Rejuvenation and Restoration of Surface Water Quality Amid COVID-19 Lockdown: A Comprehensive Review in Indian Context
Article information
Abstract
Rivers are our country’s lifeline; however, we have done enough destruction to them which leads to deterioration in water quality. Fortunately, COVID-19 lockdown has brought new life to nature. This encouraged us to outline present review article which discusses pilot impacts of lockdown on six Indian rivers. Few rivers including Ganga showed major improvement at few sites in the assessed parameters such as pH, BOD, DO, FC, etc. The Ganga water at Haridwar and Rishikesh was investigated ‘fit for drinking’ (Class A) while at Kanpur was found fit for ‘outdoor bathing’ (Class B). These improvements can be attributed to strict restriction on human activities during lockdown as there were no or minimum industrial discharge, tourism activities, mass bathing and commercial events near rivers. However, after upliftment of lockdown, these activities will return to their previous state and most likely pollutants will eventually reappear in the water bodies. So, in this review we have reviewed government’s existing water pollution control schemes, analysed their limitations and recommended several scopes for improvement. Further research directions in this area have also been highlighted. We believe that plans and actions described in the article, if implemented, will lead to fruitful outcomes in managing water resources.
Abstract
Graphical Abstract
1. Introduction
December 2019, Hubei province of China experienced an outburst of an unprecedented disease named as Corona Virus Disease 2019 (COVID-19) [1]. The contagious COVID-19 disease was declared as a global pandemic on 11th February 2020 and has affected millions of the people worldwide [1, 2]. To stop this pandemic, lockdown was viewed as the immediate measure. In view of this, a nationwide lockdown was imposed in India on 24th March, 2020 with an enforcement of various rules and regulations [3]. Lockdown seriously disrupted the life of the people by posing many prolonged adverse socio-economic impacts. During these times economic activities came to a standstill, people suffered from loss of livelihoods, production and demand systems were collapsed and healthcare systems were overburdened [4–8]. Therefore, scientists across the world attempted to study effect of these unprecedented restrictions on human activities on broad fields such as psychology, socioeconomics, agriculture, environment, and tourism to name a few [9–13]. Interestingly, the imposition of the lockdown turned out to be inoculation to the environment resulting in overall improvements in lithosphere, atmosphere, and hydrosphere [14–18].
Water pollution is a common phenomenon of both developed and developing countries where untreated domestic and industrial wastes are dumped directly into water bodies [19–21]. However, during lockdown period, due to the complete shutdown of industries, socio-cultural activities, tourism and all non-essential works and restrictions imposed on the transportation systems, a huge reduction in the greenhouse gas emissions and discharge of domestic, industrial, and other pollutants into the environment have been observed globally. In this regard, water quality improvements have been studied and documented by various researchers from different countries [22–26]. Various parameters were analysed such as pH, DO, BOD, TDS, FC, metal ion concentration, level of inorganic and organic pollutants, plastic pollution, colour, odour, transparency, turbidity, and effect of aquatic life. Majority of the studies reported positive impression of lockdown on physical, chemical, and biological health of hydrosphere.
All these studies encouraged us to design the present review article where we aim to summarize the available scientific literature and analyse the primary impacts of COVID-19 lockdown on the Indian riverine system. We have analysed essential parameters (where data available) for six different rivers of the India and compared the trends before and during the lockdown period. Another motive of the article is to interpret learnings from the lockdown and recommend certain modifications in the existing river revival schemes. For this, we have first reviewed government’s current water pollution control and river revival schemes and their limitations. Further highlights are directed towards the probable future plans and actions that can be implemented to achieve fruitful outcomes in managing the water resources. Although a few literature reviews are available with similar aims to study effect of pandemic on natural resources on a global scale [27–30], we on the other hand have managed to diagnose and highlight the effects in heavily populated territories, where there is a lack of advanced wastewater treatment plants and availability of adequate quality water is a challenging and urgent need. We endorse that such countries must prioritize implementation of effective wastewater treatment schemes in their existing water policies.
