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• Nimesh.N.,Virdi.G.S.,Jain.S. Evaluation of oxygen tolerance in Fresh water Fishes. A journal of sciences-Life Sciences, Voyager: Vol.III, Dec.2012, ISSN: 0976-7436.
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Voyager: Vol. III, 2012 ISSN: 0976-7436, (e): 2455-054X
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EVALUATION OF OXYGEN TOLERENCE IN FRESH WATER
FISHES Ms. Neetu Nimesh *
Dr. G. S. Virdi, **
Dr. Seema Jain ***.
ABSTRACT
Dissolved oxygen (DO) is one of important environmental variable. It has changed so
drastically, in such a short period of time that causes loss of fisheries, loss of biodiversity and
alteration of food webs. Dissolved oxygen is required to meet the respiration needs of fish fauna.
Once the supply of oxygen is cut off in water and the oxygen consumption rate exceeds resupply,
the fish fauna suffocate and results into moribundity.
In the present study four different fresh water fishes such as Gambusia affinis (Baird and Girrard),
Clarias magur (Linnaeus), Xiphophorus clemenciae (Alvarez) and Labeo rohita (Hamilton) were
selected for finding lethal oxygen concentration .We found oxygen consumption rate of all fishes.
This study shows that smaller size fish has moderately high rate of dissolved oxygen consumption
than the larger ones.
KEYWORDS: Dissolved oxygen (DO), Oxygen consumption rate, Moribundity
INTRODUCTION
The economics of most modern aquaculture operations require that animals be cultured at
high densities. Various factors affecting this intensive culture include proper concentration of
dissolved oxygen level, the availability of food, and the optimum range of various physical and
chemical factors. The vital physical factors are temperature, light etc. whereas important chemical
factors include the sustainable range of pH, carbon dioxide, ammonia, salinity, etc.
Dissolved oxygen concentration (DO) is considered the most important water quality
variable in fish culture, in the broadest sense. However, dissolved oxygen concentration is no more
important than other environmental variables because any factor that is outside the range tolerated
by fish can cause stress or death.
The availability of oxygen is the most striking feature, which remains as top priority
requirement for aquatic life. The dissolved oxygen content in aquatic environment also varies
much than in the air because availability of oxygen is limited. To begin with, small differences in
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the metabolism of aquatic life can dramatically change dissolved oxygen concentration. If
dissolved oxygen concentration is consistently low, the growth of aquatic animals will be affected
and will be more susceptible to infectious diseases. If still concentration falls to further low level,
the fish may die. This level of dissolved oxygen is considered as lethal oxygen concentration and
the dissolved oxygen concentration above this which is enough for just survival but not for growth
and health is called sublethal concentration.
What makes dissolved oxygen concentration so important in intensive fish culture is the
speed with which it can change, over a matter of hours, or sometimes even minutes, from optimum
to lethal level. No other environmental variable in fish culture is so dynamic.
The dynamic nature of dissolved oxygen concentration results from the interaction of three
factors. First, oxygen is not very soluble in water so water has only a limited capacity to hold
oxygen. Second, the rate of oxygen used by aquatic biota (fish, plankton and other organism)
living in the pond and its bottom mud can be high. Third, oxygen diffuses very slowly from the
atmosphere into undisturbed water. The combination of these three factors, i.e. limited solubility,
rapid use and slow replenishment can cause drastic change in dissolved oxygen concentration (P.
Mickel: Ecological methods for field and laboratory investigations).
As the pressure on aquaculture industry increases, the fresh water fishes play an important
role. The production of fish has become increasingly intensive during the last few decades with
reduced flow of water as one of the key feature (Rosten et al. 2004). This is made possible with the
extensive use of hyper oxygenation in the inlet water, increasing the oxygen saturation typically up
to 160% (Wedemeyer, 1996; Lygren et al., 2000).
Metabolism and growth of fishes are dependent on the availability of oxygen (Doudoroff
and Shumway, 1970; Fry 1971; Davis, 1975; Brett, 1979; Kutty, 1981). Thus all factors affecting
changes in dissolved oxygen concentration, including the lowering of oxygen and resultant
hypoxia and diet flux of oxygen can affect production of fish in pond. There is considerable
information on how ambient oxygen limits growth in fishes. For example, Hermann (1975) found
that growth of the salmonid, Onchorhyncus kisutch is proportional to dissolved oxygen between 4
and 8 mg/l at 20ºC.
