A Review on Effects of Heavy Metals on Aquatic Animals and Public Health Significance
A Review on Effects of Heavy Metals on Aquatic Animals and Public Health Significance
Maria Al Mazed1*, Md. Ashikur Rahman1 and Sk. Istiaque Ahmed2
1Freshwater Station, Bangladesh Fisheries Research Institute, Mymensingh, Bangladesh; 2Department of Fisheries Resource Management, Chattogram Veterinary and Animal Sciences University, Bangladesh.
Abstract | Heavy metals such as As, Pb, Hg, Cd, Cr, Fe, Mn, Ni and Zn are usually toxic for the aquatic ecosystem. Exposure of heavy metals in the aquatic organisms is linked to the retardation of growth, lesions in liver and damages in kidney. They are also causing infertility in animals. Chronic exposure and excessive concentrations are also deleterious for the normal physiological functions of human. Consumption of fishes contaminated with toxic metals are neurotoxic and carcinogenic to blood, lungs, kidneys, bones, liver and other vital organs of human. The present review outlines the contamination of aquatic environment with heavy metals and their contagious effects on aquatic animals and their public health concerns.
Editor | Muhammad Abubakar, National Veterinary Laboratories, Park Road, Islamabad, Pakistan.
Received | June 09, 2022; Accepted | September 28, 2022; Published | November 17, 2022
*Correspondence | Maria Al-Mazed, Freshwater Station, Bangladesh Fisheries Research Institute, Mymensingh, Bangladesh; Email: [email protected]
Citation | Al Mazed, M., M.A. Rahman and S.I. Ahmed. 2022. A review on effects of heavy metals on aquatic animals and public health significance. Veterinary Sciences: Research and Reviews, 8(2): 96-104.
DOI | https://dx.doi.org/10.17582/journal.vsrr/2022/8.2.96.104
Keywords | Heavy metals, Aquatic animals, Human health, Exposure, Toxicity
Copyright: 2022 by the authors. Licensee ResearchersLinks Ltd, England, UK.
This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Introduction
Fish is considered as one of the most important protein sources for human (Balami et al., 2019; Karayakar et al., 2022). Fish may also concentrate large amounts of some metals from the water (Mansour and Sidky, 2002) and transfer throughout the web chain into human. Of late, aquatic environment is repetitively polluted through heavy metals (HMs) from a variety of sources and right now it has anticipated a dangerous scenario for aquatic life and fish species. HMs is usually available in natural waters and some are essential to living organisms even though they may become highly toxic when existing in high concentrations. U.S. Environmental Protection Agency listed metals of major interest in bioavailability studies, are Al, As, Be, Cd, Cr, Cu, Hg, Ni, Pb, Se and Sb (Abdel-Mohsien and Mahmoud, 2015). A number of health risks can expose because of excessive intake of these metals. For instance, fish consuming heavy metals can seriously lessen some essential nutrients in the body causing a decrease in immunological defenses, intrauterine growth retardation, impaired psycho social behaviors, disabilities associated with malnutrition and a high prevalence of upper gastrointestinal cancer (Arora et al., 2008). There is limited comprehensive information about effects of heavy metals on aquatic animals and public health significance in humans. In this review, we attempted to provide an updated and comprehensive knowledge on the heavy metals effects and human health hazards.
Sources of heavy metals
HMs is introduced into the aquatic environment by means of natural and anthropogenic sources. They are naturally found in the earth’s crust, soil, air, water and all biological substances at various concentrations, from where they are being distributed widely through the anthropogenic activities such as rapid industrialization, overgrowing urbanization, globalization, intensive agricultural practices and environment manipulation (Gupta et al., 2009; Vaseem and Banerjee, 2016). Industrial sources of HMs pollution are refinery, smelter, lead-based paints, lead-soldered food cans, lead plumbing pipes, auto mobile exhaust (tetraethyl lead) refinery, plastic, paints, antiseptic, scientific instruments, photography, fuel combustion, tannery, smelter, mining, electroplating, pigments (Cadmium yellow), plastics, pesticides, land application of fertilizers, animal manures, sewage sludge, pesticides, waste water irrigation, spillage of petrochemicals and Uranium mining etc. (Verma et al., 2018). However, the most common source of HMs pollution in the aquatic environments is come from the mining companies. Residues of toxic metals may persist in the environment and can accumulates in higher concentrations ranging from hundreds to thousands times than their concentration of water and sediments (Goodwin et al., 2003; Osman et al., 2007). Toxic heavy metals are generally accumulates in fish body directly from the environment through the contact with water and diets of fish.