1.1. Indian Riverine System: An Overview
India accounts for nearly 4% of the world’s water resources, including various forms of surface water [31]. Among all, rivers hold crucial significance in the country and are used for various purposes such as drinking, irrigation of crops, generation of electricity and many more [32]. The Indian rivers are divided into Himalayan and Peninsular rivers on the basis of their origin. Ganga, Indus, and Brahmaputra riverine systems form a large river basin constituting the Himalayan rivers and flows through the Northern plains of India. Mahanadi, Godavari, Krishna, Cauvery are the major rivers flowing across Peninsular India and are characterised by their seasonal flow. These rivers and their various tributaries comprise India’s river system [33]. Various important civilizations and cities like Delhi, Varanasi and Ahmedabad are situated on the banks of the river. Thus, rivers have an enormously important role on the economy and lives of the people of India. Nevertheless, the overexploitation and dumping of the largely untreated industrial, municipal and domestic effluents into these water bodies results in the water pollution which ultimately mutating our precious resources into a trash [34]. The factors like population outburst, deforestation, technological advancements, unplanned urbanization, agricultural developments, and industrial upliftment have also contributed immensely towards the increasing water pollution. A wide range of chemicals, pathogens and other toxic substances have been found in the waterbodies which accounts for the alterations in the physical, chemical, and biological characteristics of water causing harmful effects on human and aquatic life [35–37].
2. Major Pollutants in Indian Rivers and Their Adverse Effects
Access to clean and safe water has always been a major concern for mankind. With the ever-growing population, expanding industries and expeditious urbanization, toxic and hazardous waste materials are continuously being dumped into the water bodies. Amongst all, heavy metals (like lead, zinc, copper, chromium, cadmium, nickel and arsenic) constitute a major class of contaminants as they have long-term persistence in water bodies and leads to severe environmental pollution [38]. Heavy metals have relatively high density and are toxic and hazardous for life if present above a permissible limit. Harmful substances and chemicals used in fertilizers, insecticides and pesticides may leach in water bodies [39, 40]. Flawed mining processes, discharge of industrial effluents containing metallic solutions, dumping of solid waste and chemicals such as metal-based biocides used in agricultural processes are some of the major causes of heavy metal accumulation in rivers. Industrial waste is another dominant class of contaminants that cause critical environmental deterioration. Industries related to dyeing, tanning, printing, battery manufacturing units, etc. largely operate alongside the rivers and discharge their effluent directly into the mainstream, thus polluting them heavily and affecting the water quality (Table S1 describes the current limit values imposed by the legislation on industrial discharges into rivers). Different types of chemicals which are responsible for the increased water pollution in Indian water bodies and their rate of production per year have been depicted in Fig. 1.
These chemicals once landed up into the water possess severely negative effects on the living beings and on the environment. Unfortunately, water pollution leads to more than 14,000 deaths per day, high rate of infant mortality, degradation in biodiversity, outbreak of chronic diseases and many more [41]. Table 1 summarizes the major pollutants found in the Indian rivers, their sources, and toxic effects on living species.
3. Government’s Schemes to Combat Water Pollution
Considering the continually deteriorating quality of our water resources and the adverse effects it poses on all forms of life, government of India launched various schemes and programs to combat water pollution. In this regard, the Water (Prevention and Control of Pollution) act of 1974 was the very first initiative of the government towards curbing water pollution. The purpose of this act was to prevent and control water pollution, as well as to maintain and restore the wholesomeness of water [53]. Central/state pollution control board (CPCB/SPCB) was established under this act as a regulating body for pollution control. The CPCB is the apex body in field of water quality management. The CPCB in collaboration with SPCBs has developed a concept of “designated best use”, based on which it has graded the water bodies on the basis of their pH, dissolved oxygen (DO), biological oxygen demand (BOD), conductivity, free ammonia and total coliform matter. This classification or gradation of water bodies not only assists water quality managers and planners in setting water quality targets but also in identifying needs and priorities for water quality restoration programs for India’s various water bodies. Many programs have been launched by the Government of India to clean the rivers. The first such plan was the Ganga Action Plan (GAP). The ambitious GAP was launched on January 14th, 1986, to clean the Ganga river. According to ministry of environment and forest, 6788.78 crore Indian currency was released by Prime minister late Shri Rajiv Gandhi to clean Ganga [54]. Nevertheless, only 39% of its primary target of sewage treatment was met as indicated in an audit report by the comptroller and auditor general (CAG). The complete top-down bureaucratic exercise and lack of data on water usage and wastewater generation were the most important reasons for failure of GAP [55].
After the failure of GAP, the government in 2009 took a more comprehensive step. A basin-wide and multi-sectoral approach was taken, and National Ganga River Basin Authority (NGRBA) was constituted. The NGRBA is a planning, financing, monitoring and coordinating body of the centre and state government whose aim is to ensure effective pollution abetment and conservation of national rivers. The NGRBA received USD 1 billion loan sanctioned by the world bank in 2011. This body was dissolved in 2016 and was renamed as National Council for Rejuvenation, Protection and Management of River Ganga [56]. The parliamentary committee on Environment and Forests states that the reason for the failure of NGRBA were that the social aspects of pollution in the rivers were ignored and their catchment areas were encroached upon and diverted for construction and development activities [57].
