water was carried out at the interval of 24
hrs after real start time. All the physicochemical
parameters were tested according to APHA (1989).
Values were calculated by one way ANOVA with
software Graph pad-5 demo version.
RESULTS:
It fact the zinc is an essential inorganic element
requires to perform normal physiological function.
Deficiency of this element affects the general
physiology. However the higher concentration causes
the detrimental effect to all the aquatic organisms. In the
present study we observed that the Ophiocephalus
punctatus exhibited 50% mortality at 44.25mg/l of zinc
chloride.
At 50% lethal concentration of zinc chloride fish
exhibited notable changes in its behavior like continuous
fin movement, intermittent twitch and rapid opening and
closing of operculum and mouth. All these activities
were much more frequent in initial time of exposure
compared to the later period but remained higher than the
control throughout the experimental period. It was
observed that the exposed fish secreted large quantity of
mucus from 24 hrs to 96 hrs and till 96 hrs caudal region
became blood red colored (Fig. 1).
Atmospheric temperature was constant (25°C)
during experimental tenure i.e. from 24 to 72 hours of
exposure. However, the water temperature was gradually
increased from 24 to 72 hrs. and at 96 hrs it was
observed to decrease (Table-1, Fig. 2).
Bacher and Chilke, 2012
008 Journal of Research in Animal Sciences (2012) 1: 007-012
The water conductivity was steadily increased
(Table-1, Fig. 3) from 24 to 96 hrs, the maximum
conductivity (0.519 ± 0.006) was observed at 96 hrs. and
lowest at 24 hrs (0.379 ± 0.011). However the pH
(negative logarithmic hydrogen ion concentration) also
increased perpetually from 24 to 96 hours of exposure
(Fig. 4). The maximum pH (6.84 ± 0.013) was noticed
on fourth day (96 hrs) of exposure and minimum (6.35 ±
0.009) at 24 hrs.
Dissolved oxygen (DO) in water was maximum
(Fig. 5) at 24 hrs (0.68 ± 0.87 mg/l) and minimum (0.28
± 0.60 mg/l) was recorded at 98 hrs. The DO was
observed decreasing consistently from 24 to 96 hrs of
exposure. But opposite results were obtained for the free
carbon dioxide. The free carbon dioxide was
continuously increased from 48 to 96 hrs. (Fig. 6), it was
recorded minimum at 24 hrs and maximum at 96 hrs of
exposure.
It was also observed that the total alkalinity as
calcium carbonate increased consistently similar to free
carbon dioxide from 24 to 96 hrs. The total alkalinity
was noted minimum at 24 hrs and maximum at 96 hrs
(Fig. 7).
DISCUSSION:
Zinc has been recognized to play a vital role in
almost all aspects of living systems either directly or
indirectly (Alabaster and Lloyd, 1982 and Shukla et al.,
2003). When zinc occurs at higher levels than normal, it
can act as a pollutant (Agrawal and Srivastava, 2003).
However, no report is available on the extent of changes
in the physicochemical factors of water after exposure of
fish to the LC-50 of Zinc chloride. Therefore the present
study was undertaken to find out the induction of change
in the physicochemical factors of water upon exposure of
Bacher and Chilke, 2012
Journal of Research in Animal Sciences (2012) 1: 007-012 009
Fig 1. Ophiocephalaus punctatus showing an excess
secretion of mucous and redness of caudal fin on
exposure to Zinc Chloride LC-50 up to 96 hrs.
Fig 2. Showing the difference in Ambient and Water
Temperature during the experiment from 24hrs to
96hrs upon exposure of Ophiocephalaus punctatus to
Zinc LC-50.
Fig 3. Showing change in Water Conductivity from
24hrs to 96hrs upon exposure of Ophiocephalaus
punctatus to Zinc LC-50.
Ophiocephalus punctatus to the Zinc chloride.
The murrel O. punctatus is well known to live in
oxygen deficit polluted water in the Indian fresh water
ecosystem due to presence of accessory respiratory
organs. Bacher and Chilke (2012) have reported the
effect of Cadmium LC-50 on the alternation of
physicochemical characteristics of water.
