Abstract
The global outbreak of the COVID-19 pandemic has given rise to a significant health emergency to adverse impact on environment, and human society. The COVID-19 post-pandemic not only affects human beings but also creates pollution crisis in environment. The post-pandemic situation has shown a drastic change in nature due to biomedical waste load and other components. The inadequate segregation of untreated healthcare wastes, chemical disinfectants, and single-use plastics leads to contamination of the water, air, and agricultural fields. These materials allow the growth of disease-causing agents and transmission. Particularly, the COVID-19 outbreak has posed a severe environmental and health concern in many developing countries for infectious waste. In 2030, plastic enhances a transboundary menace to natural ecological communities and public health. This review provides a complete overview of the COVID-19 pandemic on environmental pollution and its anthropogenic impacts to public health and natural ecosystem considering short- and long-term scenarios. The review thoroughly assesses the impacts on ecosystem in the terrestrial, marine, and atmospheric realms. The information from this evaluation can be utilized to assess the short-term and long-term solutions for minimizing any unfavorable effects. Especially, this topic focuses on the excessive use of plastics and their products, subsequently with the involvement of the scientific community, and policymakers will develop the proper management plan for the upcoming generation. This article also provides crucial research gap knowledge to boost national disaster preparedness in future perspectives.
Similar content being viewed by others
Introduction
Plastic is mostly used for packaging, equipment, and disposable and medical appliance due to its high strength and durability. Plastic has a significant role in the healthcare industry and public health security, as the COVID-19 outbreak has shown (Parashar and Hait 2021). The novel coronavirus creates an unprecedented and dramatic universal calamity; it is the 3rd zoonotic eruption of the twenty-first century. That disease was first reported in India in January 2020 in the state of Kerala. More than 4 crore people affected by SARS-CoV-2 infection in India up to the month of September 2022 and 5 lakhs of death cases were reported till now. The COVID-19 outbreak has given rise to a global health crisis with an adverse impact on biodiversity, as well as on the economy and human society (Tripathi et al. 2020). The lockdown period was declared on the 24th of March 2022 in India with 4 phases, i.e., 21 days, 19 days, 14 days, and another 14 days (Fig. 1a). Post-COVID-19 pandemic not only affects human beings but also creates various challenges on regulations and management practices of single-used plastic pollution crisis worldwide. Even though, air pollution and environmental noise reduction have been reported during the COVID-19 pandemic because people were confined at home and followed waste management strategies (Jena and Patnaik 2021). Assessment of the many crucial environmental effects of the COVID-19 pandemic has grown to be a high priority for academics and research personnel all around the world. It also noted during the lockdown period that our system can readjust to its pure or virtually pristine form. The lockdown has been shown to have numerous positive benefits, providing a doable corrective action for improving the standard of various natural resources. Consequently, typical production of single-use waste products (gowns, masks, PPE kits, hand sanitizers, and gloves) from both health amenities and households lately emerged to be a waste emergency to a drastic change in nature. Inappropriate management of households and medical waste may lead to serious damage to present flora and fauna and when it is directly discharged into the ambient environment. Untreated solid or liquid waste from both medical and household can create serious concern about environmental pollution (water and soil) and can induce severe health threat that ultimately causes infectious disease like TB, cholera, other respiratory and abdominal infection, AIDS, and hepatitis (Aggarwal and Kumar 2015). In India, about 0.34 kg of solid waste is created per capita on daily basis. Whereas, approximately 75% of biomedical waste does not recover, 40% of waste goes to landfills, and 32% leaks out of the collection system. The COVID-19 pandemic directs as consequence of a 40% increase in the global production of biomedical waste. Remarkably, 8% of biomedical waste was generated and that changed soil quality on dumping sites. According to WHO, nearly about 85% are non-hazardous wastes which exist in the open environment. The remaining 10% may be infectious or hazardous in nature, and 5% of toxic or chemical and radioactive waste may enter into the water, air, and soil bodies. It also noted that the COVID-19 pandemic wave generates 20% of biomedical waste on any given day in India (Fig. 1a). The global outbreak of COVID-19 increased healthcare waste production undesirably in our environment. In this critical situation of the pandemic, the number of quarantine policies has been encouraged like online shopping and home delivery for every public daily need which also eventually increases household wastes (Somani et al. 2020). Whereas, the disposal of general municipal wastes is not much dangerous as the biochemical wastes increase the level of pollutants in nature. The disposal of biochemical wastes needs proper treatment before being discarded as they can be potent elements to spread infections. Contact with hazardous chemicals and radioactive wastes can be responsible for carcinogenic health issues in human beings. A rapid increase of hospitalized patients in this pandemic situation has produced a huge amount of healthcare wastes (Kulkarni and Anantharama 2020). On the other hand, due to a lack of proper knowledge about infectious waste management practices, most of these wastes from hospitals and isolation centers are dumped in open places (Singh et al. 2020). Some of these wastes are directly discarded in the nearest water sources, although a sudden rise in waste due to pandemic situations is a big challenge for the local waste management authorities in every place. Dumping and burning of untreated biochemical and domestic wastes are the main reasons for pollution and infections in the locality. Heavy metals such as lead, cadmium, and mercury are one of the most dangerous elements of biochemical wastes. When they get absorbed by plants and enter the food chain, it results in deadly effects on lives. Thus, it becomes very necessary to study the harmful effect of environmental pollution and its anthropogenic impact on human beings after the pandemic situation. Therefore, awareness should be created among people and prepare us for every worse situation in the future days. The anthropogenic activities of untreated biomedical waste (BMW) have various sources like toxicity, infectious, and radioactivity. Various medical wastes are made up of single-use plastic materials and these untreated materials cause contamination and COVID-19 infection. The SARS-CoV-2 virus remains in single-used plastic and other materials for several time periods and up to several days (Nghiem et al. 2020). A huge number of viral tests and the admission of infected persons into hospitals or home isolation for their own safety led to a rise in the quantity of single-use plastic. Lockdowns, social exclusion, and prohibitions on public gatherings also rapidly increase the reliance on Internet purchasing, and packaging of frequently used plastics (Thakur 2021; Picheta 2020). Consequently, the amount of plastic garbage being treated is not keeping up with the daily rise in plastic product demand. Particularly in health centers, waste processing is very difficult, and not all single-used biomedical materials and packed products are managed or recycled. Subsequently, this inadequately handled biomedical plastic waste is released into the open ecosystem (Woodall et al. 2014). Several studies and research outputs find that the excess use of beauty products and pharmaceuticals contains antibacterial and fungicide molecules, and are progressively increased in the environment (Du et al. 2019). These agents are extremely toxic and create serious endocrine disruption and other neurological disorders. These substances adversely affect the aquatic flora and fauna (Capoor and Parida 2021a, b). Numerous works of research discovered that COVID-19 waste can cause a number of ailments and may have long-term effects on daily living. It might have a serious effect on species invasion, emergence of new illnesses, eventual demise of living things, and even the ability to endanger the whole environmental system.