After the dissolution of NGRBA, a new mission called “Namami Gange” was launched by the government of India with a budget of more than $3 billion [58]. The major objective of this project was to improve the quality of Ganges with continuous and unpolluted flow while maintaining its ecological and geological integrity. The project programmes were based on recommendations of Ganga River Basin Management Plan (GRBMP) and the main activities included were construction of bigger sewage treatment plants with increased capacity, riverfront development programmes, biodiversity conservation and afforestation along river banks, public awareness and industrial effluent monitoring [56]. The government has also implemented National River Conservation Plan (NRCP) for abetment of pollution in identified stretches of various rivers. The states have also prepared action plan for sewage management and restoration of river quality in aquatic sources [59]. The goal of the NRCP is to assess the water quality of the state’s rivers, that are the major water sources, through the implementation of pollution reduction projects. The highlights of NRCP include 77 towns and 34 rivers in 16 states. The sanctioned cost of detailed project report was Rs. 5870.54 crores. A fund of Rs. 2510.63 crores have been sanctioned by the government of India whereas the expenditure has been 3339.96 crores. The total pollution load tackled has been estimated as 2520.43 MLD [60]. On the similar note, various other plans were launched to rejuvenate major rivers of the country. For instance, the Yamuna Action Plan was launched in 1993, with successive phase II in 2001, was aimed at rejuvenating river Yamuna [61]. Strengths, achievements and weaknesses of different government schemes to clean major rivers of India have been documented in table 2. Apart from these major undertakings by government, the CPCB has adopted various methodologies to curb water pollution (Fig. S1).
Thus, the government is taking numerous steps towards cleaning national rivers (Fig. 2), however despite these efforts and investing huge amount of budget, the quality of our water resources is still unacceptable. The CAG report of 2017 stated that the ‘Namami Gange’ mission does not have a river basin management plan even after NGBRA notifications. The coliform level in Ganga was found to be 3343 times higher than prescribed limit of 2016–17. Mercury metal is still being under-reported [56]. Disregarding the guidelines, people are still bathing and washing in rivers, idols are still being immersed, no proper cremation ghats are present across the rivers and untreated water is still being discharged into water bodies. According to WHO report of 1992, only 209 towns out of 3119 towns have partial sewage treatment facility whereas only 8 have full water treatment facility [53].
A new water policy and action plan has been prepared which suggests new policies that India should adopt to curb water crisis and pollution. The action programme of the plan states that community partnership and privatization, change in institutional structure, watershed project implementation, legal framework changes, financial assistance and modernization will help in outnumbering the shortcomings of previous programmes.
4. Wastewater Remediation Technologies
Besides Government’s water policies and schemes, many wastewater remediation technologies have also been developed and applied to deal with a variety of contaminants present in the water bodies. These technologies include various physical, chemical, and biological methods for wastewater remediation where a variety of materials have been used (Fig. S2) [62–73]. Further, various thermal and electro-chemical technologies are available that are used to treat saline wastewater [74–76]. Among all, adsorption is one of the best available technologies as it is convenient, has broad applicability, high efficiency, good selectivity, and cost effectiveness [77–81]. On this perspective, our research group is working to develop various efficient and reusable materials as adsorbents to selectively remove contaminants [82–88] and as catalysts that have remarkable efficiency for degrading toxic water pollutants [89–91]. Membrane processing, ion exchange, electrochemical precipitation, photo-chemical treatment, solvent extraction, adsorption and chemical- and biological-degradation are some of the other most employed technologies for this purpose [92–103]. However, majority of these techniques work effectively under certain operational conditions and can be futile in other circumstances. Table S2 summarizes merits and demerits of some of the mentioned techniques [63].
5. Methodology
This study was conducted by reviewing published literatures including research articles, reports from CPCB, SPCB and other government and non-government organizations, case studies, scientific opinions, and websites. Literature was searched by using different electronic means majorly Google Scholar, Research Gate, Science Direct and PubMed. The following terms were used while searching: ‘COVID-19 pandemic’, ‘lockdown’, ‘water’, ‘positive impact’, ‘environment’, ‘Indian rivers’, ‘water quality’, ‘aquatic life’, etc. Further we restricted our search to articles published in English language.