Toxic heavy metals
Toxic heavy metals are individual metals and metalloids that have negative effect on human health. Heavy metals are noteworthy environmental pollutants and their toxicity is a problem of increasing significance for ecological, evolutionary, nutritional and environmental reasons (Shah, 2017). Toxic effects of heavy metals include reduction in fitness, interference in reproduction leading to carcinoma and finally death. The toxic effects usually associated with chronic exposure by pollutant heavy metals are mutagenicity, carcinogenicity, teratogenicity, immunosuppression, poor body condition and impaired reproduction (Pandey and Madhuri, 2014). Toxicity of HMs can lower the energy levels and can damage the functioning of brain, lungs, kidney, liver and blood composition and other important organs (Shah, 2017). Long term exposure to the higher concentrations of HMs leads to the gradual and progressive physical, muscular and neurological degenerative processes that initiate disease like multiple sclerosis (Shah, 2017).
Commonly encountered toxic heavy metals
- Arsenic (As)
- Lead (Pb)
- Mercury (Hg)
- Cadmium (Cd)
- Chromium (Cr)
- Iron (Fe)
- Manganese (Mn)
- Nickel (Ni)
- Zinc (Zn)
Arsenic
Arsenic (As) is an ubiquitous element, released into the aquatic environment through anthropogenic activities such as metal smelting, chemical manufacturing, and agricultural runoff (Schlenk et al., 1997; Singh and Banerjee, 2008). As and its compounds are very poisonous at higher concentrations. It is an important and ubiquitous environmental contaminant, that can exerts carcinogenic risks to the public health worldwide (Rossman, 2003). As exposure in the aquatic environment causes bioaccumulation in aquatic organisms and can lead to physiological and biochemical disorders, such as poisoning, liver lesions, decreased fertility, cell and tissue damage, and cell death (Bears et al., 2006; Ribeiro et al., 2005).
Lead (Pb)
Lead (Pb) is a dangerous environmental contaminant and due to its higher toxicity it can possess a great threat for human health (Afshan et al., 2014). Depending on the degree and duration of Pb exposure, a variety of consequences might occur. Lead accounts for most of the cases of pediatric heavy metal poisoning. Lead accumulates in the liver, kidney, brain and bone (Afshan et al., 2014). Newborns and young children are especially delicate to even low levels of lead (Elder and Collins, 1991). Acute Pb toxicity after absorption of contaminated seafood usually occurs in brain and kidney, and it is absorbed through the gastrointestinal tract (Markowitz, 2000) is regulated by nutritional calcium and iron status and age (children adsorb more, and consequently, are more vulnerable than adults) of exposed humans and solubility and lead species, among others (Flegal, 1986).
Mercury (Hg)
Mercury toxicity depends on its chemical form, methyl mercury is found to be more hazardous than metallic form of mercury (Verma et al., 2018). Mercury in the atmosphere has nearly tripled through human activities and the atmospheric burden is increasing 1.5 percent per year (Clifton II, 2007). Natural mercury arises from volcanoes, land or water surfaces due to the use of land, biomass burning, by evaporation from the ocean, meteorological conditions and gaseous mercury at air water soil snow ice exchange (Boening, 2000; Mason, 2009; Pirrone et al., 2001). Whereas, major anthropogenic source of mercury (~ 60% of the year 2000) is the combustion of fossil fuels (coal; stationary combustion) followed by gold mining, non-ferrous metals manufacturing, cement production, waste disposal and caustic soda production (Pacyna et al., 2006; Pirrone et al., 2010). Fish is the primary source of MeHg poisoning in humans (Rice et al., 2014) as well as various species of fish tend to have higher rates of MeHg bioaccumulation (Mozaffarian and Rimm, 2006).
Cadmium (Cd)
Cadmium is known as the most toxic and non-essential heavy metal (Jaishankar et al., 2014) and enters the environment by natural sources, such as volcanism. Anthropogenic activities such as smelting, mining nonferrous metals, production of nonferrous metals, iron and steel and the production and disposal of Cadmium containing materials (electroplating, pigments, stabilizers and Ni-Cd batteries) use phosphate fertilizers, arsenic pesticides, herbicides, fungicides, plastic stabilizers, wood preservatives and others (Thornton, 1992). Additionally, Cd chronic toxicity affects bones, causing fractures, severe pain, malformations, hypercalciuria and impaired vitamin D metabolism (Bhattacharyya et al., 1992). Cd is transported by blood and distributed mainly to the liver and kidney where it is long-term stored in the organism.