While few existing studies are looking at the long-term detrimental effects of COVID-19 on the environment and other waste management practices, there are multiple investigations and articles detailing the beneficial consequences of COVID-19 on the environment. The COVID-19 immediate and long-term ramifications on the ecology, waste disposal, and health practices of human beings are covered in the current article. For upcoming initiatives and goal-specific policies, it is also crucial to assess the long-term harmful effects of COVID-19 on the ecosystem. All data analysis can also be utilized to evaluate immediate and long-term mitigation strategies against the potential negative effects of COVID-19.
Main sources’ effects on environmental pollution and anthropogenic contributions
COVID-19 waste: what is it?
Generally, biomedical waste known as infectious waste or medical waste is described as trash produced during the diagnosis, immunization, and treatment of animals or humans in research and clinical testing in hospitals as well as biological research facilities. The generated total amount of waste is 85% and the rest is hazardous waste. Some of the 10% of the waste is considered potentially dangerous waste, which includes radioactive, lethal, chemical, and sharps trash, like infectious waste (Prüss et al. 2014; Chand et al. 2020). Any trash product produced by the isolation, treatment, quarantine, and diagnosis of SARS-CoV-2-infected individuals is referred to as BMW during the COVID-19 epidemic. The COVID-19 patients who contaminated those wastes render contagious; otherwise, these are handled by the solid waste management rules from 2016. Between March 2020 and November 2021, the WHO analyzed about 87,000 tonnes of PPE, 140 million test kits (approximately 2600 tonnes of plastic), 731,000 l of chemical waste, and an additional 14,000 tonnes of vaccine-related waste that have been produced worldwide.
Immensity of the BMW problems worldwide
The World Health Organization (WHO) reported that a total of 24 countries have 58% facilities of proper management practices of BMW before COVID-19 (Capoor and Parida 2021a, b). About 10,000 tonnes of extra medical waste are produced around the world, as per the WHO report. In developing countries, COVID-19 has created several major problems in BWM management due to increases in hazardous waste. During the COVID-19 infection period, China produced 247 tonnes of BMW per day; at the same time, India, Bangladesh, and the USA generated BMW was ~ 101 metric tonnes, 2.5 million tonnes, and 206 tonnes per day respectively (Singh et al. 2020; Rahman et al. 2020; Dehal et al. 2022). According to National Green Tribunal, the capital of India increases daily by 11% of COVID-19 BMW than pre-COVID-19 period. However, during the pandemic period, BMW production increases 5 times within the healthcare system worldwide (WHO 2020a, b).
At the time of the COVID-19 outbreak worldwide, the frontline worker utilizes around 89 million masks, 1.59 million face shields, 30 million gowns, and 76 million gloves each month. According to the WHO, 40% of protective care was produced during the initial stages of the epidemic. From June to July 2020, this equipment steadily rose from 5.5 to 50.4 million (Haque et al. 2021). Due to the enormous demand for protective gear, China has offered 150 nations and 7 international organizations 1.73 billion protective garments and 17.9 billion masks through the month of October 2020 (Table 1) (https://www.ebmg.online/plastics). Regrettably, the epidemic causes a significant amount of microplastic garbage to be produced daily. The presence of plastic in freshwater, marine water, and soil habitats poses a significant threat to our ecosystem and public health aspects. In the pandemic period in India, about 7.3 lakh tonnes are hospital waste, 26,787 tonnes are test kits, 5 lakh tonnes are face masks, of which 4 lakh tonnes are medical masks, and the remaining 1 lakh tonnes are N95 and express delivery packaging plastics, which is equivalent to about 3 lakh tonnes of BMW. The details of such produced BMW are listed in Table 1.
The situation with plastic trash linked to COVID-19 epidemic
Population and the total number of confirmed COVID-19 cases data were collected from 30 districts of the state of Odisha, India (data source: https://statedashboard.odisha.gov.in/). Additionally, the baseline information about the total population in each district and the percentage of the urban population was collected (data source: https://www.populationu.com/in/odisha-population). This model has used a spatial variation of the pandemic in different countries. These crucial data are important to evaluate the post-COVID-19-related various waste generation in Odisha state, India (Table 2).
Medical waste estimation
In low- and high-income areas, 0.2 and 0.5 kg/day of hazardous biomedical waste are produced each day, respectively, according to World Health Organization (WHO). Odisha reflects a yearly biomedical waste growth rate of more than 7%, and by 2021, it is predicted that the state’s daily biomedical waste production might reach 6.65 metric tonnes (Das et al. 2020). The most BMWs were produced in different states like Andhra Pradesh, Gujarat, Haryana, Karnataka, Kerala, Madhya Pradesh, Maharashtra, Tamil Nadu, Uttar Pradesh, and West Bengal between May 2020 and March 2021 (Fig. 1b). Moreover, the Arunachal Pradesh, Chhattisgarh, Goa, Jharkhand, Manipur, Meghalaya, Mizoram, Nagaland, Sikkim, and Tripura are the states having with the lowest BMW generation (Fig. 1c). However, Delhi generates more than 2978 tons of BMW rather the other union territory regions’ combined condition (Fig. 2). The average waste created per individual bed and the numbers of infected individuals are directly related to the amount of medical waste produced in diverse locations. For example, in Odisha state, there are 9274 beds in 56 hospitals, 7251 beds in quarantine camps or COVID-19 centers, a total of 31 RT-PCR testing laboratories, all Community Health Center (CHC) and Primary Health Care (PHC) collection sites, and 36 TrueNAT testing labs responsible for the generation of COVID-19 waste materials (Fig. 3). Our current study assesses the BWM production, collection, and scientific management on a daily basis during the COVID-19 pandemic in 30 districts of Odisha state. Because of this, the predicted values for BMW in numerous cities in Odisha showed the yearly average value per day has climbed from 0.3 kg/bed/day in 2019 to 1.6 kg/bed/day in 2021 (Goswami et al. 2021). A significant partial correlation exists between the SARS-CoV-2-infected individuals and the average output of BMW in Odisha during the COVID-19 pandemic period. Khordha district of Odisha state is the place where the maximum BMWs are produced, and Deogharh is where 14.03 tons of single-use products is produced in daily basis (Fig. 4) (Table 3). As a result, when evaluating the medical waste, the earlier studies estimated BMW of 1.6 kg/bed/day during the COVID-19 period and was given more focus (Sangkham 2020; Saxena et al. 2021).
