Chronic effects of organic pesticides on the aquatic environment and human health: A review

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Abstract

Aquatic environment could be termed as the intercommunicating arrangement of water, sediment and biota that provide food for humanity. Aquatic environments have deteriorated substantially due to the accumulation of toxic inorganic and organic pollutants that cause potentially adverse, widespread and detrimental effects on human health. Among the toxic pollutants, pesticides are among the most concerning compounds. Pesticides are applied broadly to restrict insect infestation in agricultural crops as well as to eradicate a variety of pests and disease bearing organisms such as mice, rats, ticks and mosquitoes from human habitats and environments. Among the top ten pesticide-using countries of the world, more than 30 % are in South-Asia. Organochlorine pesticides (OCPs) such as dichloro-diphenyl-trichloroethane (DDT), aldrin, dieldrin and polychlorinated biphenyls (PCBs) are among the most environmentally detrimental pesticides. OCPs can persist for more than 40 years among components of the environment such as soil, water, fish tissues, and other aquatic biotas. Environmental integrity and human health are threatened by over 500,000 tons of OCPs in numerous countries. About 1–5 million cases of intense pesticide toxicity happen annually worldwide, causing approximately 200,000 deaths annually, in part because of bio-accumulation and bio-magnification of persistent pesticides. In aquatic environments, pesticide toxicity causes mortality, reproductive failure, egg shell thinning, suppression of the immune system, and other fish health complications such as excessive slime on fish scales and gills, cancers, tumors and lesions. In humans, pesticide toxicity causes short-term diseases such as skin and eye irritation, nausea, dizziness, headaches, and also chronic impacts such as diabetes, asthma and cancer. This review provides the historical overview with regard to the levels and distribution of organic pesticides in a range of environmental compartments of the Asian region as well as a worldwide perspective. It also presents a comprehensive consideration of chronic effects of pesticides on human health.

Introduction

Aquatic resources (ponds, lakes, rivers, streams as well as oceans) and fisheries are especially precious natural assets. Recognition of aquatic systems along with fisheries has been associated to rising concern about the impact of increased human population and their activity on the aquatic environment. Pesticides are a major group of toxic compounds linked to human exposure that inflict substantial impacts on aquatic environments (Helfrich and Hipkins, 2009).

Any substance or mixture of substances engaged for mitigating, restricting, demolishing or dispersing pests such as weeds, insects, rats, nematodes, mites etc. are referred to as pesticides (Zhang et al., 2011). The worldwide application of pesticides is increasing steadily as a consequence of continually-rising population in need of increased quantities of food. Liu et al. (2002) documented that around one third of the worldwide agricultural products are subject to pesticide application. Cai (2008) reported that if pesticides are not applied, 32 %, 54 % and 78 % production loss of cereals, vegetable and fruits, respectively could be anticipated. Pesticides figure essentially in the health sector beyond their role in agriculture. The most effective and broadly utilized techniques for restricting malaria-bearing insects with insecticides have been reported by World Health Organization (WHO) and described by Elibariki and Muguta (2017). Particularly during improper application, almost all pesticides become severely toxic to the environment as well as to humans. Ubiquitous application and discharge of pesticides is considered among the most common sources of pesticide metabolites in river, sediment and air with threatening ecosystem and human health implications. Environmental pollution originating from pesticides creates severe problems in Asia, Africa, Eastern Europe, Latin America and the Middle East (Sitaramaraju et al., 2014). Organchlorine pesticides like hexachlorobenzene, heptachlor, endrin, dieldrin, aldrin, hexachlorocyclohexane (HCHs) and dichlorodiphenyltrichloroethane (DDTs) are particularly responsible for acute cases of pollution. Organochlorine pesticides (OCPs) are still used, in spite of being banned in most countries (UNEP, 2009). Due to their properties of high lipid solubility (lipophilicity), less aqueous solubility and less polarity, OCPs are capable of bio-accumulating in food chain causing considerable threats to the global environment, and ultimately to humans (Afful et al., 2010). Because of their extended mobility, persistence in the environment and long half-life, OCPs have been found in water, soil sediments and food for decades after their initial application (Abbassy et al., 1999).