It has been observed that the ambient
temperature influence the temperature of aquatic media
and in general temperature of water is always lower than
the ambient temperature. The Zinc at LC-50 were
observed to decrease initially value of temperature till 72
hrs of exposure and later in 96 hrs that got insignificantly
increased. This decrease in temperature could be due to
decrease in basic metabolic rate of fish. It was observed
that the fish showed continuous movement of mouth,
operculum and fins but fish was quiescent. However in
the last period of experiment from 72 to 96 hrs the entire
activity was seemed to increase as compared to earlier
period along with excessive secretion of mucus. This
could be implicated to slightly increase in basic
metabolic rate of fish till 96 hrs of incubation.
The overall conductivity of water consistently
increased from 24 to 96 hrs of exposure and this increase
in water conductivity could be due to successive increase
in the ionic strength of water. It could be concluded that
the zinc at above tolerance capacity induce the loss of
ions by the fish. The pH of water gradually changed from
the first day of exposure till 96 hrs was reported (Bacher
and Chilke, 2012) upon exposure of fish to cadmium
chloride LC-50. The same was observed in the present
study that zinc also induces the loss of protons by the
Bacher and Chilke, 2012
010 Journal of Research in Animal Sciences (2012) 1: 007-012
Fig 5. Showing alternation in Dissolved Oxygen in
water during the experiment from 24hrs to 96hrs
upon exposure of Ophiocephalaus punctatus to Zinc
LC-50.
Table-1. Effect of Zinc chloride (LC-50) on Physicochemical Parameters of Water
Sr.No. Parameters 24-Hrs 48-Hrs 72-Hrs 96Hrs.
1 Ambient Temp. 25 °C 25°C 25°C 25°C
2 Water Temp. 24°C 24°C 23.2°C 23.3°C
3 Conductivity 0.379 ± 0.011 0.452 ± 0.006 0.483 ± 0.008 0.519 ± 0.006
4 pH 6.35 ± 0.009 6.43 ± 0.011 6.70 ± 0.013 6.84 ± 0.013
5 Dissolved O2 0.68 ± 0.87 0.58 ± 0.60 0.45 ± 0.60 0.28 ± 0.60
6 Free CO2 15.48 ± 0.14 21.51 ± 0.28 23.39 ± 0.11 27.69 ± 0.15
7 Total Alkalinity 23.67 ± 0.42 25.5 ± 0.43 27.33 ± 0.49 32.67 ± 1.05
Fig 4. Showing change in pH (logarithmic hydrogen
ion concentration) during the experiment from 24hrs
to 96hrs upon exposure of Ophiocephalaus punctatus
to Zinc LC-50.
fish at lethal concentration-50.
The gases like the oxygen and the carbon dioxide
exhibited dramatic change from 24 to 96 hrs. It was
observed that quantitatively the level of oxygen
decreased and contrary to this the level of carbon dioxide
increased. This finding indicates the rate of oxygen
consumption increased and hence the carbon dioxide
level in water increased might be due to increase in
metabolic rate of fish. The total alkalinity as calcium
carbonate was also increased from 24 to 96 hrs of
exposure could be due to loss of calcium by the fish
which reacts with the excess of carbonic acid to form the
calcium carbonate.
ACKNOWLEDGEMENT
Authors are very thankful to the Principal, Shree
Shivaji Arts, Commerce and Science College, Rajura
(M.S.) for providing the laboratory facilities.
REFERENCES:
Agrawal M and Srivastava N. 2003. Effects of chronic
zinc exposure on the thyroid gland activity of a fres
water fish, Channa punctatus (Bloch). J. Ecophiol.
Occup. Hlth., 3: 273-278.
Agtas, Semsettin, Huseyin Gey and Suleyman Gul.
2007. Concentrations of heavy metals in water and chub,
Leuciscus cephalus (Linn.) from the river Yildiz, Turkey.
J. Environ. Biol., 28, 845-849.
Alabaster JS and Lloyd R. 1982. In: Water quality
criteria for fresh water fish (Eds: Ababaster JS and Lloyd
R). Butterworth Scientific London. 160-163.
APHA. 1989. Standard methods for examination of
water and waste water. American public health
association, Washington DC.
Bacher SS and Chilke AM. 2012. On exposure to LC-
50 of cadmium chloride, Ophiocephalus punctatus alters
the physicochemical parameters of water. Journal of
Research in Biology 2:119-124.
Frieden E. 1972. The chemical elements of life.
Scientific American. 337: 52-60.