where Mw = medical waste (tons/day), Ncc = number of COVID-19 cases (infected persons), and Mwgr = medical waste generation rate, that is, 1.6 kg/bed/day.
Using the weblink (https://statedashboard.odisha.gov.in), you may view the number of confirmed COVID-19 cases throughout numerous districts in the Odisha area, as well as the infected individuals receiving medical treatment or home quarantine, along with the individuals who have passed away after contracting the COVID-19.
Short- and long-term impacts of the pandemic period on environment
Both positive and negative effects impacted the global environment and climate disruption caused by COVID-19. Several researchers confirmed that levels of air quality gases of NO2, CO, SO2, NOx, PM2.5, VOCs, and water quality index improved worldwide during the pandemic period (Yunus et al. 2020). Furthermore, due to movement restrictions of the people and slow social and economic activities, the quality of water has improved in several urban and rural areas, with improved air quality in different parts of India (Selvam et al. 2020). However, a huge amount of BMW generation shows negative impacts on biodiversity.
COVID-19 pandemic environmental benefits: a near-term reality
Reduction of air pollution and GHG emission
Unlike before COVID-19, air quality analysis decreased throughout the lockdown period. Industries, businesses, and transportation mechanisms also contributed to a sharp decline in air pollutants and other greenhouse gas (GHG) emissions during nationwide lockdowns. There has been a roughly 50% decrease in CO and N2O enhanced the O2 level by 16–48% in India because power plant operations have been partially shut down (Biswal et al. 2020; Selvam et al. 2020). Throughout the lockdown period, air pollutions fall down and were reported by the Central Pollution Control Board (CPCB) in various parts of the industrialized state of Gujarat, India. The concentration level of PM2.5 plummeted by 38–78%; subsequently, the PM10 level decreased in the range of 32–80% than before the lockdown, respectively (Lokhandwala and Gautam 2020). One of the key gases of NO2 emission has been reduced by 70% in the capital of India, which is emitted from the burning of fossil fuels (Ghosh 2020). The level of NO2, PM10, and PM2.5 was reduced by 46–50% during the nationwide lockdown in the entire Odisha (IEP 2020; Thiessen 2020; Mekonnen and Aragaw 2021). Correspondingly, 72% and 11% of key contributors in transport sectors are vehicles and aviation which emit GHG gases. According to IEA, 7% of CO2 emission has been reduced during the COVID-19 pandemic (Henriques 2020; IEA 2020).
Reduction of water pollution
In Odisha, water pollution is a common case, where industrial and domestic wastes are dumped into the sea and rivers. During the lockdown period, the export and import businesses have stopped and a sudden drop in sewage and industrial effluents caused reduction of the pollution load in rivers and marine water (Yunus et al.2020).
Reduction of noise pollution
Noise pollution adversely affects living organisms due to undesired human activities like machines, vehicles, and construction sites. Due to noise pollution, nearly about 360 million people are affected by hearing loss worldwide. During this pandemic, travel and vehicular restrictions have considerably changed the level of noise pollution in Delhi City of India around 50–60 dB, out of 100 dB (Gandhiok and Ibrar 2020; Somani et al. 2020).
The closure of numerous industrial and commercial operations that rely on fossil fuels resulted in a notable decrease in GHG emissions, VOCs, and other particulate matter. The bulk of global investigations has shown that the air, water, and noise quality significantly improved during the shutdown conditions. The worldwide lockdown had a huge influence on the energy supply, which resulted in lowering of GHG emissions and noticeable reductions in energy usages. The findings unequivocally demonstrated the long-term positive effects on the potential for global warming. Decreased demand for all fossil fuel–related energy sources and heavily relying on other renewable resources are also essential needs.
Environmental consequences of the COVID-19 pandemic: a terrifying trip
Issues with the handling of uprising biomedical waste
The current BMW collection and recycling infrastructure is under a lot of stress, which has resulted in inefficient waste reduction techniques like portable incinerations and open-air disposal of single-use plastics; these are also crucial factors for the safety of frontline workers (Basu and Basu 2021). In the face of mounting concern, the manufacturing line for single-use plastics is working to seize the moment and revitalize a once-thriving but now failing sector (Mousazadeh et al. 2021). Currently, many supermarkets prohibited customers from bringing their own cloth bags because they worry people might decide to buy their things in single-use plastic packaging substitutes. Additionally, a rise in online food orders has contributed to an increase in plastic consumption per person, illustrating how the COVID-19 pandemic has intensified environmental harm on a worldwide basis. As a result, there has been undoubtedly a large increase in the use of plastics, which will aggravate the leakage of microplastics into the environment. The use of plastic has increased dramatically (40%), as have other applications (17%), such as medical equipment and other associated ones. During COVID-19, the generation of BMW suddenly increased all over the world, which is considered an important threat to public health and biodiversity. In COVID-19, the BMW is generated from infected people, sample collection site, and diagnosis centers (Zambrano-Monserrate et al. 2020). In India, during the 1st lockdown period, medical waste has increased from 550 to 600 kg/day to around 1000 kg/day. Science COVID-19, the production of single-use plastic is increased globally. It is reported that about 14,607,834 face masks are used and a large number of BMW are produced during the COVID-19 period in Odisha; for a long period, these masks release dioxin and various toxic elements that pollute land and water ecosystem (Selvam et al. 2020).
