Water Quality and Water Pollution in Time of COVID-19: Positive and Negative Repercussions
Abstract
:1. Introduction
2. Materials and Methods
3. Results and Discussions
3.1. Virus COVID-19 in Water—General Information
3.2. Reviews and Analyses of the COVID-19 Effects on Different Water Bodies All over the World
3.3. Analyses of the COVID-19 Effects on Different Water Bodies in India
3.4. Analyses of COVID-19 Effects on Different Water Bodies in South Africa
3.5. Analyses of COVID-19 Effects on the Water Bodies of Lombardy (Northern Italy) and on Meriç—Ergene River Basin (Turkey)
3.6. Analyses of COVID-19 Effects on Different Water Bodies in South America, Bangladesh and China
3.7. Analyses of COVID-19 Effects on Different Water Bodies in Southeast and South Asia
4. Conclusions
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- The SARS-CoV-2 monitoring in the wastewaters is a useful mechanism for the prompt exposure of collective infections at the pandemic debut. This valuable tool can help authorities implement the most adequate COVID-19 mitigation policies, and, in this respect, no discrepancy between scientists has been found. While SARS-CoV-2 RNA can be identified in the sewage water using RT-qPCR testing, no official conduct code for primal SARS-CoV-2 identification and quantification in wastewaters has been drawn up yet, which we acknowledge to be a priority.
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- During the COVID-19 lockdown, many surface and ground-/subsurface water bodies all over the world saw lower pollution levels as a result of a significant decrease in domestic and industrial wastewater discharge and agricultural activities, boat/vessel traffic and tourist activities. This positive impact has been emphasized by all researchers who analysed the environmental benefits linked to the COVID-19 lockdown.Succinctly, the negative impacts are along these lines:
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- Following the COVID-19 pandemic outbreak, the SARS-CoV-2 virus could be detected in wastewater, but it is unlikely to be transmitted through contact with this type of water, due to its sensitivity to disinfectants, solvents, detergents and treatment methods and, in general, due to its poor stability when exposed to the environmental conditions of wastewater. Even if genetic fragments (RNA) can be detected in wastewater, the virus is not viable once its envelope is damaged. On the other hand, untreated wastewaters could be the agent for a high contamination risk. Due to the fact that a scientific uncertainty has been identified, we strongly recommend further analyses of SARS-CoV-2 viability in sewage waters.
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- Many reports asserted the significant harm along the shorelines caused by the disposal of sanitary consumables (masks, gloves, contaminated wipes, protective suits, safety shoes, etc.) arising from the medical activities or personal protection. The different water animals can swallow the masks or get tangled in their elastic cords.
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- COVID-19 diagnostic laboratories pollute all environmental elements, including water, with different plastic materials and chemicals substances. In addition, it is important to mention the methacrylate from plastic screens and other physical spacing equipment, which finally may also reach water bodies.
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- The medications used to cure COVID-19 consist of persistent, bioaccumulative and dangerous substances to aquatic organisms, and they are considered emerging pollutants. Sewage water treatment technology cannot eliminate these remedies, and they will be discharged into inland water bodies. In this sense, new water treatment technologies should be developed by medical and technical scientists.
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- Chemical compounds such as triclosan, triclocarbon and acrylate copolymers in sanitizers already posed environmental issues.
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- Plastics and drugs in wastewaters, especially non-biodegradables, produced during the COVID-19 pandemic will persist for longer periods of time after pandemic end.
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- The asepsis of the roads led to the presence of residual Cl in treatment plant effluents, which contaminates water and jeopardises water organisms.
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- The new coronavirus increased biological pollution, especially in hospitals and SARS-CoV-2 mortuary wastewaters, and we consider this demands distinctive biological wastewater treatment methods.
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- Since the COVID-19 outbreak, municipal and medical waste production has increased globally and represents a considerable danger for population health and the environment, including water bodies; this co-occurred unfortunately with a decrease in waste recycling.