Chromium (Cr)
Chromium is one of the most common pollutants in the environment where Cr (VI) and Cr (III) being the most stable forms (Velma et al., 2009). The toxicity of chromium is mainly relate to its Cr (VI) form. In hexavalent [Cr (VI)] form, health risks of Cr exposure vary depending on its oxidation state, ranging from moderate toxicity to high toxicity (Velma et al., 2009). Chromium enters into aquatic environment from a wide variety of natural and anthropogenic sources like as industrial applications (leather tanning, electroplating, and corrosion protection) contaminate ground water (Palmer and Wittbrodt, 1991), discharges from manufacturing processes and cooling towers (Elwood et al., 1980).
Iron (Fe)
Iron is mostly abundant metal which have basic roles in cellular respiration and metabolism. Iron can switch its redox state and in case of oxygen availability convert into ferrous to ferric iron (Fe2+ to Fe3+). This reaction generates the superoxide anion, which through a series of redox reactions leads to the generation of toxic hydroxyl radicals. Henceforth, iron can be both beneficial and toxic effects to organisms and it is mandatory to balance iron status in the body for maintaining biological functions, whereas excess Fe2+ which can lead to oxidative stress (Carriquiriborde et al., 2004).
Manganese (Mn)
Manganese is one of the vital elements for aquatic animals that have a negative effects on total erythrocyte count (TEC), haemoglobin (Hb), haematocrit (Hct), mean corpuscular volume (MCV) and mean corpuscular haemoglobin (MCH) concentrations (Sharma and Langer, 2014). Mn toxicity accounted for abnormal structure of nucleus in RBCs which finally impacts on RBCs production in blood levels. Several researchers reported that Mn toxicity is noticeable in some aquatic species such as goldfish (Carassius auratus) (Vieira et al., 2012). In addition, it caused oxidative stress and increases GPx activity.
Nickel (Ni)
Initial effects of Ni on the respiratory system of aquatic animals are causing swollen gill lamellae, distress in the ventilation and respiratory system (Pane et al., 2003). Ni toxicity is highly prevalent in goldfish (Carassius auratus), streaked prochilod (Prochilodus lineatus) and mummichog (Fundulus heteroclitus) (Palermo et al., 2015). Behavioral effects of Ni exposure were studied and found out that Ni affects locomotors activity in fish, thus causing hypo activity in goldfish (Carassius auratus) and round goby (Neogobius melanostomus) (Blewett and Leonard, 2017).
Zinc (Zn)
Zinc is common heavy metals for aquatic toxicity worldwide. Geological rocks, industrial wastages and domestic garbage’s are the major source for Zinc pollution in freshwater and sea water (Adeyeye, 1996). Excessive levels of Zn causes reduce physical and growth performance of fish. Zn initially deposits in gills and resulting top hypoxia which leads to death. Alternations of hatchability and blood hematology also caused by excessive levels of Zn. Deficiency of Zn effects the fish behavior such as restless swimming, air guzzling, periods of dormancy and death (Kori-Siakpere and Ubogu, 2008).
Public health hazards of heavy metals by fish and fish products intake
Arsenic: Arsenic contamination is an alarming issue in worldwide and has given a higher weight in Bangladesh. Arsenic is one of the crucial heavy metals causing public health hazards. Semi-metallic nature of As accounted for toxic and carcinogenic effects (Singh et al., 2007). The primary signs and symptoms of acute arsenic poisoning includes nausea, vomiting, abdominal cramping, muscle pain and diarrhea. This is followed by immobility and creeping of the head, hand and legs, muscle shivering and death. In case of chronic exposure due to contaminated drinking water resulting different lesions such as pigmentation in skins, and hyperkeratosis in palms and soles of the feet. Lower levels of arsenic exposure can cause decrease production of blood cells such as erythrocytes and leukocytes (Jaishankar et al., 2014). Damaging blood vessels and heart beat abnormality also occurred due to low As exposure. Long time exposure of As can develop cancer in the skin, liver, kidneys and lungs. Cardiovascular and pulmonary complications, hypertension and neurotoxicity also outcomes of long term As consumption by human (Smith et al., 2000).
Lead (Pb)
Fossil fuel burning, manufacturing and mining play vital role for accumulation of Pb in water, soil and air. According to the Environmental Protection Agency (EPA), lead is considered a carcinogen agents. Chronic exposure of lead by fish and fish products intake can cause in pregnancy difficulties, mental disorder, autism, dyslexia, hyperactivity, muscular atony, kidney and brain damage (Martin and Griswold, 2009). Acute exposure leads to anorexia, hypertension, abdominal pain, renal dysfunction, fatigue, arthritis and hallucinations. Plasma membrane influx into the interstitial spaces of the brain when the blood brain barrier is exposed to elevated levels of lead concentration, resulting edema (Teo et al., 1997). It also disturbs the intracellular second messenger systems and alters the central nervous system functions.