The problem of hypoxia occurred in fish is the reduction of respiratory frequency, which
causes accumulation of acidosis (Bernier and Randell, 1998).
Several researchers have reported that dissolved oxygen levels can also affect the toxicity
of ammonia to aquatic organisms. Thurston et al. (1981) showed an increase in ammonia toxicity
to rainbow trout (Onchorhyncus mykiss) at reduced levels of dissolved oxygen.
There are numbers of ways to measure dissolved oxygen concentrations. These are
selected on the basis of 1) the number of tanks/ experimental bottles to be measured, 2) the
level of accuracy required 3) the cost of the measurement technique. The titration based “drop -
count” method fairly rapidly assesses, whether or not there is sufficient dissolved oxygen in
water. The drop-count method is in expensive and appropriate.
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The purpose of this study intend to check the oxygen tolerance level for some fresh water fishes
named as Gambusia affinis (Baird & Girard), Clarias magur (Linnaeus), Xiphophorus clemenciae
(Alvarez) and Labeo rohita (Ham.).
MATERIALS AND METHOD
I. Selection of Fish
Four different fresh water fishes were selected for the experiment. These are Gambusia affinis
(Baird & Girard), Clarias magur (Linnaeus), Xiphophorus clemenciae (Alvarez) and Labeo rohita
(Ham.).
1. Gambusia affinis (Baird & Girard) It is a mosquito fish. It is an actinoptergian fish, native
to North and Central America, distributed in Mississippi river basin from central Indiana
and Illinois in USA to south of Gulf of Mexico. Most abundant in lower reaches of streams.
Its maximum size is 40 cm. Total length (male/ Unsexed); 7 cm. (female) and reported age
3 year. In India it is exotic fish but very well established all over.
2. Clarias magur (Linnaeus) It is an actinoptergian cat fish, distributed in India, Pakistan,
Nepal, Sri Lanka, Bangladesh, Thailand, Myanmar, Philippines, and Indonesia. USA,
Singapore. Its approximate size is about 60 cm. experiment was done on fish fingerlings of
size 10 cm approximately.
3. Xiphophorus clemenciae (Alvarez) It is an aquarium fish, it belong to class
Actinopterygii, its size is about 4 cm. it is a native to Central America, Mexico.
4. Labeo rohita (Ham.) This also belongs to class Actinopterygii. Its common name is rohu.
It is a carp fish, attaining a maximum size of about 200 cm. weight about 45.0 kg; it is
distributed throughout the Asia.
All the above selected fishes have specific importance. They have different oxygen tolerance. The
fish were collected from different sources. 50 fish of each sample were collected and transferred to
glass aquaria or in buckets. The fish were maintained in aerated, dechloroinated municipal tap
water. They were fed on artificial diet once a day, around noon, with 3% to 4% of total fish
biomass given in a form of dry pellets which were floating type.
II. Acclimatization
This part is important for fish for and it’s stocking in new environmental condition. In the
laboratory, the fish were acclimatized in the experimental tanks for a week prior to the conducting
of an experiment. The acclimatization period varies for different species of fish. During
acclimatization oxygen level was maintained above 5 ppm and water temperature was maintained
at 24ºC to 30ºC.
III. Starvation
Prior to starting of an experiment the fishes were starved. The fishes were transferred from
aquarium to the plastic containers containing dechlorinated water. The fishes were starved for 24
hours before starting an experiment. This was done to avoid excess contamination of water due to
fecal discharge of fishes. 3-4 fishes were stocked in each plastic container and the water was
changed after 24 hours.
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IV. Setting of an Experiment
The acclimatized and starved fish were transferred to BOD bottle of capacity 150ml,
250ml, 500ml and 1 liter as per the weight of fishes.