Organochlorine pesticides (OCPs) enter the environment through assorted means including spraying and discharging of polluted wastage into disposal areas, as well as from industrial effluents (CDC, 2016). Prior to accumulation in soils and water, airborne OCPs can move into remote areas as influenced by wind (Leadprathom et al., 2009). By this mode of dispersal, OCPs have been observed at hundreds to thousands of miles from their initial point of use (Hung, 2002). Few OCPs are volatile, whereas some can attach to soil or air particles (Smaranda and Gavrilescu, 2008). The metabolites of DDT and dieldrin can persist in soil for years after initially entering food chains by adsorption (Ritter et al., 1995). By the consumption of these polluted foods, both people and animals are vulnerable to the uptake and accumulation of OCPs. Because of their highly lipophilic (fat soluble) characteristics, the risk of the presence of OCPs in fatty foods is enhanced. Above 90 % OCP adulterants have been found in food, particularly in fish (Li et al., 2008).

For the reasons mentioned above, in order to adopt preventive measures towards limiting the application of organic pesticides for ensuring ecofriendly aquatic ecosystems, there is a compelling need to evaluate the distribution of and contamination by organic pesticides in water, sediment, aquatic biota as well as their ultimate chronic effects on human health.

Section snippets

Water

In aquatic environments, residues of organochlorine pesticides (OCPs) might be introduced through different routes such as wet/dry degradation, non-point sources run-off, industrialized effluents as well as drainage water discharges (Fig. 1). In aquatic ecosystem, OCPs can enter into food chains and become concentrated in living aquatic organisms such as plankton. Primary points of supply and introduction of OCPs in water occur through discharges by way of water–air up-welling mechanisms (

Eco toxicity

Due to the noxious characteristics to some specific classes of living things, pesticides can have profoundly antagonistic impacts on various environmental compartments like water, soil along with other existing living bodies (Aktar et al., 2009). Because of their chemical persistence, some pesticides such as hexachlorobenzene, heptachlor, endrin, dieldrin, dichlorodiphenyltrichloroethane (DDT), chlordane and aldrin remain in the environment for years and can react chemically with persistent

Impact on human health

Organochlorine pesticides cause various health hazards including both acute and chronic diseases. Meenakshi et al. (2012) observed that pesticides may spread in the human body through dermal, oral, eye, and respiratory pathways. Intensity of pesticides toxicity may vary on the basis of exposure pathways like dermal, oral, respiratory system. Absorption can happen from exposure to excessive amounts of residue (Beard et al., 2014). Ear canal and genital areas of the body are more susceptible to

Preventive measures of organic pesticides

To limit the use of organic pesticides, various Asian countries have individual regulatory guidelines (as presented in Table 8) regarding POPs in place within those countries. The environmental act concerning the country-wise application of POPs is stated as below:

Conclusion

Excessive levels of HCHs in water samples from Asian rivers were reported to be 13–593 ng/L where the maximum level is 49.41 % higher than the maximum residue limit (300 ng/L), as recommended by WHO. DDT levels in water were also the highest in Asian rivers and ranged from 6.2 to 7.1 μg/L, which are 67.74–71.83 % higher than the maximum residue limit of 2 µg/L, as recommended by WHO. Higher levels of HCHs and DDTs were found within the range from BDL to 81.2 μg/g and BDL to 109 μg/g, in the

CRediT authorship contribution statement

Md. Ariful Islam: Writing – original draft, Data curation. S.M. Nurul Amin: Conceptualization, Visualization, Investigation, Software. M. Aminur Rahman: Writing – review & editing. Abdul Shukor Juraimi: Visualization. Md. Kamal Uddin: Visualization. Christopher L. Brown: Writing – review & editing. Aziz Arshad: Conceptualization, Supervision, Visualization.

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgments

The authors are so much thankful to UPM library as well as Toxicology Laboratory, Faculty of Agriculture, Universiti Putra Malaysia (UPM) for helping to collect the literatures. The authors are also thankful to National Agricultural Technology Program-2 (NATP-II) Project bearing Memo No.: NATP-2/PIU-BARC-44/2017/1662 (54) and Long-Term Research Grant Scheme from Ministry of education Malaysia (LRGS/1/2019/UPM/1 and VOT number 5545102) for the financial support.

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