Mercury
People mainly exposed to mercury when they continuous intake of fish and shellfish. Mercury is toxic for peripheral and central nervous system (Washington, 2005). It also harmful for digestive and immune systems, lungs and kidneys, and may be fatal. Symptoms include tremors, insomnia, memory loss, neuromuscular effects, headaches and cognitive and motor dysfunction. Mild, subclinical signs of central nervous system toxicity can be seen in workers exposed to an elemental mercury level in the air of 20 μg/m3 or more for several years (Washington, 2005).
Cadmium
Cadmium is a byproduct of zinc production (Jaishankar et al., 2014). Cadmium is highly deposited in proximal tubular cells of kidney which caused kidney toxicity and renal dysfunction (Bernard, 2008). Hypercalciuria, renal stones formation and osteoporosis caused by continuous exposure of Cd. Deposition of excess concentrations in lungs may cause severe damage (Bernard, 2008). Inhaling higher levels of Cd have a detrimental effects in lungs. In gastrointestinal system, Cd causes irritation, vomiting and diarrhea. Pregnancy complications, premature birth and unexpected birth weights are occurred due to high levels of exposure during pregnancy period (Henson and Chedrese, 2004).
Chromium
Chromium derivatives are highly perpetual in water sediments. Cr(III) and Cr(VI) are the common stable forms and only their relation to human exposure is of high interest (Zhitkovich, 2011). Chromium derivatives such as lead chromates, strontium chromate, zinc chromates and calcium chromate are showed toxic and carcinogenic properties. Metal coatings and alloys, magnetic tapes, paint pigments, rubber, cement, paper, wood preservatives, leather tanning and metal plating are responsible for Cr contamination in freshwater and seawater (Martin and Griswold, 2009). Higher concentration exposure of chromium compounds caused decrease levels of erythrocyte glutathione reductase, which in turn lowers the capacity to reduce methemoglobin to hemoglobin (Jaishankar et al., 2014). Chromate compounds also responsible for chromosomal aberrations, DNA adducts, exchange of sister chromatid, alterations in replication and transcription of DNA (Matsumoto et al., 2006).
Iron
Aquatic animals is the prominent source of iron and it shows various health benefits in humans (Rahmani et al., 2018). However, continuous high intake initiates toxic effects in human body (Ashraf et al., 2006). Mammals are not capable for eliminate excess amount of Fe from body through secretions and continuous deposition of Fe causing organs failure with detrimental outcomes. The maximum permitted concentration of Fe in fish fillet established by FAO/WHO 100 μg/kg ww, respectively (FAO/WHO, 2009).
Manganese (Mn)
Manganese is very pivotal elements for both animals and plants, especially for skeletal and reproductive system in mammals. Mn helps the body absorb vitamins B1 and E, and works with all B-complex vitamins in combating depression, anxiety, and other disorders of the nervous system (Eneji et al., 2011). Excess Mn interferes with the absorption of dietary Fe and long-term exposure may result in Fe-deficiency anemia and the impairment of the activity of copper dependent metalloenzymes. Significant increases in Mn concentrations have been observed in patients with severe hepatitis, dialysis patients, and patients who have had cardiac arrests. In addition, studies on mice injected with Mn chloride tetrahydrate during gestation have shown fetotoxicity.
Nickel (Ni)
Ni is considered one of the most important elements to perform functions of vital organs but excess amount is pernicious for human body (Genchi et al., 2020). In human body, Ni combines with thiol resulting in the formation of Ni-Thiol complexes. When these complexes react with molecular oxygen it results in free radicals production that ultimately causes Ni toxicity (Das et al., 2006). Researchers investigated that because of Ni exposure to human body its physiological chemistry is altered because of decreased excretion of calcium ions via urinary routes and also because retention of nitrogen is decreased following Ni exposure. Red Blood Cells in blood, packed cell volume (PCV) %, and the concentration of hemoglobin were increased due to raised synthesis of erythropoietin and this happened in response to tissue hypoxia produced by Ni exposure (Denkhaus and Salnikow, 2002). Placental membrane is disrupted because of peroxidation of lipids induced by prenatal Ni exposure. Because of this peroxidation pathway permeability of placenta is increased and toxic damage is induced in fetus (Cortijo et al., 2010).