Goodwin TH, Young AR, Holmes MGR, Old GH
and Hewitt N. 2003. The temporal and spatial variability
of sediment transport and yields within the bradford beck
catchment, West Yorkshire. Sci. Total Environ., 314-
Bacher and Chilke, 2012
Journal of Research in Animal Sciences (2012) 1: 007-012 011
Fig 7. Showing change in Total Alkalinity in water
during the experiment from 24hrs to 96hrs upon
exposure of Ophiocephalaus punctatus to Zinc
LC-50.
Fig 6. Showing variation in Free Carbon dioxide in
water fom 24hrs to 96hrs upon exposure of
Ophiocephalaus punctatus to Zinc LC-50.
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Bacher and Chilke, 2012
012 Journal of Research in Animal Sciences (2012) 1: 007-012
316:475-494.
Gupta P and Srivastava N. 2006. Effects of sub lethal
concentrations of zinc on histological changes and
bioaccumulation of zinc by kidney of fish, Channa
punctatus (Bloch). J. Environ. Biol., 27:211-215.
Holcombe GW, Benoit DA and Leonard EN. 1979.
Long-term effects of zinc exposure on brook trout
(Salvelinus fontinalis). Trans. Amer. Fish. Soc., 108:76-
87.
Labonne M, Othman DB and Luck JM. 2001. Lead
isotopes in muscels as tracers of metal sources and water
movements in a Lagoon (Thau Basin, S. France). Chem.
Geol., 181:181-191.
Shukla V, Rathi P and Sastry KV. 2003. Effect of
Cadmium individually and in combination with other
metals on nutritive value of freshwater fish, Channa
punctatus. J. Environ. Biol., 23:105-110.
Shukla V, Dhankhar M, Prakash J and Sastry KV.
2007. Bioaccumulation of Zn, Cu and Cd in Channa
punctatus. J. Enivron. Biol., 28:395-397.
Srivastava N and Verma H. 2009. Alterations in
biochemical profile of liver and ovary of zinc-exposed
fresh water murrel, Channa punctatus. J. Environ. Biol.,
30:(2/3).
Yoon S, Sang-Seop H and Rana SVS. 2008. Molecular
markers of heavy metal toxicity - A new paradigm for
health risk assessment. J. Environ. Biol., 29:1-14

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Effect of zinc chloride (lc 50) on physicochemical parameters of water upon exposure to ophiocephalus punctatus

  • 1. Effect of Zinc Chloride (LC-50) on physicochemical parameters of water upon exposure to Ophiocephalus punctatus Keywords: Zinc, Physico-chemical parameter, Ophiocephalus punctatus. 007-012 | JRAS | 2012 | Vol 1 | No 1 © Ficus Publishers. This Open Access article is governed by the Creative Commons Attribution License (http:// creativecommons.org/licenses/by/2.0), which gives permission for unrestricted use, non- commercial, distribution, and reproduction in all medium, provided the original work is properly cited. Submit Your Manuscript www.ficuspublishers.com http://ficuspublishers.com/ Authors: Swapan S. Bacher and Arun M. Chilke. Institution: Division of Toxicology and Biomonitoring, Department of Zoology, Shree Shivaji Arts, Commerce and Science College, Rajura-442805 (India). Corresponding author: Arun M. Chilke. Email: achilke.2011@rediffmail.com Web Address: http://ficuspublishers.com/ documents/AS0007.pdf Dates: Received: 05 Mar 2012 /Accepted: 15 Mar 2012 /Published: 04 Apr 2012 Article Citation: Swapan S. Bacher and Arun M. Chilke. Effect of Zinc Chloride (LC-50) on physicochemical parameters of water upon exposure to Ophiocephalus punctatus. Journal of Research in Animal Sciences (2012) 1: 007-012 An International Online Open Access Publication group Original Research JournalofResearchinAnimalSciences Journal of Research in Animal Sciences ABSTRACT: Zinc is an essential element and cause deleterious effect at high concentration to both the animals and plants. In the present study, we observed that the Zinc chloride at lethal concentration fifty alters the behavior of fish which also change the physico-chemical properties of water. It was observed that the Zinc chloride steadily increased the pH, conductivity, free carbon dioxide and total alkalinity of water from 24 to 96 hrs, whereas the dissolved oxygen concentration in water was gradually decreased. It is concluded that the increase in pH, conductivity, free carbon dioxide and total alkalinity of water and decrease in oxygen could be due to increase in the metabolic processes of Ophiocephalus punctatus upon exposure to zinc chloride at lethal concentration 44.25 mg/l. Journal of Research in Animal Sciences An International Open Access Online Research Journal