6. COVID-19 Lockdown and Improvement in Water Quality
A significant improvement has been seen in the quality of water within 10 days from imposement of the lockdown, which the various schemes of the government with crores of rupees pumped in, were unable to do for past few years. Referring to Fig. 1, it is clear from the trends of the graph that the amount of chemical production increased up-till 2019 but the lockdown imposed in view of COVID-19 pandemic dented the production of these chemicals, thus reducing the pollutants and hence the pollution in Indian rivers. Moreover, lockdown offered an opportunity to assess the water quality of some of the major rivers in India and compare it with pre-lockdown period [104]. Some of the rivers that improved during the lockdown period are discussed below.
6.1. River Ganga
The river Ganga, being one of the largest rivers on the Earth, is known to be the lifeline of millions of Indians. The national river flows over 29 cities, 97 towns and thousands of villages and thereby is severely polluted with industrial effluents and domestic sewages (Fig. S3). The nationwide lockdown appeared to be a gift to Ganga as there was an improvement seen in the quality of water within 10 days which the various schemes of the government with crores of rupees pumped in, were unable to do for past few years. Since the river was extensively polluted, COVID-19 lockdown served as an opportunity for CPCB and SPCBs to study the water quality of the river system before and during the lockdown period [105]. It is reported that water collected from 42 out of 65 monitored locations (64.6%) before lockdown and 25 out of 54 monitored locations (46.3%) during lockdown is categorized well within the desirable limits of primary water quality criteria for outdoor bathing. As per the report of Uttarakhand pollution control board, the Ganga water at Haridwar and Rishikesh was investigated ‘fit for drinking’ (Class A) giving a positive sign towards restoration of the river as the levels of DO, BOD and TC were within prescribed water quality criteria. Following this, the water quality observed between Haridwar, and Kanpur was found fit for outdoor bathing (Class B). A huge withdrawal of water was avoided since there was a complete halt on the water-intensive agriculture. Excessive rainfall during the lockdown period further improved the river flow leading to dilution of pollutants in the river. This resulted in an increase in the concentration of DO (above 5 mg L−1) at all the locations [105]. Overall moderate improvement in water quality of river Ganga was noticed with respect to the parameters i.e., DO, BOD and FC.
The higher rainfall also attributed to the increase in the turbidity and suspended solids in the river after the lockdown. The assessment of BOD of Ganga River before and during the lockdown makes it evident that there was a major decrease in BOD during the lockdown period at most of the stations. At the same time, a marginal decrease in chemical oxygen demand (COD) values have been noted due to complete restrictions on industrial activities. The lockdown also ensured the reduction in nitrate concentration and the values of ammoniacal nitrogen were also seen less than the prescribed criteria of 1.2 mg L−1 limit along with an improvement in bacterial quality of the river [105].
According to the of data of CPCB, out of 36 monitoring stations, the water quality at 27 points was found suitable for bathing (Class B) and 9 points suitable for propagation of wildlife and fisheries (Class C). The data also shows an increase in DO values of the river at most of the locations. Overall analysis on river Ganga before and during lockdown period is depicted in Fig. S4.
6.2. River Yamuna
Yamuna, the largest tributary of the river Ganga is known to be one of the most polluted rivers in the world. The 2% of Yamuna’s total length flows through National Capital Territory (NCT) of Delhi and receives 79% of its total pollution in this stretch of about 48 km making it the worst affected stretch of the entire river (Fig. S5). A study was conducted by Patel et al. to ascertain the impact of restricted anthropogenic activities on the water quality and a significant improvement in the water quality index (WQI) was recorded out of 9 monitoring stations [106]. A notable reduction in the concentration of polluting parameters, despite not receiving a substantial amount of rainfall, was also observed during the lockdown phase between 6th April to 14th April 2020 when compared to the pre-lockdown phase [106]. Whereas in some areas of NCT, the Yamuna water quality did not meet the prescribed limit of WQI values (except Palla and Surghat), even after 3 weeks of complete lockdown which highlights the concern over the deterioration in the water quality of Yamuna. The mean concentrations of BOD and COD (considering all monitoring stations) had changed by −42.83% (net reduction of 11.82 mg L−1) and −39.25% (net reduction of 32.06 mg L−1), respectively when compared with the previous year’s reduction amounts of 19.78% and 10.45%, respectively [106]. Despite all this, the water quality parameters in some monitoring stations like Khajori Paltoon did not even meet the Class B and Class C standards.