Zinc
Zinc is an eccentric element that is little essential for human vital organs. Hence, lack of Zn resulting reduce in sense of taste and smell, slow wound healing, loss of appetite, and skin sores (Afshan et al., 2014). Although humans beings can manage large concentrations of Zn, too much Zn can cause prominent health problems such as skin annoyances, such as stomach cramps, anemia, vomiting and nausea. Excessive concentration of Zn is deleterious for pancreas, initiate disturbances in protein metabolism and resulting arteriosclerosis. Several researchers reported that adverse effects of the fish are neutralized in the process of cooking (Afshan et al., 2014).
Conclusions and Recommendations
The concentration of HMs is dangerous for the aquatic animals as well as human health. Environmental contamination from HMs may damage the marine organisms at the cellular level and causes imbalance in the ecosystem. HMs in the aquatic organism might entered through the three ways: the body surface, gills and food. In aquatic environment, microorganisms accumulate metals and consequently, small fish become enriched with the accumulated substances. Predatory fish again, general display higher levels than their prey. Man at the end of food chain suffers from the results of an enrichment having taken place at each trophic level, where less is excreted than ingested. Therefore, preventive measures should be taken to reduce the intensity of aquatic pollution through the HMs.
Acknowledgements
We are grateful to all faculty members of Department of Fisheries Resource Management, Chattogram Veterinary and Animal Sciences University, Chattogram, Bangladesh for continuous support during the preparation of this review manuscript.
Novelty Statement
This review paper narrates the recent information’s about the effects of heavy metals on aquatic animals with their public health importance.
Author’s Contribution
MAM and SIA: Conceptualization.
MAM and MAR: Literature review.
MAM, MAR and SIA: Writing the original paper, review, edit and supervision.
All authors have read carefully and approved the manuscript.
Compliance with ethics requirements
Not applicable
Funding
The author(s) received no specific funding for this work.
Conflict of interest
The authors have declared no conflict of interest.
References
Abdel-Mohsien, H.S., and Mahmoud, M.A.M., 2015. Accumulation of some heavy metals in andlt, iandgt, oreochromis niloticusandlt, iandgt from the Nile in Egypt: Potential hazards to fish and consumers. J. Environ. Prot., 6(9): 1003–1013. https://doi.org/10.4236/jep.2015.69089
Adeyeye, E.I., 1996. Determination of major elements in Illisha Africana fish, associated water and soil sediments from some freshwater ponds. Bangladesh J. Sci. Ind. Res., 31: 171–184.
Afshan, S., Ali, S., Ameen, U.S., Farid, M., Bharwana, S.A., Hannan, F., and Ahmad, R., 2014. Effect of different heavy metal pollution on fish. Res. J. Chem. Environ. Sci., 2(1): 74–79.
Arora, M., Kiran, B., Rani, S., Rani, A., Kaur, B., and Mittal, N., 2008. Heavy metal accumulation in vegetables irrigated with water from different sources. Food Chem., 111(4): 811–815. https://doi.org/10.1016/j.foodchem.2008.04.049
Ashraf, W., Seddigi, Z., Abulkibash, A., and Khalid, M., 2006. Levels of selected metals in canned fish consumed in Kingdom of Saudi Arabia. Environ. Monit. Assess., 117(1): 271–279. https://doi.org/10.1007/s10661-006-0989-5
Balami, S., Sharma, A., and Karn, R., 2019. Significance of nutritional value of fish for human health. Malays. J. Halal Res., 2(2): 32–34. https://doi.org/10.2478/mjhr-2019-0012
Bears, H., Richards, J.G., and Schulte, P.M., 2006. Arsenic exposure alters hepatic arsenic species composition and stress-mediated gene expression in the common killifish (Fundulus heteroclitus). Aquatic Toxicol., 77(3): 257–266. https://doi.org/10.1016/j.aquatox.2005.12.008
Bernard, A., 2008. Cadmium and its adverse effects on human health. Indian J. Med. Res., 128(4): 557.
Bhattacharyya, M.H., Sacco-Gibson, N.A., and Peterson, D.P., 1992. Cadmium-induced bone loss: increased susceptibility in female beagles after ovariectomy. IARC Sci. Publ., 118: 279–286.
