Water is the most essential natural resource and is utilized in a wide range of contexts and at varying intensities around the planet (
McDonald and Kay, 1998). It is one of nature’s most vital gifts for keeping everything from microbes to people alive. Rapid industrialization in emerging nations aided economic growth, but it also had a significant negative impact on agricultural operations, human health and the environment as a whole due to water pollution (
Reddy and Behera, 2005). The contaminated water adversely affected agricultural productivity and restricted to yield of crops. In this connection,
Prabhu (2009) finds that organic pollution in Akaki water body and irrigation with contaminated river water containing variables amount of heavy metals leads to increases in the concentration of metals in soil and vegetables and impacts negatively. High concentrations of metal will degrade soil fertility and also make poisonous vegetables
(Kim et al., 2015). Arsenic is the king of poisons, high concentration of arsenic in drinking water and the food chain has caused severe health problems (
Mukharjee and Bhattacharya, 2001).
River water is an indispensable natural resource supporting economic and social development. River and streams have largely been exploited for supplying water for human consumption, livestock drinking, aquaculture, irrigation, industries, transportation, recreation and other purposes
(Barakat et al., 2016). Despite these benefits, in developing countries, rivers and streams are subjected to various anthropogenic and natural sources of pollution. These include expansion of urban, industrial growth, agrochemicals run-off, municipal and domestic wastes
(Oketola et al., 2013). As a result, organic, nutrients, trace metals and potentially hazardous substances are introduced in river system, causing deterioration of river water quality.
Further, river water pollution has negative effects on human health, economic stability and agricultural productivity (
Singh, 2020a). In addition, pollution’s negative impacts on water quality have a domino effect, harming aquatic life while upsetting the natural order of things and decreasing the bioavailability of drinkable water. Consuming polluted water on a frequent basis may have serious consequences for human health, including reduced blood flow, nausea, vomiting, diarrhoea, skin sores, cholera and harm to the central nervous system (
Afroz, 2014).
The cross-country and cross-sector spill-over of environmental pollution through of waterborne effluents continues to be an important topic of research in environmental economics
(Costantini et al., 2013). Environmental pollution, as it is unambiguously accepted in the subject in general is a public ‘bad’ requiring interventions to ameliorate the negative externality associated with it. The loss of agricultural production and lower land fertility owing to pollution transmission are therefore central to various adjustments that an economy may have to endure. Effect of trans-boundary pollution generated by an upstream country on the welfare of a downstream country through trade linkage offers the mainstay of the present study.
The literature on the use of contaminated river water shows that farmers are well aware of the risks associated with it
(Haghi et al., 2020; Chen et al., 2022). A study conducted by
Haghi et al., (2020) in Iran revealed that more than 60 per cent of farmers perceived high or very high risk from treated wastewater use in crop production resulting in low crop yield with high input cost. The study also claimed that there is no specific source of information available on the subject for farmers. Further, extension services provided by the government were the most common source of information, followed by relatives and fellow farmers, which are relatively less aware of river water pollution. A responsible person like the local farmer help desk which is the only reliable source of information hardly engaged with farmers to deal with wastewater issues.
Likewise,
Chen et al., (2022) have conducted a study on farmers’ perception of heavy metal-polluted cultivated land. The results show that farmers are aware of land pollution due to heavy metal but the cost of land treatment is beyond their capacity, hence, they are not in a position to deal with the existing crisis. Further,
Zhou et al., (2022) have conducted a study in Hubei Province, China on the impact of heavy metal pollution in farm productivity and also captures farmer’s perception on the use of polluted mining water in agriculture. The results demonstrate that knowledge and information have significant positive effects on perceptions. They divided farmers into two groups namely farmers’ adaptation perception and risk perception. A low level of adaptation perception, for which technology is the most important limiting factor followed by money, limits the adaptation behaviors of farmers. In additions, farmers’ characteristics have significant effects on adaptation behaviors. Farmers tend to engage in adaptation behavior according to the actual situation of their family such as income and obligations.
Withanachchi et al., (2018) have conducted a study in Mashavera River Basin, Georgia to capture farmers’ perception of the water quality and their perceived risks to the economy. They found that aesthetic attributes (
i.e., color changes observed in the river) and the sources of the water contamination (
i.e., mining sites) were the main predictor variables for a perceived risk to water quality, health and livelihoods. The people who work in agriculture as the main income source had more concern about their ability to sell their agricultural products as a result of water contamination in river, compared with people for whom agriculture is a secondary source of income. The results also show that the health risk is perceived more strongly in areas with more heavily contaminated water compared to less polluted areas.
Yonggua et al., (2001) have estimated the impact of industrial pollution on agriculture, human health and industrial in Chongqingm, which is one of the heavily polluted mega cities in China. It was estimated that the total costs of industrial pollution were 1.2 per cent of Chongqing’s gross domestic product (GDP). Of this, 56 percent is in agriculture sector, while the damages to human capital and industrial sector are 20 per cent and 18 per cent, respectively. Further,
Hanif et al., (2020) have conducted a study to evaluate the Kapotaksha river water pollution status and its impacts on human health. The findings of this study highlight that the polluted water due to various types of diseases such as scabies, asthma, dysentery and respiratory disease. Most of the people (49 per cent) are affected by scabies, 4 per cent are affected by diarrhea, 5 per cent are affected by dysentery, 25 per cent of people are suffering from respiratory diseases and 4 per cent suffering from asthma and the polluted water pollutes soil by using the water in agriculture purpose answered by 20 per cent respondents. If someone does not use contaminated water can not affect soil answered by 80 per cent of respondents. In totality, they find that river water becomes more polluted and harmful for human health and environment because contaminated water hampered by the local colony, local trader, lack of proper management of sewage system, mis-use on the river bank area for the dumping various soil waste on the river bank, chemical fertilizers, industries
etc.
Above mentioned studies highlights the nexus between river water contamination and livelihoods of farmers using contamination water for irrigation and drinking purposes. Hence, the present study aims to capture farmers’ perceptions of river water contamination in the Maharajganj district of Eastern Uttar Pradesh, India. The study also recorded farmers’ responses on the impact of contaminated river water on agriculture production and human health. How contaminated water is creating chaos among the farming communities living bank of Rohini River which is polluted by heavy metals.