  • 2. INTROCUTION: Heavy metals accumulate in the aquatic organism through various sources like sediments, soil erosion and runoff, air depositions of dust, aerosol, and discharge of waste water (Labonne et al., 2001; Goodwin et al., 2003). But majority of aquatic ecosystems are greatly affected by the industrial waste containing variety of heavy metals. Heavy metals from industries not only disturb the aquatic environment but leads to environmental health hazards (Shukla et al., 2007; Gupta and Srivastava, 2006; Agtas et al., 2007; Yoon et al., 2008). Zinc is a common trace metal essential in minute quantities for mammal and fish (Frieden, 1972 and Holcombe et. al., 1979), and is generally regarded as one of the less hazardous element, though its toxicity may be enhanced by the presence of other heavy metals like cadmium, copper and ferrous etc. However small quantities of zinc are required for normal development and metabolism of organisms, if levels exceed the physiological requirements, zinc can act as a toxicant. Exposure to excess zinc has been reported to bring about biochemical as well as histological changes in various organs of fishes (Agrawal and Srivastava, 2003; Srivastava and Verma, 2009). Indeed, much work is available on the effect of zinc on various aspects of animal behavior, histopathology, biochemical and histochemical variation etc. But very little work has been done with respect to effect of heavy metal on physicochemical change of water (Bacher and Chilke, 2012) upon exposure to fish in general. In the present work the attempt was made to fill out the lacunae by correlating the effect of zinc on alteration of physicochemical properties of water upon exposure to Ophiocephalus puctatus. MATERIALS AND METHODS: Healthy fingerlings of Ophiocephalus puctatus measuring the size 12-15cm were purchased from fisherman of Mulchera (District-Gadchiroli). It was carried to the laboratory in hygienic condition and acclimatized for fifteen days. During this period of acclimatization fish were fed with boiled eggs and rice bran. Zinc LC-50 for 96 hrs was carried out thrice to confirm exact dose of LC-50. Then the fish were divided into six groups. Each group was contained twenty fish each. Later all these fish were exposed to lethal concentration of Zinc for 24, 48, 72 and 96 hrs. The estimation of water was carried out at the interval of 24 hrs after real start time. All the physicochemical parameters were tested according to APHA (1989). Values were calculated by one way ANOVA with software Graph pad-5 demo version. RESULTS: It fact the zinc is an essential inorganic element requires to perform normal physiological function. Deficiency of this element affects the general physiology. However the higher concentration causes the detrimental effect to all the aquatic organisms. In the present study we observed that the Ophiocephalus punctatus exhibited 50% mortality at 44.25mg/l of zinc chloride. At 50% lethal concentration of zinc chloride fish exhibited notable changes in its behavior like continuous fin movement, intermittent twitch and rapid opening and closing of operculum and mouth. All these activities were much more frequent in initial time of exposure compared to the later period but remained higher than the control throughout the experimental period. It was observed that the exposed fish secreted large quantity of mucus from 24 hrs to 96 hrs and till 96 hrs caudal region became blood red colored (Fig. 1). Atmospheric temperature was constant (25°C) during experimental tenure i.e. from 24 to 72 hours of exposure. However, the water temperature was gradually increased from 24 to 72 hrs. and at 96 hrs it was observed to decrease (Table-1, Fig. 2). Bacher and Chilke, 2012 008 Journal of Research in Animal Sciences (2012) 1: 007-012