Blewett, T.A., and Leonard, E.M., 2017. Mechanisms of nickel toxicity to fish and invertebrates in marine and estuarine waters. Environ. Pollut., 223: 311–322. https://doi.org/10.1016/j.envpol.2017.01.028
Boening, D.W., 2000. Ecological effects, transport, and fate of mercury: A general review. Chemosphere, 40(12): 1335–1351. https://doi.org/10.1016/S0045-6535(99)00283-0
Carriquiriborde, P., Handy, R.D., and Davies, S.J., 2004. Physiological modulation of iron metabolism in rainbow trout (Oncorhynchus mykiss) fed low and high iron diets. J. Exp. Biol., 207(1): 75–86. https://doi.org/10.1242/jeb.00712
Clifton II, J.C., 2007. Mercury exposure and public health. Pediatr. Clin. North Am., 54(2): 237-e1. https://doi.org/10.1016/j.pcl.2007.02.005
Cortijo, J., Milara, J., Mata, M., Donet, E., Gavara, N., Peel, S.E., Hall, I.P., and Morcillo, E.J., 2010. Nickel induces intracellular calcium mobilization and pathophysiological responses in human cultured airway epithelial cells. Chemico-Biol. Interact., 183(1): 25–33. https://doi.org/10.1016/j.cbi.2009.09.011
Das, K.K., Gupta, A.D., Dhundasi, S.A., Patil, A.M., Das, S.N., Ambekar, J.G., 2006. Effect of L-ascorbic acid on nickel-induced alterations in serum lipid profiles and liver histopathology in rats. J. Basic Clin. Physiol. Pharmacol. 17(1):29–44.
Denkhaus, E., and Salnikow, K., 2002. Nickel essentiality, toxicity, and carcinogenicity. Crit. Rev. Oncol. Hematol., 42(1): 35–56. https://doi.org/10.1016/S1040-8428(01)00214-1
Elder, J.F., and Collins, J.J., 1991. Freshwater molluscs as indicators of bioavailability and toxicity of metals in surface water systems. Rev. Environ. Contam. Toxicol., 37–79. https://doi.org/10.1007/978-1-4612-3198-1_2
Elwood, J.W., Beauchamp, J.J., and Allen, C.P., 1980. Chromium levels in fish from a lake chronically contaminated with chromates from cooling towers. Int. J. Environ. Stud., 14(4): 289–298. https://doi.org/10.1080/00207238008737408
Eneji, I.S., Sha’Ato, R., and Annune, P.A., 2011. Bioaccumulation of heavy metals in fish (Tilapia Zilli and Clarias Gariepinus) organs from River Benue, North Central Nigeria. Pak. J. Anal. Environ. Chem., 12(1): 25–31. http://search.ebscohost.com/login.aspx?direct=truean=Cm+3==andcrl=c
FAO/WHO., 2009. Codex General Standard for Food Additives. Food and Agricultural Organization of the United Nations and World Health Organization., Rome.
Flegal, A.R., 1986. Lead in tropical marine systems: A review. Sci. Total Environ., 58(1–2): 1–8. https://doi.org/10.1016/0048-9697(86)90071-9
Genchi, G., Carocci, A., Lauria, G., Sinicropi, M.S., and Catalano, A., 2020. Nickel: Human health and environmental toxicology. Int. J. Environ. Res. Publ. Health, 17(3): 679. https://doi.org/10.3390/ijerph17030679
Goodwin, T.H., Young, A.R., Holmes, M.G.R., Old, G.H., Hewitt, N., Leeks, G.J.L., Packman, J.C., and Smith, B.P.G., 2003. The temporal and spatial variability of sediment transport and yields within the Bradford Beck catchment, West Yorkshire. Sci. Total Environ., 314: 475–494. https://doi.org/10.1016/S0048-9697(03)00069-X
Gupta, A., Rai, D.K., Pandey, R.S., and Sharma, B., 2009. Analysis of some heavy metals in the riverine water, sediments and fish from river Ganges at Allahabad. Environ. Monit. Assess., 157(1): 449–458. https://doi.org/10.1007/s10661-008-0547-4
Henson, M.C., and Chedrese, P.J., 2004. Endocrine disruption by cadmium, a common environmental toxicant with paradoxical effects on reproduction. Exp. Biol. Med., 229(5): 383–392. https://doi.org/10.1177/153537020422900506
Jaishankar, M., Tseten, T., Anbalagan, N., Mathew, B.B., and Beeregowda, K.N., 2014. Toxicity, mechanism and health effects of some heavy metals. Interdisciplin. Toxicol., 7(2): 60-72. https://doi.org/10.2478/intox-2014-0009
Karayakar, F., Işık, U., Cicik, B., and Canli, M., 2022. Heavy metal levels in economically important fish species sold by fishermen in Karatas (Adana/ Turkey). J. Food Compos. Anal., 106: 104348. https://doi.org/10.1016/j.jfca.2021.104348
Kori-Siakpere, O., and Ubogu, E.O., 2008. Sublethal haematological effects of zinc on the freshwater fish, Heteroclarias sp. (Osteichthyes: Clariidae). Afr. J. Biotechnol., 7(12). https://doi.org/10.5897/AJB07.706
Mansour, S.A.,Sidky, M.M. 2002. Ecotoxicological studies: 3. Heavy metals contaminating water and fish from Fayoum Gov, Egypt. Food Chem. 78:15–22.