The concerning issues of microplastic contamination in our environment have grown significantly. These are typically located in natural settings. In addition, individuals are utterly dependent on plastic and its other form (microplastic) produced by numerous events of pandemics (Oyedotun et al. 2020). Microplastic has a higher COVID-19 viral persistence rate than other materials. Therefore, it has been suggested that a potential source of microplastic in the surroundings is single-use plastic-based protective gear (Knowlton 2020; Sridharan et al. 2021). The N-95 masks are erected by polypropylene, whereas Tyvek is used to make the safety gloves and face shields. Dioxin was released into the surroundings by such two microplastics (Wang et al. 2021a, b). Polypropylene fibers make up the bulk of the microplastic released from different types of face masks (Chen et al. 2021). Organic waste and household protective equipment are also responsible for spreading several viral infections to regular people. Due to the absorption of heavy metals and organic contaminants by the natural environment, microplastics have a significant role to hinder this phenomenon. These microplastics affect the endocrine system and are considered harmful. By 2025, it is predicted that there will be 250 million metric tons of microplastic in marine waste worldwide (Jambeck et al. 2015; Ye et al. 2020).
Impact of biomedical waste on water
As COVID-19 spreads very rapidly because of close contact from one individual to another, more production of personal healthcare equipment is necessary to stop the harmful impact of biomedical waste on water. Dumping of healthcare wastes without proper treatment measures not only affects soil but also affects the groundwater level of that particular site as liquid toxic pollutants leach out and get mixed with groundwater. From hospitals to COVID care centers, direct disposal of medical wastes into the nearest pond or river has been noticed worldwide during the COVID-19 pandemic situation (Aggarwal and Kumar 2015). The toxic metals of these wastes alter the biology of water, which has a number of negative impacts on the water ecosystem. Plastic wastes in water bodies harm aquatic lives which eventually affects human beings. Additionally, this polluted water can spread infections very rapidly in the nearby locality. Research laboratories release various non-biodegradable chemical and radioactive elements in liquid form having carcinogenic effects on human health (Patil and Pokhrel 2005). In contact with air or water, the antibacterial substances (triclocarban and triclosan) found in laundry and cleaning products also create a protective surface layer. These contaminants have an adverse effect on both the habitats of humans and marine life (Ion et al. 2019). Chloroquine and hydroxychloroquine are released into the water system in huge amounts, which has significant ecotoxicological effects on living things (Kuroda et al. 2021). The components of the environment interact with one another. Handwashing soap contains bisphenol A (BPA), which has several negative impacts on soil and water quality. BPA has been shown to affect the endocrine system in a number of different organ systems in laboratory experiments (Dodson et al. 2012; Kim et al. 2021).
All major rivers of Odisha link up with the Bay of Bengal, in the northeastern part of the Indian Ocean. Inadequately treated water released microplastics into these waterways, finally transferring microplastic into the Indian Ocean. The basic water qualities were analyzed throughout pre-COVID, COVID, and post-COVID periods like temperature of water, pH, DO, BOD, COD, TC, and FC, which have been shrivelled. During the COVID period, the TC and FC variables of the Bay of Bengal are relatively high than the pre- and post-COVID pandemic at the Paradeep region of Odisha (Fig. 5a). Principal component analysis (PCA) of the fundamental water quality indicators such as water temperature, pH, DO, BOD, COD, TC, and FC of three important lakes, i.e., Anshupa, Chilka, and Tampara, has been inspected. Tampara Lake has higher peak metrics in the pre-COVID period (Fig. 5b). The DO, TC, FC, and COD are peak in Chilka Lake but only BOD more in Tampara during the pandemic period (Fig. 5c). Throughout post-COVID, TC and FC are high in Anshupa Lake, BOD, and COD is high in Tampara Lake (Fig. 5d). Unlikely, the pH and water temperature are always showed elevated in Chilka. The major rivers in Odisha are the Mahanadi, Subarnarekha, Brahmani, Baitarani, Budhabalanga, and Rushikuly. The basic water quality parameters of these rivers were analyzed in-between pre-COVID, COVID, and post-COVID, and these parameters are water temperature, pH, DO, BOD, COD, TC, and FC, which have been consistently investigated. In pre-COVID time, the TC, FC, and BOD parameters are unsatisfactory in Mahanadi, Brahmani, Budhabalanga, and Rushikuly than other two rivers (Fig. 6). On the other hand, the TC and FC levels are high in Mahanadi, and only BOD and TC are unsatisfactory in Brahmani during the pandemic period (Fig. 6). Throughout the post-COVID, BOD, TC, and FC water quality parameters are higher in Mahanadi and Brahmani than in other rivers (Fig. 6). Unlikely, all these water parameter concentrations will increase in the future days due to the rise of single-use plastics.
Biomedical waste’s effects on soil
According to the WHO, non-steroidal anti-inflammatory medicines (NSAIDs), such as ibuprofen, acetylsalicylate, and diclofenac, were utilized in pandemic outbreaks, while furosemide has been recommended for SARS-CoV-2-infected individuals (Brennecke et al. 2020; WHO 2020a, b). Solid waste management during pandemic situations especially during the COVID-19 outbreak has been a great challenge for many developing countries. The global pandemic has reported the dumping of an unusual amount of contaminated PPE kits, masks, and gloves by healthcare workers. Numerous other wastes from the isolation wards near the municipal dumping sites have also been reported (Jena and Patnaik 2021). It not only changes the soil quality of that site but also becomes an unhygienic place for citizens. Improper disposal of medicines and patients’ urine and feces during the treatment process not only infects the soil but also creates a nasty environment to the atmosphere (Shah et al. 2001). Alcohol-based products like hand sanitizers harm aquatic life when discharged into the environment. In addition, it affects groundwater indirectly through the soil. The soil and water ecology is impacted by triclosan, hydroxychloroquine, triclosan, and triclocarban. The anti-inflammatory medications also have an impact, exacerbating the negative effects of COVID-19 (Selvaranjan et al. 2021).