The lockdown has proven to be boon for the river and a finding by Delhi Pollution Control Committee (DPCC) showed that the river Yamuna in Delhi has cleaned by around 33%. The analysis of monitoring stations at Delhi revealed that:
Four critical parameters during pre-lockdown period were pH (7.2–8.7), DO (17.1mg/L), BOD (7.9–78 mg/L) and FC (1300–920000 MPN/100mL) at the 05 monitored locations while during lockdown these parameters were found to be pH (7.1–7.8), DO (1.2–8.3 mg/L) and BOD (2–6.1 mg/L).
Before lockdown, BOD at all monitored locations was not conforming to the limits described for primary water quality for outdoor bathing while during lockdown BOD at 1 monitoring station was complying within the limits.
Overall decreasing trend was noted for DO (51.46%) at 01 location and BOD (74.70% – 90.20%) at 03 monitoring locations.
6.3. River Godavari
Godavari is the second longest river in India which traverses via Telangana, Andhra Pradesh, and Chhattisgarh (Fig. S6). CPCB in association with Maharashtra Pollution Control Board (MPCB), Telangana State Pollution Control Board (TSPCB), Andhra Pradesh Pollution Control Board (APPCB) monitored the water quality to access the impact of lockdown on the river water quality. It was revealed that 29 out of 37 monitoring locations were in accordance with the water quality criteria for outdoor bathing [104]. A maximum reduction in BOD levels from 6.8 to 6.2 mg L−1 and FC levels from 70 to 47 MPN/100mL were seen at Tapovan. An increasing trend in the levels of DO at 19 locations, BOD at 5 locations and FC at 5 locations were also observed.
Overall assessment of the data obtained from different SPCBs revealed that:
Maharashtra: It was observed that DO was increased at 9 locations (1.5% – 61.3%), decreased at 3 locations (1.5–3.1%) while 2 locations showed no variation. Similarly, BOD (7.7–27.3 %) and FC (28.6 %) was increased at 3 and 1 locations, respectively. While decreasing trend in BOD (5.9–29.5 %) and FC (15–45.5 %) was recorded at 10 and 4 locations, respectively.
Telangana: It was observed that DO was increased at 9 locations (4.2–46.3%), decreased at 3 locations (1.4–28.6%) while 4 locations showed no variation. Similarly, BOD (14.3–33.3%) and FC (46.7–100%) was increased at 2 and 3 locations, respectively. While decreasing trend in BOD (3.3–30%) was recorded at 5 locations.
Andhra Pradesh: It was observed that DO was increased at 1 location (1.5%), decreased at 5 locations (1.5–26.2%) while 1 location showed no variation in DO. Similarly, BOD (5.6–57.1%) and FC (33.3%) was increased at 3 and 1 locations, respectively. While decreasing trend in BOD (13.3–40.9%) and FC (26.7–63.6%) was recorded at 4 and 5 locations, respectively.
Thus, when compared with pre-lockdown period, it was evident that lockdown emerged as a tool for cleaning the river [104].
6.4. River Gomti
River Gomti, a tributary of river Ganga, enters Lucknow after a journey of 190 km which flows in the middle of city and is employed for drinking and other domestic purposes at many locations (Fig. S7). A study was conducted by Khan et al. to evaluate the impact of COVID-19 lockdown on the heavy metal pollution status on the river Gomti at Lucknow city [107]. 30 samples from well-mixed segments (three at each sampling station) were collected from the river, across a total stretch of nearly 61 km in June 2020 to analyse the heavy metal levels within the water samples. The assessment of pollution levels and influence of heavy metals in water quality is classified using an index called heavy metal pollution indices (HPI). A considerable improvement in HPI was witnessed at all sites, with an overall average improvement of 19.15% in June 2020 when compared with pre-lockdown period signifying the impact of closure of industrial enterprises on the river water. The average concentration of As, Cd, Pb, Mn, and Cr metal at all sites showed a reduction of approximately 29%, 15.13%, 11.21%, 9.62%, and 16.37%, respectively which signifies the effectiveness of control measures (Fig. 3) [107].
The maximum improvement in the values of HPI was observed at site S1 (Chandrika Devi) with a drastic reduction of 32.2% due to the halt in agricultural activities. At the same time a decrease of 25.28%, 14.46, and 16.78% in the HPI values was observed at sites S2 (IIM Road), S3 (Harding Bridge), and S4 (Arti Sthal), respectively. Stations S8 (Dilkusha Bridge), S9 (Shahid Path) and S10 (Bharwara STP Discharge point-Gomti Confluence) situated at downstream locations also showed a notable improvement of ~21.2%, ~32%, and ~19.2 in individual HPI values, confirming the positive impact of the COVID-19 lockdown (Fig. S8) [107].