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Type of Article | Location of Water Quality COVID-19 Impact Analysis | Investigated Hydrosphere Component/ Water Type | Evaluated Parameters/ Pollutants of the Hydrosphere Component/ Water Type | Positive Effects | Negative Effects | Sources of Water Quality COVID-19 Impact Information |
---|---|---|---|---|---|---|
Review on COVID-19 environmental effects | Spain, Netherlands, Australia, USA, France, Italy, Turkey, Ecuador, and China | Wastewater | SARS-CoV-2 virus and its RNA | ✓ + SARS-CoV-2 exposure in wastewater | ✓ | Al Huraimel et al. 2020 [39] |
India, China | Wastewater | SARS-CoV-2 virus | ✓ | Bhowmick et al. 2020 | ||
[40] | ||||||
India | Surface water (river, lake); groundwater | Suspended particulate matter (SPM); heavy metals | ✓ | Casado-Aranda et al.2021 [25] | ||
Italy, Hong Kong, Canada, Germany, and Austria | Surface water; wastewater | SARS-CoV-2 virus; medical and hygienic waste | ✓+ SARS-CoV-2 exposure in wastewater | ✓ | Cheval et al. 2020 [4] | |
Asian countries, Italy | Surface water; wastewater | Chemical pollutants; plastic waste; and suspended solids | ✓ | ✓ | Espejo et al. 2020 [41] | |
India, Italy, and Saudi Arabia | Surface water (rivers); sea/ocean water | Dissolved oxygen (DO); biochemical oxygen demand (BOD); total coliforms (TC); pH; and aquatic life | ✓ | Khan et al. 2021 [30] | ||
China, India, and Spain | Surface water; sea/ocean water | Medical and plastic waste; dioxin | ✓ | Patricio Silva et al. 2021 [42] | ||
China, Iran | Surface water; wastewater | Chlorine (Cl); infectious and plastic waste; and chemical and biological pollution | ✓ | Poursadeqiyan et al. 2020 [43] | ||
China, India, Iran, USA | Wastewater | SARS-CoV-2 virus | ✓ | ✓ | Rahimi et al. 2021 [9] | |
India, Bangladesh, Italy, Malaysia, Thailand, Maldives, Indonesia, Australia, Sweden, Netherlands, USA, China | Surface water (rivers); sea/ocean water | Medical and plastic waste; chemical pollution; DO; and BOD | ✓ | ✓ | Rume and Islam 2020 [44] | |
India, France, Italy, USA, Spain, China | Surface water (rivers); sea/ocean water | Chemical pollution | ✓ | Rupani et al. 2020 [45] | ||
China, India, Iran, and USA | Sea/ocean water | Chemical pollution; plastic waste | ✓ | Sivaranjanee and Kumar 2021 [46] | ||
Italy, India | Surface water; sea/ocean water; wastewater; recreational activity and physical therapy pools | Chemical pollution; plastic waste; and SARS-CoV-2 virus | ✓ | ✓ | Usman and Ho 2021 [47] | |
India, China, Malaysia, and Morocco | Surface water (rivers and lakes); sea/ocean water; wastewater | Biodiversity; macroplastic and microplastic pollution; chlorophyll a (Chl-a); phyto-plankton; nitrogen; turbidity; pharmaceuticals and disinfectants; and SARS-CoV-2 virus | ✓ | ✓ | Yusoff et al. 2021 [48] | |
China, USA, Italy, Spain, Mexico, Ecuador, Australia, Bangladesh, India, Netherlands, and Sweden | Surface water; sea/ocean water; wastewater | Chemical pollution; plastic waste; and SARS-CoV-2 RNA | ✓ | ✓ | Zambrano-Monserrate et al. 2020 [49] | |
Specific area article | India | Surface water (rivers) | Physical, chemical (e.g., DO) and heavy elements; and TC | ✓ | Chakraborty et al. 2021 [26] | |
Surface water (rivers) | Chemical pollution; wildlife; bio-medical, hazardous and plastic waste | ✓ | ✓ | Debata et al. 2020 [50] | ||
Groundwater | Fluoride (F); nitrate (NO3); ionic loads; and bicarbonate | ✓ | Karunanidhi et al. 2021 [51] | |||
Surface water (lake) | Chemical parameters | ✓ | Kulk et al. 2021 [52] | |||
Surface water (rivers) | Chemical parameters (e.g., DO, BOD) | ✓ | Lokhandwala and Gautam 2020 [53] | |||