One-third of the ecosystem’s components are made up of plastic garbages, and soil by which it enters the initial habitat (de Souza Machado et al. 2018). Numerous types of microplastics exist in the terrestrial ecosystems’ soil, including agricultural systems, food plains, forests, and sands. These microplastics can come from various sources, including landfills, sewage sludge, composts, and wastewater-irrigation systems (Kumar et al. 2020; Scheurer and Bigalke 2018; Ng et al. 2021; Wang et al. 2020). Plastic garbage may modify the permeability and water-holding capacity of the soil and impair its bulk density and structural integrity (de Souza Machado et al. 2018; Wan et al. 2019). Additionally, it also affects various chemical and physical characteristics, such as enzyme activity and hydrogen ion concentration (Fei et al. 2020; Boots et al. 2019). The carbon, phosphorus, and nitrogen cycles in soil are crucial to the soil’s fertility and nutrients; it may also be impacted by COVID-19 waste (Zhang et al. 2019). The microplastic-containing harmful chemical sinks may modify the soil’s physicochemical qualities, bioavailability, and biodiversity as well as its mobility and adsorption capacity (Hüffer et al. 2019). The adsorption of microplastic by soil microorganisms and microbial communities may influence the possible dangers to both humans and animals (Zhang et al. 2019; Imran et al. 2019). There is still more research needed to access the possible effects and ecological concerns on terrestrial ecosystems of the interaction between protective equipment-associated microplastics and the COVID-19 virus in soils and waters.
Exposure and hazardous gas emissions during incineration
As biochemical wastes contain many infectious agents as well as hazardous chemical elements, improper disposal of this waste can lead to fatal effects on society. Open flaming of biochemical wastes produces injurious gases such as fly ash, carbon monoxide (CO), carbon dioxide (CO2), and other toxic flue gases. These not only pollute our environment but also cause many respiratory and skin diseases. Exposure to dioxins and mercury emitted by the burning of plastic and other medical wastes leads to hormonal misbalance and reproductive and developmental problems in living animals. Moreover, the increased atmospheric carbon dioxide ultimately affects global climate change and the food chain process (Manzoor and Sharma 2019).
Impacts of microplastics on the atmosphere
COVID-19, at first glance, reduces greenhouse gas emissions and enhances air quality. On the other hand, as plastic waste pollution rises over time, a hidden catastrophe will be the real cause of increasing worldwide GHG emissions. Plastic garbage is responsible for 850 million metric tons of annual GHG emissions, which will rise to 56 billion tons by 2050. The single-use protective plastic emits 0.05 kg of CO2 when shipping is not included, whereas the shipping emits 0.059 kg of CO2 gas. The washing of single-use plastic contributed to the 0.36 kg of CO2 that was released (Klemeš et al. 2020; Silva et al. 2021). Additionally, dangerous substances like dioxins and furans can be released during landfalls and the combustion of garbage from protective equipment, which can pollute the atmosphere (Vanapalli et al. 2021). Recent research has discovered that the protective gear can also fracture and linger in the air as microplastics (Zhang et al. 2021). As a result, the atmosphere plays a crucial role in the cycle of microplastics related to safety gear and contributes to the spreading of microplastics in various contexts. Additionally, the atmosphere contributes to producing protective gear made up of plastic through the microplastic cycle, and microplastic wastes degrade air quality, impact the climate, and absorb associated dangerous substances.
Effects of COVID-19 on energy sources
In the energy sector, the COVID-19 epidemic has caused serious problems. Coal accounts for around 40% of the electric energy produced by the major fuels globally. China, India, and Australia together generate 70% of the world’s coal. About 8.1 billion tons of coal were produced year by 2019; however, during the pandemic, that quantity fell sharply to only 40,000 metric tons in 2020 (Rizou et al. 2020; Mousazadeh et al. 2021). Similarly to this, during the initial lockdown period, world oil consumption declines by around 5% (Atolani et al. 2020). Consequently, there has been a significant lowering in the global use of power. Reducing air pollution due to lower NO2 production during COVID-19 leads to less electricity usage, which enhances the environment’s well-being (Lian et al. 2020).
Animal and aquatic life’s response to microplastics
Different detergents are released into water sources, creating foam. Some aquatic plants, including Potamogeton and Ranunculus aquatilis, cannot survive in a detergent level of 2.5 ppm (Kumar et al. 2021). In soils, harmful compounds build up and deteriorate the quality of the soil texture. Numerous aquatic ecosystems and biota are harmed by domestic water. The plasma of marine fish and some marine organisms has been found to include certain newly developed medicinal compounds (Vasquez et al. 2014). Ibuprofen, an anti-inflammatory drug, has been linked to substantial, long-lasting harmful effects on aquatic creature reproduction (De Girolamo et al. 2020; Carlsson et al. 2006).
Without any doubt, the COVID-19 epidemic causes water pollution around the planet. Low-density polymers in polystyrene and polypropylene cause them to float in seawater whereas high-density polymers such as polyethylene terephthalate, polyvinyl chloride, and polyvinyl alcohol readily sink on the bottom (De-la-Torre and Aragaw 2021). Therefore, key threats to its biodiversity are acidification of saltwater and microplastic degradation of the environment. Every year, seas are getting between 57,000 and 265,000 million metric tons of microplastic trash. In recent years, microplastics have been discovered in the groundwater, rivers, and lakes of India (Selvam et al. 2021).