6.5. River Damodar
Damodar, a river of total length 563 Km, flows across the states of Jharkhand and West Bengal (Fig. S9). There are many industries established in both sides of the river which highlights the importance to evaluate the changes in the water quality during the lockdown period. A study was conducted by Chakraborty et al. in which water samples from 11 discharge sites of industries were collected before (December 2019) and during the lockdown period (July 2020) [108]. The significant change in the pH level of the river from 7.04–8.21 before lockdown to 6.12–7.72 was observed during the lockdown period which is directly related to the lesser disposal of effluents from the industries. Lower mixing of waste materials in the river resulted in the decrease in the TDS from 665.6 to 806.4 mg L−1 in pre-lockdown period to 480 to 563.2 mg L−1 during lockdown period [108]. Since TDS and EC are linked to each other, decrease in TDS decreases the EC which ranged from 1040 to 1260 μS cm−1 in pre-lockdown period and from 750 to 880 μS cm−1 during lockdown period which was lower than the standard limit according to WHO (2011).
The mean cation concentration of major cations (Ca2+, Na+, Mg2+, K+) were lowered down to their standard limit set by WHO (2011) as compared to their high concentration before the lockdown session. Similar results were seen in case of anions (SO42−, Cl−, NO3− and F−) which is allocated to the fact that no mixing of industrial toxic elements took place during the lockdown.
6.6. River Bhogavati
Bhogavati River, which originates near Osmanabad city of Maharashtra (Fig. S10), was studied at village Balinga in Kolhapur district of Maharashtra after three weeks of the enforcement of nationwide lockdown to compare the physico-chemical parameters of the water quality before and after the lockdown. It was found that the water quality parameters like pH, TDS, hardness, EC, etc. showed betterment in the quality of water during lockdown (Fig. 4) [109].
Table 3 compares various water quality parameters recorded before and during the lockdown period for major rivers in India.
7. Impact of COVID-19 Lockdown on Aquatic Species
A wide variety of aquatic species including plants, animals and other small living organisms can be found in the water bodies. Increasing pollution of surface water and climate change poses some serious and threatening effects on the survival of these aquatic plants and animals. The lockdown not only boosted the physical health of water resources, it also contributed largely towards improving the biological health. Studies have ascertained that due to positive changes in water quality, aquatic life is flourishing in the rivers, especially the number of fishes has found to be increased when compared with pre-lockdown period. A news article by ‘Timestravel’, Kolkata published that Gangetic dolphin were located at Kolkata ghats after a good 30 years [117]. Moreover, a report published by ‘ActionAid Association’ states that “there has been increase in aquatic species in Mahanadi, Narmada, Ganga, Yamuna and Nagavali while there was large majority reported increase of aquatic life in Krishna (75%), Kaveri (70%), Gandak (75%), Godavari (80%) and Gomati (78%)” (Fig. 5) [118].
8. Analysis and Interpretation
8.1. Potential Reasons for Improvement in Water Quality
8.1.1. High rainfall during the period
The surplus rainfall during the lockdown was the result of simultaneous occurrence of higher number of western disturbances, which improved the self-cleansing properties of the rivers. India Meteorological Department, New Delhi observed that the Ganga basin experienced 60% increase in rainfall than normal from March 1 to May 6, 2020, leading to the dilution of pollutants in the river [105].
8.1.2. Reduction in the discharge of untreated water into natural sources
The COVID-19 lockdown ensured the reduction in discharge of untreated industrial wastewater from the tanneries to the rivers which majorly destroys the quality of the rivers. When these effluents get mixed with the domestic sewages, they badly affect the self-cleansing properties of the rivers. It was analysed that there was a total reduction of 1300 to 1340 MLD of toxic industrial effluents during the period [105].
8.1.3. Halt on activities such as tourism, bathing and cloth washing
Since there was complete restriction on activities such as tourism, fairs, bathing and washing clothes, which usually has a severe impact on the quality of river, the rivers did not experience any problems related to solid wastes and littering by the visitors [105].
8.1.4. Decline in electricity demand
According to the Power System Operation Corporation, in India, the daily demand for electricity got lowered by 32.2% to 1.91 billion units (kWh) on account of mandated nationwide lockdown which impacted the hydropower production during the period. This allowed more water to flow into the rivers and diluting various pollutants coming into the rivers [105].