Surface water (lake); groundwater | Chemical parameters | ✓ | ✓ | Mukherjee et al. 2020 [54] | ||
Surface water (rivers and lakes) | Hardness; alkalinity; total dissolved solids (TDS); TC; and pH | ✓ | Nandan et al. 2021 [55] | |||
Surface water (river) | BOD; chemical oxygen demand (COD); SPM; turbidity; algal signatures; and fecal coliforms | ✓ | ✓ | Patel et al. 2020 [56] | ||
Groundwater | Physico-chemical parameters (pH; TDS; electrical conductivity (EC); NO3; F; heavy metals; As; Se); bacterial parameters (TC; fecal coliforms; and E. coli; fecal streptococci) | ✓ | Selvam et al. 2020 [57] | |||
Surface water (lake) | Chl-a; colored dissolved organic matter (CDOM); total suspended solids (TSS) | ✓ | Wagh et al. 2021 [58] | |||
Surface water (lake) | SPM | ✓ | Yunus et al. 2020 [24] | |||
South Africa | Surface water, ocean water | Antiretro-virals (ARVs); plastic and hygienic waste; and sanitizer chemicals | ✓ | Horn et al. 2020 [59] | ||
Surface water | Physico-chemical parameters | ✓ | Molekoa et al. 2021 [60] | |||
Italy | Surface water; sea water | Plastic and hygienic waste; microplastics | ✓ | Binda et al. 2021 [61] | ||
Turkey | Surface water (river) | Physico-chemical parameters; metal(loid)s | ✓ | Tocatlı and Varol 2021 [62] | ||
South America | Surface water; ocean water | Plastic, textile and hygienic waste; microplastics | ✓ | Ardusso et al. 2021 [63] | ||
Bangladesh | Surface water; ocean water | Plastic, textile and hygienic waste | ✓ | Islam et al. 2021 [64] | ||
China | Wastewater (pit latrines) | SARS-CoV-2 | ✓ | Liu et al. 2021 [65] | ||
Southeast Asia (Indonesia, Malaysia, Thailand, the Philippines, and Vietnam) | Surface water (rivers); sea/ocean water | TSS; DO; and plastic and medical waste | ✓ | ✓ | Praveena and Aris 2021 [66] | |
South Asia (Pakistan, India, and Bangladesh) | Sea/ocean water | Chl-a; turbidity; and nitrogen load | ✓ | Shafeeque et al. 2021 [67] |
Positive COVID-19 Impacts on Water Bodies/Systems/Types | Negative COVID-19 Impacts on Water Bodies/Systems/Types |
---|---|
SARS-CoV-2 monitoring in wastewaters—a useful mechanism in the promptly exposure of community infections | SARS-CoV-2 presence in wastewaters > high risk of untreated wastewaters |
Many surface and ground-/subsurface water bodies all over the world saw lower pollution levels caused by domestic and industrial wastewater discharge | Plastic, drugs/chemicals and biological pollution in wastewaters > lack of adequate elimination processes at wastewater treatment plants |
Greater amounts of municipal and medical waste (sanitary consumables, disposable supplies, etc.) that may pollute surface water bodies, shorelines and beaches, and lower waste recycling rates. |
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Manoiu, V.-M.; Kubiak-Wójcicka, K.; Craciun, A.-I.; Akman, Ç.; Akman, E. Water Quality and Water Pollution in Time of COVID-19: Positive and Negative Repercussions. Water 2022, 14, 1124. https://doi.org/10.3390/w14071124
Manoiu V-M, Kubiak-Wójcicka K, Craciun A-I, Akman Ç, Akman E. Water Quality and Water Pollution in Time of COVID-19: Positive and Negative Repercussions. Water. 2022; 14(7):1124. https://doi.org/10.3390/w14071124
Chicago/Turabian StyleManoiu, Valentina-Mariana, Katarzyna Kubiak-Wójcicka, Alexandru-Ioan Craciun, Çiğdem Akman, and Elvettin Akman. 2022. "Water Quality and Water Pollution in Time of COVID-19: Positive and Negative Repercussions" Water 14, no. 7: 1124. https://doi.org/10.3390/w14071124
APA StyleManoiu, V.-M., Kubiak-Wójcicka, K., Craciun, A.-I., Akman, Ç., & Akman, E. (2022). Water Quality and Water Pollution in Time of COVID-19: Positive and Negative Repercussions. Water, 14(7), 1124. https://doi.org/10.3390/w14071124