  • 3. The water conductivity was steadily increased (Table-1, Fig. 3) from 24 to 96 hrs, the maximum conductivity (0.519 ± 0.006) was observed at 96 hrs. and lowest at 24 hrs (0.379 ± 0.011). However the pH (negative logarithmic hydrogen ion concentration) also increased perpetually from 24 to 96 hours of exposure (Fig. 4). The maximum pH (6.84 ± 0.013) was noticed on fourth day (96 hrs) of exposure and minimum (6.35 ± 0.009) at 24 hrs. Dissolved oxygen (DO) in water was maximum (Fig. 5) at 24 hrs (0.68 ± 0.87 mg/l) and minimum (0.28 ± 0.60 mg/l) was recorded at 98 hrs. The DO was observed decreasing consistently from 24 to 96 hrs of exposure. But opposite results were obtained for the free carbon dioxide. The free carbon dioxide was continuously increased from 48 to 96 hrs. (Fig. 6), it was recorded minimum at 24 hrs and maximum at 96 hrs of exposure. It was also observed that the total alkalinity as calcium carbonate increased consistently similar to free carbon dioxide from 24 to 96 hrs. The total alkalinity was noted minimum at 24 hrs and maximum at 96 hrs (Fig. 7). DISCUSSION: Zinc has been recognized to play a vital role in almost all aspects of living systems either directly or indirectly (Alabaster and Lloyd, 1982 and Shukla et al., 2003). When zinc occurs at higher levels than normal, it can act as a pollutant (Agrawal and Srivastava, 2003). However, no report is available on the extent of changes in the physicochemical factors of water after exposure of fish to the LC-50 of Zinc chloride. Therefore the present study was undertaken to find out the induction of change in the physicochemical factors of water upon exposure of Bacher and Chilke, 2012 Journal of Research in Animal Sciences (2012) 1: 007-012 009 Fig 1. Ophiocephalaus punctatus showing an excess secretion of mucous and redness of caudal fin on exposure to Zinc Chloride LC-50 up to 96 hrs. Fig 2. Showing the difference in Ambient and Water Temperature during the experiment from 24hrs to 96hrs upon exposure of Ophiocephalaus punctatus to Zinc LC-50. Fig 3. Showing change in Water Conductivity from 24hrs to 96hrs upon exposure of Ophiocephalaus punctatus to Zinc LC-50.
  • 4. Ophiocephalus punctatus to the Zinc chloride. The murrel O. punctatus is well known to live in oxygen deficit polluted water in the Indian fresh water ecosystem due to presence of accessory respiratory organs. Bacher and Chilke (2012) have reported the effect of Cadmium LC-50 on the alternation of physicochemical characteristics of water. It has been observed that the ambient temperature influence the temperature of aquatic media and in general temperature of water is always lower than the ambient temperature. The Zinc at LC-50 were observed to decrease initially value of temperature till 72 hrs of exposure and later in 96 hrs that got insignificantly increased. This decrease in temperature could be due to decrease in basic metabolic rate of fish. It was observed that the fish showed continuous movement of mouth, operculum and fins but fish was quiescent. However in the last period of experiment from 72 to 96 hrs the entire activity was seemed to increase as compared to earlier period along with excessive secretion of mucus. This could be implicated to slightly increase in basic metabolic rate of fish till 96 hrs of incubation. The overall conductivity of water consistently increased from 24 to 96 hrs of exposure and this increase in water conductivity could be due to successive increase in the ionic strength of water. It could be concluded that the zinc at above tolerance capacity induce the loss of ions by the fish. The pH of water gradually changed from the first day of exposure till 96 hrs was reported (Bacher and Chilke, 2012) upon exposure of fish to cadmium chloride LC-50. The same was observed in the present study that zinc also induces the loss of protons by the Bacher and Chilke, 2012 010 Journal of Research in Animal Sciences (2012) 1: 007-012 Fig 5. Showing alternation in Dissolved Oxygen in water during the experiment from 24hrs to 96hrs upon exposure of Ophiocephalaus punctatus to Zinc LC-50. Table-1. Effect of Zinc chloride (LC-50) on Physicochemical Parameters of Water Sr.No. Parameters 24-Hrs 48-Hrs 72-Hrs 96Hrs. 1 Ambient Temp. 25 °C 25°C 25°C 25°C 2 Water Temp. 24°C 24°C 23.2°C 23.3°C 3 Conductivity 0.379 ± 0.011 0.452 ± 0.006 0.483 ± 0.008 0.519 ± 0.006 4 pH 6.35 ± 0.009 6.43 ± 0.011 6.70 ± 0.013 6.84 ± 0.013 5 Dissolved O2 0.68 ± 0.87 0.58 ± 0.60 0.45 ± 0.60 0.28 ± 0.60 6 Free CO2 15.48 ± 0.14 21.51 ± 0.28 23.39 ± 0.11 27.69 ± 0.15 7 Total Alkalinity 23.67 ± 0.42 25.5 ± 0.43 27.33 ± 0.49 32.67 ± 1.05 Fig 4. Showing change in pH (logarithmic hydrogen ion concentration) during the experiment from 24hrs to 96hrs upon exposure of Ophiocephalaus punctatus to Zinc LC-50.