8.2. Interpretation and Key Findings
In this work, we attempted to recognize the effect of restrictions imposed during COVID-19 lockdown on Indian river water quality. We collected and compiled research data from various published literature for six major rivers of India, namely Ganga, Yamuna, Godavari, Gomti, Damodar and Bhagovati to evaluate impact of lockdown on water quality. This investigation of water quality parameters for different rivers will help researchers to understand key steps that should be incorporated in the existing water management system to achieve long term benefits. Some of the key findings of the work are:
During lockdown, discharge of domestic and industrial effluents such as heavy metals, plastics, wastewater, crude oil, etc. have been reduced or stopped largely, therefore, decrease in pollution level was seen. Due to which not only chemical health but physical and biological health of rivers was improved.
Physical: Major improvements were seen in terms of cleanness, colour, transparency, and odour of water.
Chemical: Studies revealed that there has been significant improvement in water quality in terms of DO, BOD, COD, FC, TDS, pH, and other parameters. Moreover, the concentration of heavy metal pollutants has been reduced.
Biological: We analysed that there have been considerable changes in aquatic life too. It has been observed that the presence of aquatic species especially fishes have increased due to decrease in water pollution. There has been rise in aquatic species in various rivers including Ganga, Yamuna, Godavari, and Gomati. Even the Gangetic dolphin could be located at Kolkata ghats after a good 30 years.
Few studies also reported the increase in the presence of migratory birds around water bodies. 100% increase was seen around river Ganga and Yamuna while 80% was observed around Gomati River.
Reduction in the discharge of untreated water, decrease in human interferences, halt on activities such as tourism, bathing and cloth washing, decline in electricity demand and high rainfall during the period due to improved climatic conditions are described as potential reasons for improvement in water quality.
It is a matter of concern that how much pre-treatment is required for effluents prior to discharging it into rivers. Government needs to ensure that no effluent could enter river stream without proper treatment. Simply investing high budget projects will not help in cleaning rivers. Rather it requires strict punishments against industries discharging untreated waste into the water.
The findings indicates that nature has self-capacity of healing, cleansing, and maintaining its resources until human interferences are minimal.
With the resumption of industrial activities, tourism and other human interventions, the pollutants will eventually reappear in the water bodies therefore, it is essential to learn lessons from nature and inculcate them in future strategies on the priority basis.
9. Recommendations and Future Directions
India is presently undergoing a decrease in freshwater resources. Scarcity of water is an issue in many parts of the country. If the country’s water use efficiency does not improve, it may face drought conditions within the next couple of decades. Therefore, water management in India has been a concern whose amplitude has grown exponentially over the last 50 years attributed to a myriad of factors. Major river water management challenges in India can be broadly classified as a) water accessibility, variance and increasing withdrawals b) the ecosystem and quality c) project development d) water-sharing conflicts e) water oversight and organizations and f) challenges induced by urbanization and climate change [119]. To overcome these challenges, there is an urgent need for the modifications in water-related guidelines, strategies, and regulatory frameworks.
COVID-19 lockdown showed us that how the shutting down of industrial units, decrease in discharge of untreated industrial and municipal waste and halt on human activities (like tourism, bathing, cloth washing, etc.) in water bodies has led to significant improvements in river water quality and facilitated flourishing of new lives in polluted rivers. However, there is a considerable uncertainty about how long these improvements will sustain after the complete upliftment of restrictions which were imposed during the lockdown period. Most likely, with the resumption of industrial activities, tourism and other human interventions, the pollutants will eventually reappear in the water bodies. In this scenario, we strongly believe that the teachings from the lockdown will surely help in the better management of our resources, and these should be reflected in the future plans and models for the rejuvenation of water systems. Therefore, in this section, we have tried to highlight gaps in the existing water management plans and recognize the various key factors that should be considered in future strategies for better management. In our view, future strategies should focus on the following key areas:
Appropriate measures and policies must be adopted by CPCB to ensure adequate wastewater treatment. Before the discharge of sewage and different effluents into the water bodies, they must be treated and bring to the prescribed limits.
Emphasis should be given to provide affordable sanitation in urban areas to reduce introduction of human waste in the water bodies. Besides, awareness drives should be conducted among slum communities which will help in improving waste management, increasing health awareness, and improving sanitation facilities to reduce contamination of water bodies.
Adaptation of fully integrated river basin planning techniques over isolated wastewater treatment methods (one treatment plant per municipality) would prove to be more sustainable and resilient approach. Integrated approaches would allow for more effective expenditures by developing effluent regulations based on the specific circumstances of distinct water bodies.