The MCD tap water was used for experiment. It was dechlorinated by leaving it open for 24 hr.
before its use in the experiment or storage of fish, acclimatization etc. The pH of the water was
checked by using the digital pH-meter. The temperature of water was also determined with the
help of laboratory thermometer. The dissolved oxygen of the water sample was determined by
using Winkler’s method. The fish was introduced into the BOD bottles already filled with
dechlorinated water up to the brim. A small muslin cloth net was used for transferring the fish
from the acclimatization tank to the BOD bottle. A large funnel was put on the mouth of BOD
bottle, so that fish was handled least with hands. Thereafter the BOD bottle was stopper using
airtight stopper taking care that no air bubble gets trapped below the stopper. The time of starting
the experiment was recorded. The number of fishes in each BOD bottle depended upon the weight
and length of the fish. Each fish was mandatory provided with 1 liter of water/ 5 gms of body
weight. During experiment the fish was observed for the following activities
Locomotion
Opercular movement
Movement of fins
Quiescence
Death (moribundity) time.
The fish was observed till it reached the moribundity which was symptomized by the absence of
any movement of operculum and fins and more frequently turning of fish upside down. At this
point the pH, temperature and dissolved oxygen was again calculated in the experimental water.
The fishes were than taken out for recording their length and weight.
OBSERVATIONS AND RESULTS
Gambusia affinis
Experiment (Table 1): In all 9 fishes were tested. The weight of the test fishes ranged between 0.03gm
to 0.171gms. Each fish was provided with around 0.45 liters water/ gm body weight. pH of water at the
start of experiment was 7.5 and temperature ranged between 30ºC±1ºC .The Dissolved oxygen was
5ppm. All the fishes reached moribundity or died between 220 minutes with average death time of
211.6 minutes.
The perusal of Table 1 shows that the initial dissolved oxygen was 5ppm. The dissolved oxygen at
the end of the experiment ranged between 1.7ppm and 2.1ppm. The average lethal oxygen
concentration was 1.86ppm.
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Total dissolved oxygen consumed was 3.16ppm i.e. 3.92mg/gm fish, @1.112mg oxygen/hr./gm
wt. of fish.
Clarias magur
Clarias magur available for the experiment were medium sized and weight ranged between 6.538
gm and 10.896 gm hence large bottles were used (250ml or 350ml or 500ml)
Experiment (Table 1): The first set of experiment was on lines similar to that of other 3 test fish.
The average weight of the fish was 9.23gms and ranged between 6.538 and 10.846gm. Each fish
was provided around 250 ml or more of water. The initial pH of the water was 7, temperature
range was 27ºC to 28ºC and dissolved oxygen 7.0ppm.
A perusal of table 3 shows that the Clarias magur died faster than Gambusia affinis with mean
death time much lower than i.e. only 95 minutes (range 65- 120 minutes). The most striking
fact was that this fish had a very a high Lethal dissolved oxygen value with an average of
4.00ppm; the least lethal concentration for a fish was 3.8ppm. The total oxygen consumed was
3ppm i.e. 2.25 mg i.e. 0.081 mg/gm at the rate of 0.51 mg/gm fish/hr.
Xiphophorus clemenciae
Experiment (Table 1): The experiment with Xiphophorus clemenciae (Yellow sword tail) was
conducted with 9 fishes divided into 3 lots of 3 fishes each. The range of weight was 0.17 gm to
0.420gms, with an average of 0.327gms. The length of fishes ranged between 2.6 and 3.5cms. The
temperature remained at 25-27ºC and pH was 7. The fishes reached the moribundity in 172-
215minutes, with an average of 181.66 minutes (2 hours 2 minutes)
The dissolved oxygen at the beginning of the experiment was 6ppm but at the time of moribundity
it ranged between 3.6-4.2ppm with an average of 3.86ppm.
A perusal of table 3 shows that the rate of oxygen consumption in case of Xiphophorus clemenciae
was 0.0993mg of oxygen/gm body weight/hour (Table 2).
Labeo rohita
The experiment (Table 1) with Labeo rohita fingerlings was performed with sample of 9 fishes
divided into 3 lots of 3 fishes each. Each set of 3 fishes was kept in a glass bottle of 250 ml
capacity. The initial temperature of the water was 29ºC and the pH was 7. The average weight of
Labeo rohita fingerlings was 1.56gms with a range 0.539 to 2.539. The maximum and minimum
length of test fish was 6.5cm and 3.7 cm respectively. The initial dissolved oxygen was 9ppm and
total dissolved oxygen consumed was 4.05ppm.