Numerous studies have shown that face mask pollution impacted animals. However, the animal population and its habitat dramatically grew throughout the lockdown period. Conversely, inappropriate disposal of single-use plastics puts animals at the risk of suffocation and death by ingestion, trapping, and entanglement (Fig. 7a). Researchers also discovered that single-use plastic has an immediate and long-term impact on animal health, resulting in body deterioration, mobility issues that limit the feeding activity, changes in physiological blood parameters, strangulations, and considerable amount of reduction in biodiversity (Seif et al. 2018; Lavers et al. 2019). Consumption of microplastics can occasionally have an adverse impact on the animal’s ability to reproduce and their nutritional needs (Tavares et al. 2016; Thompson et al. 2020). Microplastics interact with intestinal-active microorganisms, reducing mucus outputs and causing dysbiosis (Wang et al. 2021a, b). Microplastics may accumulate by organisms and move up the food chain from lower biota to higher consumers, making food sources the most important way to enter the body of animals. According to experts, at least one microplastic is accumulated by 67% of sharks (Parton et al. 2020). COVID-19 face mask–released elements (exposure polymers) inhibit the development and reproduction of young earthworms. The adult earthworms’ spermatogenesis and intracellular esterase activities were similarly inhibited. The animal body’s tissue and cellular levels can be negatively impacted by microplastic (Kwak and An 2021). As a result of their additive and synergistic effects, the chemical pollutants connected to microplastics can have more severe impacts that ultimately damage different animal systems (Roda et al. 2020). In general, the COVID-19 protective gears cause harm to exposure adjacent animals by trapping, entanglement, and ingestion.
Impact of microplastics on human
Understanding the harm to human health posed by COVID-19 protective equipment linked with plastics and microplastics presents significant hurdles due to the paucity of research on adsorption properties and toxicological assessment of contaminated components. There is proof that airborne viruses or respiratory droplets from patients can be directly deposited onto personal protective equipment and stay active for more than 72 h. In 2018, many researchers discovered microplastics for the first time in the human lungs, spleen, kidneys, and liver. Microplastic is ingested into the colon and placenta of humans (Ragusa et al. 2021). With commercial marine and freshwater species, edible fruits and vegetables, consumption of soft drinks, drinking of water, and commercial marine as well as freshwater species, the concentration of microplastics consumed in the human body rises possessively. On average, 0.1 to 5 g of microplastics may enter bodies every week globally (Senathirajah et al. 2021). Some researchers noted that presently human blood samples contain 1.6 g/ml of plastic particles (Leslie et al. 2022). Top consumers have a higher concentration of microplastics than lower tropic levels, making them more riskier (Fig. 7b) (Carbery et al. 2018). The intestinal function is destroyed by the oxidative stress and inflammation brought on by the interaction of microplastics with the gut floor (Huang et al. 2021). Inflammation promotes cell death, epithelial barrier degradation causes cardiovascular illnesses, diabetes, and cancers, and airborne microplastics can harm and cause oxidative stress (Dong et al. 2020; Prata 2018; Yang et al. 2021) (Fig. 7b). Therefore, more scientific research should be required to establish that protective gear made of microplastic may certainly absorb viruses but shows as the potential contaminant source.
Concluding thoughts, future vision, and perspectives
This article emphasized the relationship between hazards to those, directly and indirectly, connected to this profession, poor and non-scientific handling of biological waste materials. The COVID-19 epidemic has unprecedentedly impacted the environment, human life, and the global economy. The COVID-19 pandemic could provide short-term advantages for the natural environment. However, the long-term environmental problems brought on by this viral pandemic might have enduring impacts and provide difficulties for all nations. Due to the widespread use of anti-microbial hand sanitizers, disinfectants, and pharmaceuticals, including triclocarban, triclosan, and hydroxychloroquine, dangerous emergent pollutants such as COVID-19 have also had a severe impact on the water qualities and soil ecology. In addition, after the COVID-19 incident, the amount of plastic garbage has increased dramatically. Protective gear can lower the chance of contracting the COVID-19 virus during the pandemic, but repeated usage and inappropriate discarding make the polymer issue in severe condition. It poses significant risks to aquatic life and people by being a significant source of microplastic discharge and build-up in aquatic and terrestrial environments. Presently, not only is too much plastic garbage damaging the marine and terrestrial environments, but it will also eventually break down into tiny plastics called microplastic and nanoscale plastic. Even more severe, irrevocable harm to both people and the environment can be brought on by these micro- and nanoscale plastics. People should be mindful of the long-term effects of plastic consumption and disposal since the COVID-19 epidemic has worsened the plastic pollution situation. According to our condensed statistics and speculative estimation, the COVID-19 epidemic has caused to gear up a tremendous amount of plastic to be produced globally. The present technologies cannot handle the plastic overload situation; hence, innovative methods for managing plastic waste are urgently required. As a result, it is crucial to enact laws and regulations restricting plastic use and inform people on how to manage, reuse, and recycle their plastic trash. Work should be done in the future to develop backup strategies for managing plastic trash in emergency scenarios and preventing plastic pollution. Future studies should also concentrate on the destiny and transportation of micro- and nanoscale plastics since the discarded plastic eventually degrades into these sizes. Further study is necessary to understand how plastic sizes and surface characteristics affect their destiny and transport behavior. Considering the mitigation strategies, recovery of the previous environment during the COVID-19 lockdown period showed environmental degradation. Such undesired incidents are also caused by humans that might be reversible, and applied strategies should be implicated to rebuild the “accidentally positive” phenomenon. One of the best examples is the “smart green city” concept. Subsequently, steps should be taken to remove the conventional plastics with greener alternative components; adding a reliable disposal platform for PPE beyond incineration and the option of landfilling. However, it may be assumed that clustering in the surroundings will be a key factor controlling their activity and offer information on how they can be moved through the environment or eliminated in treatment facilities. That would enable more methodical management of the long-term effects of global plastic pollution. It serves as a reminder of our disregard for the environment and the consequences of human-caused climate change.
Data availability
Data sharing is not applicable to this article as no new data were created or analyzed in this study.