From an Indian perspective, the integrated water resource management (IWRM) strategy is extremely relevant and beneficial. This plan is divided into three categories (water, land and livelihood management) and offers particular recommendations based on the vulnerabilities and livelihood opportunities in specific geographical locations. It also takes into account different geomorphological, hydrological, pedological, ecological, and sociocultural features.
Proper land management and water conservation policies should be implemented which will help in sustainably managing the fresh water resources and water table. This will help in dilution of pollutants in water bodies.
Green infrastructure can become a major opportunity as it offers a solution to many water woes. Vegetated rooftops, roadside planting, absorbent gardens and other such measures can cut down the pollutants reaching to rivers and lakes and will help in increasing the quality of rivers. Protection and creation of forest patches in catchment areas will also benefit in reducing pollution levels in the rivers.
To verify noncompliance with treatment of wastewater and discharge, strict quality regulation and enforcement are required. The SPCBs are not well equipped to handle it and hence a new system must be developed.
Strict implementation of rotatory lockdown must be executed near riversides. This would definitely improve water quality.
Sufficient financing is also required to make the necessary changes to the current system. Once funding is secured, resources should be directed toward repairing existing sewage treatment plants. The emphasis should be on ensuring that the treatment load meets the needs of the area, with room for the inevitable growth in population. Funding must be invested in the purchase of generators, which will allow treatment plants to operate during frequent power outages. To keep treatment malfunctions to a minimum, a task force of qualified scientists and engineers must collaborate to train more people on how to run and keep the current systems. This is a multifaceted problem with no simple solution; however, strategic action must be a top priority for the Government of India in aimed at improving the lives of the people who live along the river and the river ecology [120].
10. Opportunities for Future Research
Real-time monitoring of pollutant concentration in water and availability of proper waste disposal and treatment technologies also play a key role in restoration of water quality. Therefore, current state-of-art is to develop novel, cost-effective and efficient methods for wastewater remediation. Although a lot of treatment processes have been reported in the literature including adsorption, extraction, membrane filtration, ion exchange, chemical precipitation, bioremediation, thermal and electrochemical techniques, but still there are some demerits associated with them such as cost, efficiency, and large-scale implementation. In our view, these barriers can be overcome by integrating two or more techniques together in a synergistic means to produce better results. Therefore, more such hyphenated processes should be developed in near future and scaled to pilot level. Besides, development in sensitive and quick detection techniques for real-time pollution monitoring is much desirable. Smart sensors that are flexible, portable and are capable for simultaneous detection of different analytes could be an area to worth exploring in the near future.
11. Conclusions
In this article, we presented a snapshot of the primary impacts of COVID-19 lockdown on the water quality of densely populated territory, India. Data reviewed in the article suggest that there is overall marginal enhancement in water quality of river Yamuna and Godavari with respect to primary water quality criteria for outdoor. River Ganga showed improvements in DO and decline in BOD at few monitoring stations. The critical parameters for river Gomati were found to be in the range of pH (8.76), DO (6.35 mg/L) and BOD (3.50 mg/L) at different locations. Overall majority of the rivers showed improvements in DO, BOD, FC, and pH. The key factors leading to these improvements have been analysed in the review. Reduction in discharge of domestic and industrial effluents, decline in the consumption of electricity and improved climate conditions including changes in the rainfall patterns are major factors responsible for the enhancement of water quality. Based on the learnings from lockdown, we have presented various recommendations. In our view, the foremost priority must be to ensure that no industrial discharge could enter the river without proper treatment. Industries operating along-side rivers should be shut immediately and strict actions must be taken against polluting industries. Emphasis should also be given to provide affordable sanitation and green infrastructure. Protection and creation of forest patches in catchment areas will benefit in reducing pollution levels in the rivers. Besides, adaptation of IWRM strategy that takes into account different geomorphological and sociocultural features would be very beneficial. We also propose strict implementation of rotatory lockdown near riversides which would definitely improve the water quality. Besides, advanced wastewater and industrial effluent treatment plants and techniques should be introduced. We believe that the suggestions and future directions discussed in this review will help in revising the present strategies and will contribute towards the permanent restoration of water resources.
Supplementary Information
Notes
Conflict of Interest
The authors declare that they have no conflict of interest.
Author Contributions
G.A. (Senior Researcher-Lecturer) Conceptualization, original draft preparation, T.S. and K.K.T. (Undergraduate students) Original draft preparation, P.P. and C.G. (Assistant Professors) Organization, reviewing and editing and R.K.S. (Senior Professor) Reviewing and editing.
Funding sources
This work did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.