Markowitz, M., 2000. Lead poisoning. Pediatr. Rev., 21(10): 327–335. https://doi.org/10.1542/pir.21.10.327
Martin, S., and Griswold, W., 2009. Human health effects of heavy metals. Environ. Sci. Technol. Briefs Citizens, 15: 1–6.
Mason, R.P., 2009. Mercury emissions from natural processes and their importance in the global mercury cycle. In Mercury fate and transport in the global atmosphere. Springer. pp. 173–191. https://doi.org/10.1007/978-0-387-93958-2_7
Matsumoto, S.T., Mantovani, M.S., Malaguttii, M.I.A., Dias, A.L., Fonseca, I.C., and Marin-Morales, M.A., 2006. Genotoxicity and mutagenicity of water contaminated with tannery effluents, as evaluated by the micronucleus test and comet assay using the fish Oreochromis niloticus and chromosome aberrations in onion root-tips. Genet. Mol. Biol., 29(1): 148–158. https://doi.org/10.1590/S1415-47572006000100028
Mozaffarian, D., and Rimm, E.B., 2006. Fish intake, contaminants, and human health: Evaluating the risks and the benefits. J. Am. Med. Assoc., 296(15): 1885–1899. https://doi.org/10.1001/jama.296.15.1885
Osman, A.G.M., Wuertz, S., Mekkawy, I.A., Exner, H., and Kirschbaum, F., 2007. Lead induced malformations in embryos of the African catfish Clarias gariepinus (Burchell, 1822). Environ. Toxicol. Int. J., 22(4): 375–389. https://doi.org/10.1002/tox.20272
Pacyna, E.G., Pacyna, J.M., Steenhuisen, F., and Wilson, S., 2006. Global anthropogenic mercury emission inventory for 2000. Atmos. Environ., 40(22): 4048–4063. https://doi.org/10.1016/j.atmosenv.2006.03.041
Palermo, F.F., Risso, W.E., Simonato, J.D., and Martinez, C.B.R., 2015. Bioaccumulation of nickel and its biochemical and genotoxic effects on juveniles of the neotropical fish Prochilodus lineatus. Ecotoxicol. Environ. Saf., 116: 19–28. https://doi.org/10.1016/j.ecoenv.2015.02.032
Palmer, C.D., and Wittbrodt, P.R., 1991. Processes affecting the remediation of chromium-contaminated sites. Environ. Health Perspect., 92: 25–40. https://doi.org/10.1289/ehp.919225
Pandey, G., and Madhuri, S., 2014. Heavy metals causing toxicity in animals and fishes. Res. J. Anim. Vet. Fish. Sci., 2(2): 17–23. https://doi.org/10.14737/journal.aavs/2014/2.4s.17.23
Pane, E.F., Richards, J.G., and Wood, C.M., 2003. Acute waterborne nickel toxicity in the rainbow trout (Oncorhynchus mykiss) occurs by a respiratory rather than ionoregulatory mechanism. Aquat. Toxicol., 63(1): 65–82. https://doi.org/10.1016/S0166-445X(02)00131-5
Pirrone, N., Costa, P., Pacyna, J.M., and Ferrara, R., 2001. Mercury emissions to the atmosphere from natural and anthropogenic sources in the Mediterranean region. Atmos. Environ., 35(17): 2997–3006. https://doi.org/10.1016/S1352-2310(01)00103-0
Pirrone, Nicola, Cinnirella, S., Feng, X., Finkelman, R.B., Friedli, H.R., Leaner, J., Mason, R., Mukherjee, A.B., Stracher, G.B., and Streets, D.G., 2010. Global mercury emissions to the atmosphere from anthropogenic and natural sources. Atmosphere. Chem. Phys., 10(13): 5951–5964. https://doi.org/10.5194/acp-10-5951-2010
Rahmani, J., Fakhri, Y., Shahsavani, A., Bahmani, Z., Urbina, M.A., Chirumbolo, S., Keramati, H., Moradi, B., Bay, A., and Bjørklund, G., 2018. A systematic review and meta-analysis of metal concentrations in canned tuna fish in Iran and human health risk assessment. Food Chem. Toxicol., 118: 753–765. https://doi.org/10.1016/j.fct.2018.06.023
Ribeiro, C.A.O., Vollaire, Y., Sanchez-Chardi, A., and Roche, H., 2005. Bioaccumulation and the effects of organochlorine pesticides, PAH and heavy metals in the Eel (Anguilla anguilla) at the Camargue Nature Reserve, France. Aquatic Toxicol., 74(1): 53–69. https://doi.org/10.1016/j.aquatox.2005.04.008