The moribundity was achieved in 70-90 minutes with an average of 80 minutes (1 hour and 20
min.) the dissolved oxygen being zero in all samples. The rate of oxygen consumption in case of
Labeo rohita was 5.06mg/gm of body weight/hour (Table 3).
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The experiments were carried out 30 times and the average readings have been presented in the
paper.
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Table 1
Length, Weight, Mortality Time for the Four Test Fishes
S.No
Name of fish
Length of fish in cm
Weight of fish in gm
Mortality time limits in minutes
Average
Range
Average
Range
Average
1
Gambusia affinis
2.23
0.03-0.171
0.117
190-215
211.6
2
Clarias magur
11.1
6.538-10.846
9.233
65-120
95
3
Xiphophorus clmenciae
2.93
0.170-0.420
0.327
170-215
196.6
4
Labeo rohita
5.31
0.530-2.539
1.56
70-90
80
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Table 2
pH, Temperture and Rate of O2 Consumption in Four Test Fishes
S.No
Name of Fish
Initial
pH
Final
pH
Initial
Time
Final
Time
Initial
DO
Final
DO
1
Gambusia affinis
7.5
6
30
29
5
1.86
2
Clarias magur
7
6
28
27
7
4
3
Xiphophorus clmenciae
7
3.5
27
25
6
3.8
4
Labeo rohita
7
6
26
25
9
0
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Table 3
Rate of O2 Consumption of the Four Test Fish
S.N
o.
Name of fish
Total
dissolv
ed
oxygen
consum
ed in
ppm
Average
weight of
O2 consumed
in mg
Average rate of
O2
consumed
mg/gm fish
Average of O2
consumed mg/gm
fish/ hr
1
Gambusia affinis
3.16
0.153
3.92
1.112
2
Clarias magur
2.25
0.249
0.081
0.051
3
Xiphophorus
clmenciae
1.73
0.106
0.0163
0.0993
4
Labeo rohita
4.05
0.749
6.75
5.06
DISCUSSION
Large number of fishes have been subjected to experimentation for finding out the effect of
lethal and sub-lethal concentration of dissolved oxygen. (Salmo, Trout and Char-Albaster and
Lloyd, 1980; Trout and small mouth bass Burdick et al., 1954; channel cat fish Andrew’s et
al., 1978; Seven fresh water fish species of India Singh, G. and Virdi, G.S., 1983). In the
present study the four fishes selected for finding out of the lethal oxygen concentration belonged
to four different categories.
Gambusia affinis is a small fresh water pond and lake dweller feeding on various aquatic larvae
and is highly valued for its ability to kill mosquito larvae. It is a warm water fish and known to
be a hardy one. The current experimental data clearly indicate that this small fish has a
moderately high rate of dissolved oxygen consumption (1.112 and 0.193 mg/gm fish/hr).
The Clarias magur is another pond dwelling fish of warm waters rich in organic matter and can
survive long periods of low dissolved oxygen concentration. This ability of the fish is primarily
because of the fact that it can breath atmospheric air with the help of accessory air breathing
organs. The fish died on an average 95 minutes when kept in air tight water containing bottles
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and the dissolved oxygen consumed was much less as compared to other fishes like Gambusia
and Labeo (Table 1). The same fish when given only 40% atmospheric air above the water was
able to live for 25 hrs (1500 minutes) and consumed more oxygen to deplete it to 0.8 ppm. The
two experiments with Clarias show that the rate of consumption was very low (0.05 mg/gm
fish/hr) when fish was unable to access the atmospheric air because it is an air breathing fish.
The Xiphophorus clemenciae is a valuable aquarium fish, commonly known as yellow sword tail
primarily it is also a fish of clean warm waters but is an active mid water dweller. It is a small
fish with relatively high rate of oxygen requirement (0.0993 mg/gm fish/hr) in the experiments.
Labeo rohita is one of the most valuable fresh water carp. It is although running water breeder it
is stocked in a lower mid water dweller and very fast rate of growth and very agile habit. Its
oxygen requirement is appropriately very high consuming the total oxygen on lowest time before
its death. The rate of O2 consumption is as high as 5.06 mg/gm/hr. This is highest amongst all
the four test fishes including Clarias.