Abbreviations
- COVID-19:
-
Coronavirus disease 2019
- SARS-CoV-2:
-
Severe acute respiratory syndrome coronavirus 2
- WHO:
-
World Health Organization
- GHG:
-
Greenhouse gas
- DO:
-
Dissolved oxygen
- BOD:
-
Biological oxygen demand
- COD:
-
Chemical oxygen demand
- TC:
-
Total concentration
- IEA:
-
International Energy Agency
- PPE:
-
Personal protective equipment
- CPCB:
-
Central Pollution Control Board
- TB:
-
Tuberculosis
- CHC:
-
Community Health Center
- PHC:
-
Primary Health Care
- BMW:
-
Biomedical waste
- VOC:
-
Volatile organic compounds
References
Aggarwal H, Kumar P (2015) Need for biomedical waste management. J Med Soc 29(1):58–58
Atolani O, Baker MT et al (2020) COVID-19: critical discussion on the applications and implications of chemicals in sanitizers and disinfectants. EXCLI J 19:785
Basu A, Basu LB (2021) Questioning the green recovery: a take on Post-COVID scenario. In: Mishra M, Singh RB (eds) COVID-19 pandemic trajectory in the developing world, no 6. Springer, Singapore, pp 117–144
Biswal A, Singh T et al (2020) COVID-19 lockdown and its impact on tropospheric NO2 concentrations over India using satellite-based data. Heliyon 6(9):e04764
Boots B, Russell CW et al (2019) Effects of microplastics in soil ecosystems: above and below ground. Environ Sci Technol 53(19):11496–11506
Brennecke A, Villar L et al (2020) Is inhaled furosemide a potential therapeutic for COVID-19? Am J Med Sci 360(3):216–221
Capoor MR, Parida A (2021a) Biomedical waste and solid waste management in the time of covid-19: a comprehensive review of the national and international scenario and guidelines. J Lab Phys 13(02):175–182
Capoor MR, Parida A (2021b) Current perspectives of biomedical waste management in context of COVID-19. Indian J Med Microbiol 39(2):171–178
Carbery M, O’Connor W et al (2018) Trophic transfer of microplastics and mixed contaminants in the marine food web and implications for human health. Environ Int 115:400–409
Carlsson C, Johansson A-K et al (2006) Are pharmaceuticals potent environmental pollutants?: part I: environmental risk assessments of selected active pharmaceutical ingredients. Sci Total Environ 364(1–3):67–87
Chand S, Shastry C et al (2020) Water, sanitation, hygiene and biomedical waste disposal in the healthcare system: a review. Biomedicine 40(1):14–19
Chen X, Chen X et al (2021) Used disposable face masks are significant sources of microplastics to environment. Environ Pollut 285:117485
Das A, Garg R et al (2020) Biomedical waste management: the challenge amidst COVID-19 pandemic. J Lab Phys 12(02):161–162
De-la-Torre GE, Aragaw TA (2021) What we need to know about PPE associated with the COVID-19 pandemic in the marine environment. Mar Pollut Bull 163:111879
De Girolamo L, Peretti GM et al (2020) COVID-19—the real role of NSAIDs in Italy. BioMed Central 15:1–3
de Souza Machado AA, Lau CW et al (2018) Impacts of microplastics on the soil biophysical environment. Environ Sci Technol 52(17):9656–9665
Dehal A, Vaidya AN et al (2022) Biomedical waste generation and management during COVID-19 pandemic in India: challenges and possible management strategies. Environ Sci Pollut Res 29(10):14830–14845
Dodson RE, Nishioka M et al (2012) Endocrine disruptors and asthma-associated chemicals in consumer products. Environ Health Perspect 120(7):935–943
Dong C-D, Chen C-W et al (2020) Polystyrene microplastic particles: in vitro pulmonary toxicity assessment. J Hazard Mater 385:121575
Du H, Shi S et al (2019) Hydrophobic-force-driven adsorption of bisphenol A from aqueous solution by polyethylene glycol diacrylate hydrogel microsphere. Environ Sci Pollut Res 26(22):22362–22371
Fei Y, Huang S et al (2020) Response of soil enzyme activities and bacterial communities to the accumulation of microplastics in an acid cropped soil. Sci Total Environ 707:135634
Gandhiok J, Ibrar M (2020) “COVID-19: noise pollution falls as lockdown rings in sound of silence.” Times of India. 1–6. from https://timesofindia.indiatimes.com/india/covid-19-noise-pollution-falls-as-lockdown-rings-in-sound-of-silence/articleshow/75309318.cms. Accessed May 23 2022
Ghosh I (2020) “The emissions impact of coronavirus lockdowns, as shown by satellites.” Visual Capitalist 21. https://www.visualcapitalist.com/coronavirus-lockdowns-emissions/. Accessed June 12 2022
Goswami M, Goswami PJ et al (2021) Challenges and actions to the environmental management of bio-medical waste during COVID-19 pandemic in India. Heliyon 7(3):e06313
Haque MS, Sharif S et al (2021) SARS-CoV-2 pandemic-induced PPE and single-use plastic waste generation scenario. Waste Manag Res 39(1_suppl):3–17
Henriques M (2020) “Will COVID-19 have a lasting impact on the environment.” BBC news. https://www.bbc.com/future/article/20200326-covid-19-the-impact-of-coronavirus-on-the-environment. Accessed on June 24 2022
Huang Z, Weng Y et al (2021) Microplastic: a potential threat to human and animal health by interfering with the intestinal barrier function and changing the intestinal microenvironment. Sci Total Environ 785:147365
Hüffer T, Metzelder F et al (2019) Polyethylene microplastics influence the transport of organic contaminants in soil. Sci Total Environ 657:242–247
IEA (2020) “Oil market report: March 2020. The International Energy Agency, Paris, France. https://www.iea.org/reports/oil-market-report-march-2020. Accessed on Jul 25 2022
IEP (2020) “Impact of lockdown (25th March to 15th April) on air quality.” https://www.iea.org/reports/oil-market-report-march-2020. Accessed 13 Apr 2020
Imran M, Das KR et al (2019) Co-selection of multi-antibiotic resistance in bacterial pathogens in metal and microplastic contaminated environments: an emerging health threat. Chemosphere 215:846–857
Ion I, Ivan GR et al (2019) Adsorption of triclocarban (TCC) onto fullerene C60 in simulated environmental aqueous conditions. Sep Sci Technol 54(17):2759–2772
Jambeck JR, Geyer R et al (2015) Plastic waste inputs from land into the ocean. Science 347(6223):768–771