Rice, K.M., Walker, E.M., Wu, M., Gillette, C., and Blough, E.R., 2014. Environmental mercury and its toxic effects. J. Prev. Med. Publ. Health, 47(2): 74–83. https://doi.org/10.3961/jpmph.2014.47.2.74
Rossman, T.G., 2003. Mechanism of arsenic carcinogenesis: An integrated approach. Mutat. Res. Fundam. Mol. Mech. Mutagen., 533(1–2): 37–65. https://doi.org/10.1016/j.mrfmmm.2003.07.009
Schlenk, D., Wolford, L., Chelius, M., Steevens, J., and Chan, K.M., 1997. Effect of arsenite, arsenate, and the herbicide monosodium methyl arsonate (MSMA) on hepatic metallothionein expression and lipid peroxidation in channel catfish. Comp. Biochem. Physiol. C Pharmacol. Toxicol. Endocrinol., 118(2): 177–183. https://doi.org/10.1016/S0742-8413(97)00083-2
Shah, A.I., 2017. Heavy metal impact on aquatic life and human health. An over view. IAIA17 conference proceedings. IA’s contribution in addressing climate change 37th annual conference of the international association for impact assessment, April, 4-7 April 2017. Le Centre Sheraton, Montréal. http://conferences.iaia.org/2017/final-papers/Shah, Alkesh - Heavy Metal Impacto on Aquatic Life and Human Health.pdf
Sharma, J., and Langer, S., 2014. Effect of manganese on haematological parameters of fish, Garra gotyla gotyla. J. Entomol. Zool. Stud., 2(3): 77–81.
Singh, A.K., and Banerjee, T.K., 2008. Toxic effects of sodium arsenate (Na2HAsO4x7H2O) on the skin epidermis of air-breathing catfish Clarias batrachus (L.). Vet. Arhiv., 78(1): 73–88.
Singh, N., Kumar, D., and Sahu, A.P., 2007. Arsenic in the environment: effects on human health and possible prevention. J. Environ. Biol., 28(2): 359.
Smith, A.H., Lingas, E.O., and Rahman, M., 2000. Contamination of drinking-water by arsenic in Bangladesh: A public health emergency. Bull. World Health Organ., 78: 1093–1103.
Teo, J.G., Goh, K.Y., Ahuja, A., Ng, H.K., and Poon, W.S., 1997. Intracranial vascular calcifications, glioblastoma multiforme, and lead poisoning. Am. J. Neuroradiol., 18(3): 576–579.
Thornton, I., 1992. Sources and pathways of cadmium in the environment. IARC Sci. Publ., 118: 149–162.
Vaseem, H., and Banerjee, T.K., 2016. Evaluation of pollution of Ganga River water using fish as bioindicator. Environ. Monit. Assess., 188(8): 1–9. https://doi.org/10.1007/s10661-016-5433-x
Velma, V., Vutukuru, S.S., and Tchounwou, P.B., 2009. Ecotoxicology of hexavalent chromium in freshwater fish: A critical review. Rev. Environ. Health, 24(2): 129–146. https://doi.org/10.1515/REVEH.2009.24.2.129
Verma, R., Vijayalakshmy, K., and Chaudhiry, V., 2018. Detrimental impacts of heavy metals on animal reproduction: A review. J. Entomol. Zool. Stud., 6: 27–30.
Vieira, M.C., Torronteras, R., Córdoba, F., and Canalejo, A., 2012. Acute toxicity of manganese in goldfish Carassius auratus is associated with oxidative stress and organ specific antioxidant responses. Ecotoxicol. Environ. Saf., 78: 212–217. https://doi.org/10.1016/j.ecoenv.2011.11.015
Washington, K.R.M., 2005. Mercury exposure: Medical and public health issues. Trans. Am. Clin. Climatol. Assoc., 116: 127–154. https://www.ncbi.nlm.nih.gov/pmc/articles/PMC1473138/pdf/tacca116000127.pdf
Zhitkovich, A., 2011. Chromium in drinking water: Sources, metabolism, and cancer risks. Chem. Res. Toxicol., 24(10): 1617–1629. https://doi.org/10.1021/tx200251t
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