It can be summarized that the small fishes like Gambusia and Xiphophorus had a larger survival
time, whereas Labeo and Clarias died faster.
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... This was confirmed by the reduced heartbeat rate observed in fishes from treated groups ( and an increase in oxidative stress is related to a decreased heartbeat, as seen in this study (Shang and Wu, 2004). If the quantity of dissolved oxygen in the water is constantly low, the growth of aquatic animals will be hindered, and they will be more vulnerable to infectious diseases (Nimesh et al., 2012). Low oxygen levels cause a wide range of issues, from mass mortality of aquatic species (fish and marine mammals) to local extinction of fauna, as well as ecological disruption and fishery productivity decreases (Diaz, 2001;Pollock et al., 2007;Domenici et al., 2017;Roman et al., 2019). ...
Thesis
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Pollutants and other forms of environmental stress (lifestyle and social behaviour) are of global concern due to significant adverse effects on human health. The term "exposome" has emerged as a concept in environmental health sciences, including environmental epidemiology, exposure science, and toxicology. It is the composite of an individual's lifetime exposures and how those exposures relate to health. A major source of individual exposure to the external environment, either directly or indirectly, is via drinking water since most pollutants in the air and soil end up in water bodies, including rivers. In India, one of the major rivers that receive different wastes is the Cauvery River (CR). The Cauvery River, an interstate river, flows eastward from Karnataka through Tamil Nadu and drains into the Bay of Bengal, providing potable water for over 150 million humans and animals and has long-sustained fishing and irrigation. However, indiscriminate discharge of waste into the river water causes unexplained health hazards to human and other animal species, like skeletal deformity and dwindling numbers of fish species in the river. However, in detail, the health hazard impacts of the Cauvery water have not been investigated so far. To investigate this phenomenon, we analyzed the biological, physical, and chemical parameters as well as microplastics present in the CR water and then evaluated the toxicity effects on the zebrafish (Danio rerio) model. Zebrafish offers many advantages as a research model, including rapid development, optical transparency, a large number of offspring, and an excellent vertebrate model for toxicological research. We treated the zebrafish with KRS-CR water samples collected from three stations (fast-flowing water [X], slow-flowing [Y], and stagnant [Z] water), before and after filtration. Firstly, we detected microscopic organisms (MO) such as Cyclops, Daphnia, Spirogyra, Spirochaeta, and total coliform (Escherichia coli), which are bioindicators of water pollution present in the samples. All physicochemical parameters analyzed, including heavy metals before and after filtration of the water with Millipore filter paper (0.45 μm), were within the acceptable limits set by standard organizations, except for decreased dissolved oxygen (DO), and increased biochemical oxygen demand (BOD), and chemical oxygen demand (COD), which are indicators of hypoxic water conditions. We also identified the presence of microplastics (polybutene (≤ 15 μm), polyisobutene (≤ 20 μm), and polymethylpentene (≤ 3 mm) as well as cyclohexyl functional group in CR water samples. Zebrafish embryos treated with the water samples, both before and after filtration, exert the same cytogenotoxic effects by inducing increased reactive oxygen species (ROS) production, which triggers subcellular organelle dysfunctions, DNA damage, apoptosis, pericardial oedema, skeletal deformities, and increased mortality. As a result, we observed that both water samples and zebrafish larvae had significantly less oxygen availability, due to the presence of plastic materials (polyisobutylene). Plastic pollution has become a serious global concern. The plastic waste is broken down into minute particles known as microplastics (MPs) and released as granules, pellets, and/or powders, influencing biosystems. 'Microplastic' is a term for plastic particles without a universally established definition. In the literature, microplastic is often defined as plastic particles up to 5 mm in dimensions with no defined lower size limit. Among the three types of MPs observed in this study, we discovered that the concentration of polyisobutylene (PIB) (<10 μg/mL) was higher than that of the other MPs particles identified in the CR. Since the mechanism of polyisobutylene's toxicological effects is unknown, we synthesized, characterized, and determined the toxicity effects and accumulation of polyisobutylene (PIB) in zebrafish. Using the solvent evaporation method, we synthesized pristine and fluorescence PIB-MPs with particle sizes of < 2-10 μm. The PIB Raman peak (715.942 cm-1) and FTIR characterization tests showed that the samples have notable peaks at 1366 and 1388 wavenumber (cm-1), and zeta potential of approximately -40mV to -60 