Jena B, Patnaik S, Patnaik N, Patnaik N (2021) Impact of improper biomedical waste disposal on human health and environment during covid-19 pandemic. Eur J Mol Clin Med 8(3):4137–4143
Kim S, Gholamirad F et al (2021) Enhanced adsorption performance for selected pharmaceutical compounds by sonicated Ti3C2TX MXene. Chem Eng J 406:126789
Klemeš JJ, Van Fan Y et al (2020) The energy and environmental footprints of COVID-19 fighting measures–PPE, disinfection, supply chains. Energy 211:118701
Knowlton KU (2020) Pathogenesis of SARS-CoV-2 induced cardiac injury from the perspective of the virus. J Mol Cell Cardiol 147:12
Kulkarni BN, Anantharama V (2020) Repercussions of COVID-19 pandemic on municipal solid waste management: challenges and opportunities. Sci Total Environ 743:140693
Kumar A, Jain V et al (2021) Environmental impact of COVID-19 pandemic: more negatives than positives. Environ Sustain 4(3):447–454
Kumar M, Xiong X et al (2020) Microplastics as pollutants in agricultural soils. Environ Pollut 265:114980
Kuroda K, Li C et al (2021) Predicted occurrence, ecotoxicological risk and environmentally acquired resistance of antiviral drugs associated with COVID-19 in environmental waters. Sci Total Environ 776:145740
Kwak JI, An Y-J (2021) Post COVID-19 pandemic: biofragmentation and soil ecotoxicological effects of microplastics derived from face masks. J Hazard Mater 416:126169
Lavers JL, Hutton I et al (2019) Clinical pathology of plastic ingestion in marine birds and relationships with blood chemistry. Environ Sci Technol 53(15):9224–9231
Leslie HA, Van Velzen MJ et al (2022) Discovery and quantification of plastic particle pollution in human blood. Environ Int 163:107199
Lian X, Huang J et al (2020) Impact of city lockdown on the air quality of COVID-19-hit of Wuhan city. Sci Total Environ 742:140556
Lokhandwala S, Gautam P (2020) Indirect impact of COVID-19 on environment: a brief study in Indian context. Environ Res 188:109807
Manzoor J, Sharma M (2019) Impact of biomedical waste on environment and human health. Environ Claims J 31(4):311–334
Mekonnen BA, Aragaw TA (2021) Environmental sustainability and COVID-19 pandemic: an overview review on new opportunities and challenges. In: Muthu SS (ed) COVID-19. Environmental footprints and eco-design of products and processes. Springer, Singapore, pp 117–140
Mousazadeh M, Paital B et al (2021) Positive environmental effects of the coronavirus 2020 episode: a review. Environ Dev Sustain 23(9):12738–12760
Ng EL, Lin SY et al (2021) Microplastic pollution alters forest soil microbiome. J Hazard Mater 409:124606
Nghiem LD, Morgan B et al (2020) The COVID-19 pandemic: considerations for the waste and wastewater services sector. Case Stud Chem Environ Eng 1:100006
Oyedotun TDT, Kasim OF et al (2020) Municipal waste management in the era of COVID-19: perceptions, practices, and potentials for research in developing countries. Res Globalization 2:100033
Parashar N, Hait S (2021) Plastics in the time of COVID-19 pandemic: protector or polluter? Sci Total Environ 759:144274
Parton KJ, Godley BJ et al (2020) Investigating the presence of microplastics in demersal sharks of the North-East Atlantic. Sci Rep 10(1):1–11
Patil GV, Pokhrel K (2005) Biomedical solid waste management in an Indian hospital: a case study. Waste Manage 25(6):592–599
Picheta R (2020) Coronavirus is causing a flurry of plastic waste. Campaigners fear it may be permanent. CNN
Prata JC (2018) Airborne microplastics: consequences to human health? Environ Pollut 234:115–126
Prüss A, Emmanuel J, et al (2014) “Safe management of wastes from health-care activities.” 2nd Edition, ISBN 978 92 4 154856 4, 1–329
Ragusa A, Svelato A et al (2021) Plasticenta: first evidence of microplastics in human placenta. Environ Int 146:106274
Rahman MM, Bodrud-Doza M et al (2020) Biomedical waste amid COVID-19: perspectives from Bangladesh. Lancet Glob Health 8(10):e1262
Rizou M, Galanakis IM et al (2020) Safety of foods, food supply chain and environment within the COVID-19 pandemic. Trends Food Sci Technol 102:293–299
Roda JFB, Lauer MM et al (2020) Microplastics and copper effects on the neotropical teleost Prochilodus lineatus: is there any interaction? Comp Biochem Physiol A: Mol Integr Physiol 242:110659
Sangkham S (2020) Face mask and medical waste disposal during the novel COVID-19 pandemic in Asia. Case Stud Chem Environ Eng 2:100052
Saxena P, Pradhan IP et al (2021) Redefining bio medical waste management during COVID-19 in india: a way forward. Mater Today: Proc 60:849–858
Scheurer M, Bigalke M (2018) Microplastics in Swiss floodplain soils. Environ Sci Technol 52(6):3591–3598
Seif S, Provencher J et al (2018) Plastic and non-plastic debris ingestion in three gull species feeding in an urban landfill environment. Arch Environ Contam Toxicol 74(3):349–360
Selvam S, Jesuraja K et al (2021) Hazardous microplastic characteristics and its role as a vector of heavy metal in groundwater and surface water of coastal south India. J Hazard Mater 402:123786
Selvam S, Muthukumar P et al (2020) SARS-CoV-2 pandemic lockdown: effects on air quality in the industrialized Gujarat state of India. Sci Total Environ 737:140391
Selvaranjan K, Navaratnam S et al (2021) Environmental challenges induced by extensive use of face masks during COVID-19: a review and potential solutions. Environ Chall 3:100039
Senathirajah K, Attwood S et al (2021) Estimation of the mass of microplastics ingested–a pivotal first step towards human health risk assessment. J Hazard Mater 404:124004
Shah S, Mehta M, et al (2001) “Occupational health hazards encountered at health care facility and medical college in India.” American Industrial Hygiene Association. https://www.who.int/tools/occupational-hazards-in-health-sector#:~:text=The%20most%20common%20occupational%20infections,infections%20(coronaviruses%2C%20influenza). Accessed on 14 Jul 2022
Silva ALP, Prata JC et al (2021) Increased plastic pollution due to COVID-19 pandemic: challenges and recommendations. Chem Eng J 405:126683
Singh N, Tang Y et al (2020) