CASE STUDIES OF FISH KILLS

3.1 Oxygen depletion: The fish kill in 1996 at Sankey lake (Eutroplus suratensis, Chanda ranga, Puntius sp., Nandus nandus and Amblypharyngodon mola) was due to sudden fall in DO levels in some locations (at sewage inlet) resulting in asphyxiation and not due to any  infection (Benjamin et al., 1996). Fish death was reported in Ulsoor Lake due to chemicals that flushed into the lake after cleaning of swimming pool, introduction of different varieties of fishes and due to phosphorus loading in the lake (Maheshwari, 2005). The insufficient oxygen levels in water affects fish population as oxygen has a low solubility in water (0.5%) than in air (21%) and also diffusion of oxygen is slower in water than air. Fish death is correlated with a stinking odour resembling rotten eggs, characteristics of hydrogen sulphide (H2S). H2S (odour is perceptible in a dilution of 0.002 mg/L) is a colour-less gas produced by respiration of certain bacteria and is highly toxic to most respiratory organisms with the ability to kill animals, plants and microorganisms in micromolar range by coming into contact with the respiratory enzyme, cytochrome coxidase (Maheshwari, 2005). The disastrous mass mortality of Nile tilapia (Oreochromis niloticus) and common carp (Cyprinus carpio) in Lake Hashenge, Tigray occurred in June, 12 to 15th, 2014. The physico-chemical characteristics of Hashenge lake water revealed the presence of abnormal water color, low level of DO (2.39 mg/L), low Secchi disk reading, and slightly alkaline pH. The turnover of the lake due to the mixing of the thermally layered water was the reason for the low DO, which caused mass kills of the fishes. The mass mortality was more severe in Nile tilapia as compared to mortality of common carp (Teame et al., 2016).

3.2 Ammonia toxicity: Ammonia causes negative effects on fish like reduced growth rates, poor feed conversion and reduced disease resistance. Excess ammonia (NH4) levels accumulate in organisms and cause alteration of metabolic activities or increases in body pH harming the aquatic life. At extreme ammonia levels, fish may experience convulsions, coma and death. A short-term exposure to toxic un-ionized ammonia at about 0.6 mg/L (ppm) is capable of killing fish over a few days. But, chronic exposure to toxic un-ionized ammonia as low as 0.06 mg/L (ppm) can cause gill and kidney damage, growth reduction, brain malfunctioning and reduction in the oxygen-carrying capacity of the fish (Durborow et al., 1997; Hargreaves and Tucker, 2004; Waqar K et al., 2013). Ammonia in the range >0.1 mg/L tends to cause gill damage, destroy mucous producing membranes, “sub-lethal” effects like reduced growth, poor feed conversion and reduced disease resistance at concentrations that are lower than lethal concentrations, osmoregulatory imbalance, kidney failure. Fish suffering from ammonia poisoning generally appear sluggish or often at the surface gasping for air (Bhatnagar and Devi, 2013). The maximum admissible ammonia concentration is 0.05 mg/L, where as the ammonia level in the Taj boudi (of Bijapur) water was 2.71 mg/L, which is lethal to fish (Patil et al., 2015).  

3.3 Detergents: Detergents are commonly used for cleaning purposes in households. The extensive use of the detergents pollutes the aquatic ecosystem as they are made up of surface-active agents, builders and fillers. In addition, they contain additives such as anti re-deposition agents, optical fibre brighteners (whitening agents), bluing agents, bleaching agents, foam regulators, organic sequestering agents, enzymes, perfumes and substances that regulate density and assure the crispness of the material they are used on. Phosphates act as a builder in laundry detergents and automatic dishwasher detergents. They make the water soft and slightly alkaline and dissolve dirt and keep it in suspension during washing and thus, increase the performance of the detergent. The presence of detergent in water accelerates the corrosive action, impedes the filtering, sedimentation and coagulation processes, increases the saturation of water with oxygen and also deteriorates the taste properties of water (Vasanthi et al., 2013; Ramachandra et al., 2015).

The ‘after wash’ of detergents is either drained into the aquatic environment such as ponds, lakes, rivers, streams etc. or they find their way into the aquatic environment through sewage line connected to lakes.  Fish has been used as model organism to detect the level of toxicity of different chemicals drained/contaminated in aquatic environment. Linear Alkyl Benzene Sulphonate (LABS) detergent was found to have acute toxic and severe histopathological effects on the gill of Puntius ticto fish. When fishes were exposed to LABS (Henko) in graded concentrations (20 - 28 mg/L, except 22 mg/L) for 24, 48, 72 and 96 hr duration, it was found that all the 30 fishes (100%) died in Henko concentration of 28 mg/L at 24 hr, indicating that the acute toxicity of LABS is dose dependent. The LC50 of Henko was found to be 25.5 mg/L. The histopathological examination of fishes exposed to 2 mg/L Henko for one month revealed severe changes in the epithelial lining of gill arch, gill rakers and gill filaments, suggesting that LABS may induce abnormal cellular structure in gills. As the dose/concentration of LABS increases, the mortality percentage of Puntius ticto fingerlings also increases. Thus, the drainage of ‘after wash’ of this detergent besides other chemicals into the aquatic environment should be strictly prohibited (Varsha et al., 2011). A significant decrease in protein, carbohydrate and cholesterol content in the tissues of fish species Cirrhinus mrigala was observed when the fishes were exposed to sub-lethal concentration of detergent Tide i.e., 3.6 mg/L for 24, 48 and 72 hrs respectively. The kidney showed the highest percent decrease in carbohydrate (77.27%), in protein (76.42%) and in cholesterol (80.03%) content (Vasanthi et al., 2013). The fishes belonging to species Cirrhinus mrigala of mean body weight (1.25g±0.12) were exposed to three concentrations of detergent, Surf excel easy wash i.e, 0.5 mg/L, 1 mg/L, 3 mg/L respectively. Eventhough the test fish exhibited no signs of deformity; the fishes showed marked increase in protease activity with increasing concentration of Surf excel easy wash than the control group (Rani and Kaushik, 2014). The oxygen consumption in the freshwater fish, Mystus montanus increased with 1/3rd sublethal concentration of detergents like Surf and Nirma powderwith increase in time (Chandanshive, 2014).

3.4 Fish Diseases/Infections: Disease is a prime agent affecting fish mortality. Fishes are exposed to different environmental pollutants, including drugs and chemicals. They carry pathogens and parasites and get infected by different pathogens, microorganisms or parasites. Some commonly found fish diseases, listed in Table 1 are gill disease, water quality induced diseases, constipation, anorexia, columnaris, ick, dropsy, tail and fin-rot, fungal infections, white spot disease, pop-eye, cloudy eye, swim bladder disease, lice and nematode worms infection, tuberculosis, lymphocytosis etc. (Sharma et al., 2012). Most fish pathogenic bacteria can reside in the environment or on/in normal fish. Thus, infections induced by some stress (e.g. overcrowding, low DO, high ammonia) upsets the natural defense of organisms (Khatun et al., 2011).

    Table 2 lists fish mortality cases reported from various aquatic ecosystems in India. More than80% fishes were infected by fungi, Saprolegnia parasitica (which had cotton like appearance) in Naini Tal Lake, Uttaranchal, India. The infected parts of the body mainly included pectoral, pelvic and caudal fins, gills and skin. The symptoms include bleeding from the infected parts of the body; the fishes had ragged and tattered body appearance, peeling of skin, bulging eyes, and were sluggish (Nagdali and Gupta, 2002).

    Similar large scale mass mortality of Tilapia mossambicus due to fungal infection was reported in culture pond of University campus, Bhopal. The fungal infection was observed on body of fishes in form of cottony mycelium. Anterior region of body was the most affected area and fishes suffered from severe infection followed by death. Isolation and culture of fungi revealed the presence of six different species of zoosporic fungi viz. Achlya americana, Achlya proliferoids, Aphanomyces laevis, Pythiopsis sp., Saprolegnia diclina and Saprolegnia parasitica. Most of the fungi appeared as mixed infections. Among these, S. parasitica was found as the most virulent and pathogenic fungi (Chauhan, 2014).

    A total of 17 isolates of fungi were isolated from diseased fishes (of six different species viz. Channa stratius, Channa punctatus, Clarius batrachus, Labeo rohita, Heteropneuste fossilis and Mystus cavasius) which belong to 5 species namely Saprolegnia diclina, Saprolegnia ferax, Saprolegnia hypogyana, Saprolegnia parasitica and Achlya americana (Mastan, 2015).