mV, indicating the inherent stability of the suspensions. Zebrafish larvae exposed to various concentrations (low and high concentrations) of PIB-MP showed reduced swimming and hyperactivity, delayed hatching, increased ROS, and changes in mRNA levels of genes (mnsod, cu/znsod, gsr, and gstp1) encoding antioxidant proteins. Interestingly, we observed that the PIB-MP accumulated in all three gut regions (proximal intestine, middle intestine, and distal intestine) of both larvae and adult fish within 7 to 21 days, respectively. Histopathological examination of the gut revealed increased vacuolation as well as damage to the intestinal mucosa. The immunohistochemistry results showed an enhanced expression of two proinflammatory cytokines (TNF-α and IL-18) in the gut and tail regions of treated fish, which ultimately led to an increase in apoptosis. The build-up of these PIB particles generates adverse consequences in zebrafish larvae and adults. The most frequent phenotypic manifestation we found was skeletal abnormalities, which ultimately led to higher mortality. Our findings show that KRS-CR water can cause cytogenotoxic and embryotoxic defects in zebrafish due to hypoxic water conditions triggered by the PIB microplastic influx. The present study, with its comprehensive analysis of biological and physicochemical parameters in Cauvery River water, offers valuable insights for the evaluation of environmental health hazards. By identifying the presence of microplastics in the river, the study highlights the potential risks posed by this specific microplastic (PIB-MP) to the environment and human health. The cytogenotoxic and embryotoxic effects observed in the zebrafish highlight the potentially hazardous nature of the water, indicating a need for further investigation and implementation of appropriate mitigation measures. Such information is crucial for policymakers, regulatory bodies, and/or environmental agencies as it provides a scientific basis for developing effective strategies and interventions to mitigate the adverse impacts of microplastics in river water. The findings can help in designing targeted and efficient river water treatment strategies, aiming to reduce microplastic contamination and ensure the provision of safe and clean water resources for communities and ecosystems in other to protect the health of both aquatic organisms, animals, and human populations dependent on the river water for various purposes.
... As a result, cardiac abnormalities in the early life stages of fishes are symptomatic of stressor reactions, and an increase in oxidative stress is related to a decreased heartbeat, as seen in this study (Shang and Wu, 2004). If the quantity of dissolved oxygen in the water is constantly low, the growth of aquatic animals will be hindered, and they will be more vulnerable to infectious diseases (Nimesh et al., 2012). Low oxygen levels cause a wide range of issues, from mass mortality of aquatic species (fish and marine mammals) to local extinction of fauna, as well as ecological disruption and fishery productivity decreases (Diaz, 2001;Pollock et al., 2007;Domenici et al., 2017;Roman et al., 2019). ...
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In the Cauvery River (CR), indiscriminate discharge of waste causes unexplained skeletal deformity in some fish species present in the water. To investigate this phenomenon, we analyzed the biological, physical, and chemical parameters present in the water and then evaluated the toxicity effects on the zebrafish (Danio rerio) model. The zebrafish were treated with KRS-CR water samples collected from three stations (fast-flowing water [X], slow-flowing [Y], and stagnant [Z] water), before and after filtration. Firstly, we detected microscopic organisms (MO) such as Cyclops, Daphnia, Spirogyra, Spirochaeta, and total coliform (Escherichia coli), which are bioindicators of water pollution present in the samples. All physicochemical parameters analyzed, including heavy metals before and after filtration of the water with Millipore filter paper (0.45 µm), were within the acceptable limits set by standard organizations, except for decreased dissolved oxygen (DO), and increased biochemical oxygen demand (BOD), and chemical oxygen demand (COD), which are indicators of hypoxic water conditions, as well as the presence of microplastics (polybutene (< 15 µm), polyisobutene (≤ 20 µm), and polymethylpentene (≤3 mm)) and cyclohexyl in CR water samples. Zebrafish embryos treated with the water samples, both before and after filtration exerts the same cytogenotoxic effects by inducing increased reactive oxygen species (ROS) production, which triggers subcellular organelle dysfunctions, DNA damage, apoptosis, pericardial edema, skeletal deformities, and increased mortality. As a result, we observed that both water samples and zebrafish larvae had significantly less oxygen using SEM and EDS. Our findings show that KRS-CR water can induce cytogenotoxic and embryotoxic defects in zebrafish due to hypoxic water conditions triggered by the microplastics influx. The present study would provide valuable insights for health hazards evaluation and future river water treatment strategies.