  • 5. fish at lethal concentration-50. The gases like the oxygen and the carbon dioxide exhibited dramatic change from 24 to 96 hrs. It was observed that quantitatively the level of oxygen decreased and contrary to this the level of carbon dioxide increased. This finding indicates the rate of oxygen consumption increased and hence the carbon dioxide level in water increased might be due to increase in metabolic rate of fish. The total alkalinity as calcium carbonate was also increased from 24 to 96 hrs of exposure could be due to loss of calcium by the fish which reacts with the excess of carbonic acid to form the calcium carbonate. ACKNOWLEDGEMENT Authors are very thankful to the Principal, Shree Shivaji Arts, Commerce and Science College, Rajura (M.S.) for providing the laboratory facilities. REFERENCES: Agrawal M and Srivastava N. 2003. Effects of chronic zinc exposure on the thyroid gland activity of a fres water fish, Channa punctatus (Bloch). J. Ecophiol. Occup. Hlth., 3: 273-278. Agtas, Semsettin, Huseyin Gey and Suleyman Gul. 2007. Concentrations of heavy metals in water and chub, Leuciscus cephalus (Linn.) from the river Yildiz, Turkey. J. Environ. Biol., 28, 845-849. Alabaster JS and Lloyd R. 1982. In: Water quality criteria for fresh water fish (Eds: Ababaster JS and Lloyd R). Butterworth Scientific London. 160-163. APHA. 1989. Standard methods for examination of water and waste water. American public health association, Washington DC. Bacher SS and Chilke AM. 2012. On exposure to LC- 50 of cadmium chloride, Ophiocephalus punctatus alters the physicochemical parameters of water. Journal of Research in Biology 2:119-124. Frieden E. 1972. The chemical elements of life. Scientific American. 337: 52-60. Goodwin TH, Young AR, Holmes MGR, Old GH and Hewitt N. 2003. The temporal and spatial variability of sediment transport and yields within the bradford beck catchment, West Yorkshire. Sci. Total Environ., 314- Bacher and Chilke, 2012 Journal of Research in Animal Sciences (2012) 1: 007-012 011 Fig 7. Showing change in Total Alkalinity in water during the experiment from 24hrs to 96hrs upon exposure of Ophiocephalaus punctatus to Zinc LC-50. Fig 6. Showing variation in Free Carbon dioxide in water fom 24hrs to 96hrs upon exposure of Ophiocephalaus punctatus to Zinc LC-50.
  • 6. Submit your articles online at Ficuspublishers.com Advantages Easy online submission Complete Peer review Affordable Charges Quick processing Extensive indexing Open Access and Quick spreading You retains your copyright submit@ficuspublishers.com www.ficuspublishers.com/submit1.aspx. Bacher and Chilke, 2012 012 Journal of Research in Animal Sciences (2012) 1: 007-012 316:475-494. Gupta P and Srivastava N. 2006. Effects of sub lethal concentrations of zinc on histological changes and bioaccumulation of zinc by kidney of fish, Channa punctatus (Bloch). J. Environ. Biol., 27:211-215. Holcombe GW, Benoit DA and Leonard EN. 1979. Long-term effects of zinc exposure on brook trout (Salvelinus fontinalis). Trans. Amer. Fish. Soc., 108:76- 87. Labonne M, Othman DB and Luck JM. 2001. Lead isotopes in muscels as tracers of metal sources and water movements in a Lagoon (Thau Basin, S. France). Chem. Geol., 181:181-191. Shukla V, Rathi P and Sastry KV. 2003. Effect of Cadmium individually and in combination with other metals on nutritive value of freshwater fish, Channa punctatus. J. Environ. Biol., 23:105-110. Shukla V, Dhankhar M, Prakash J and Sastry KV. 2007. Bioaccumulation of Zn, Cu and Cd in Channa punctatus. J. Enivron. Biol., 28:395-397. Srivastava N and Verma H. 2009. Alterations in biochemical profile of liver and ovary of zinc-exposed fresh water murrel, Channa punctatus. J. Environ. Biol., 30:(2/3). Yoon S, Sang-Seop H and Rana SVS. 2008. Molecular markers of heavy metal toxicity - A new paradigm for health risk assessment. J. Environ. Biol., 29:1-14