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The daytime increase in dissolved oxygen (DO) concentration of pond waters may be estimated from solar radiation, chlorophyll a concentration, and percentage O2 saturation at dawn (coefficient of multiple determination, R = 0.83), or from solar radiation, Secchi disk visibility, and percentage O2 saturation at dawn (R = 0.80). A computer simulation model for predicting the effects of cloudy weather (low solar radiation) on DO depletion was developed for channel catfish ponds. The model incorporates the equation for estimating daytime DO increase from solar radiation and Secchi disk visibility with components for estimating the nighttime decline in DO from respiration by the plankton, fish, and benthic communities, and the gains or losses from diffusion. Results from the study demonstrated that the combination of dense plankton blooms and low levels of light intensity were closely related to low concentrations of DO.
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The effect of dissolved oxygen concentration on the toxicity of ammonia to juvenile (0.4–3.2 g) gilthead seabream (Sparus aurata) was studied. The mean 96-h LC50 value of ammonia was 23.7 mg/l total ammonia-N (19.3–28.7, 95% C.L.; equivalent to 1.27 mg/l NH3-N). By comparison, S. aurata is somewhat less sensitive to ammonia than salmonids and similar in sensitivity to nonsalmonids. Increased toxicity of ammonia was observed with decreasing oxygen level. Our data suggest that below a threshold of approximately 40% D.O. saturation, the response of S. aurata to ammonia is no longer linear. Under reduced oxygen level most of the mortality occurs within a few hours, apparently as a consequence of an additive toxic effect. No evidence of pathological changes was found in the gills, liver and kidneys of fish with lost equilibrium in the presence of added ammonia.Acutely toxic conditions for S. aurata may prevail in medium-flow systems (2–6 kg fish/m2 and 50% total daily water exchange) where oxygen and ammonia levels are influenced by microbial and algal activities. In such systems, ammonia toxicity may increase as a result of increasing ammonia levels and decreasing oxygen concentration following crashes of phytoplankton populations. In high-flow systems typical of most hatchery and nursery tanks as well as some grow-out ponds, it is likely that the chronic effects of ammonia toxicity will be more important than the acute ones. The data suggest that increasing oxygen level by aeration is sufficient to reduce acute ammonia toxicity under certain situations.
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Channel catfish (Ictalurus punctatus) were stocked in 0.02 to 0.04-hectare ponds without aeration at three rates (4,942, 10,007, and 20,385 fish per hectare) and fed daily. Fish averaged 12 cm total length and 10 g at stocking. Each treatment was replicated six times. Maximum feeding rates of 34, 56, and 78 kg/hectare, respectively, were reached by midsummer. In the low treatment, no dissolved oxygen (DO) problems occurred, and survival was 99%. In the medium treatment, DO at dawn frequently fell below 2.0 mg/liter and some fish suffocated during an oxygen depletion in one pond; however, survival averaged 93%. In the high treatment, DO at dawn was usually below 2.0 mg/liter in August and September. Fish mortalities resulted from DO depletion in three ponds of the high treatment, but survival averaged 83%. Nitrite-nitrogen and un-ionized ammonia never reached concentrations recognized to be lethal to channel catfish in any of the treatments. However, concentrations of un-ionized ammonia were possibly high enough to have adversely affected growth. Even though the average weight of individual fish decreased, harvest weight of fish increased from low to high treatment. The low treatment produced an average of 2,990 kg/hectare of fish and a net economic gain of /1,136. The medium treatment produced an average 4,100 kg/hectare for a net gain of /1,303. The high treatment produced an average of 4,860 kg per hectare, but a net gain of only $671.
Book
Preface. Acknowledgements. List of Scientific Names. Chapter 1: Introduction: Historical perspective The aquatic environment The intensive culture environment. Chapter 2: Basic physiological functions: Introduction Respiration and oxygen consumption Blood and circulation Osmoregulation Parr-smolt transformation Feeding, digestion, excretion Immune protection Stress response. Chapter 3: Effects of water quality conditions: Introduction Water quality requirements: acidity alkalinity ammonia carbon dioxide chlorine dissolved oxygen hardness heavy metals hydrogen sulfide nitrate, nitrite supersaturation temperature Total dissolved solids, salinity Total suspended solids, turbidity summary Disease problems associated with water quality conditions: Gas bubble disease (Gas bubble trauma) Methemoglobinemia (Brown blood disease) Visceral granuloma and nephrocalcinosis Blue sac disease (Hydrocele embronalis) White spot (Coagualted yolk) disease Soft shell disease (Soft egg disease) Algal toxins. Chapter 4: Effects of fish cultural procedures: Introduction Crowding Transportation Formulated diets/adventitious toxins Effects of smolt development Chapter 5: Biological interactions during rearing: Introduction Interactions between fish Interactions between fish and microorganisms: fish-pathogens-environment relationship Infection into disease:mechanisms Stress-mediated diseases Diseases as indicators of environmental quality Managing biological interactions to prevent diseases. Chapter 6: Methods to minimize pathogen exsposure: Introduction Biological methods water treatment systems: Chloration Ultraviolet light ozone. Introduction: Basic physiological functions Effects of water quality conditions Effects of fish cultural procedures Biological interactions during rearing Methods to minimize pathogen exposure.
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Dominance hierarchies of the three‐spined stickleback Gasterosteus aculeatus from river and pond populations were subjected to hypoxia (20%, range ± 1%). Under hypoxia, the hierarchies were less stable in terms of rank position and tissue L‐lactate was higher in river fish than pond fish under normoxia and hypoxia. Dominant fish gained mass under normoxia but lost mass under hypoxic conditions possibly due to them maintaining high levels of aggression.
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The 96-h median lethal concentrations of nitrite to channel catfish (Ictalurus punctatus), tilapia (Tilapia aurea), and largemouth bass (Micropterus salmoides) under similar water quality conditions were 7.1 ± 1.9, 16.2 ± 2.3, and 140.2 ± 8.1 mg NO2-N/L (mean ± SE), respectively (pH 7.7–8.2; temperature 23 °C). During 24-h sublethal exposures to nitrite, methemoglobin concentrations in the blood of all three species generally increased with increasing nitrite concentrations. Channel catfish and tilapia concentrated nitrite in their blood above environmental levels and generated higher methemoglobin concentrations than largemouth bass at all nitrite concentrations tested. Largemouth bass did not develop elevated methemoglobin concentrations until NO2-N concentrations reached 48.7 mg/L, and plasma nitrite concentrations in largemouth bass were never observed higher than environmental concentrations. These data indicate that differences in resistance to nitrite among species may be partially due to a differential ability of some species to prevent the concentration of nitrite in the plasma.
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In higher vertebrates, two opposite behavioral coping strategies can be distinguished that are associated by a typical neuroendocrine pattern. Little is known about the individual variation in the stress response in lower vertebrates such as teleosts. In the present study, rainbow trout were fitted with an indwelling aortic catheter for repeated blood sampling and exposed to severe hypoxia and subsequent recovery and their behavior was characterized semiquantitatively during hypoxia. Blood levels of catecholamines, cortisol, glucose, FFA, lactate, and electrolytes were measured. About 60% of the fish survived the experiment whereas the others died during the recovery period. Behavioral strategy appeared to be highly related to survival since nonsurviving fish displayed strenuous avoidance behavior involving burst type activity whereas surviving fish did not panic and remained quiet. These behavioral differences were associated with marked differences in plasma catecholamine levels, which were 4- to 5-fold higher in nonsurviving fish as compared to survivors whereas the cortisol response tends to be lower in nonsurviving fish. Plasma lactate levels in nonsurvivors were 4- to 5-fold higher as compared to survivors while a severe hyperkalemia developed during recovery indicating the loss of intracellular homeostasis. The individual differences in behavioral concepts and neuroendocrine activation observed in rainbow trout during stress show great similarity with the active and passive coping strategies distinguished in higher vertebrates and may be determinant for survival during hypoxia.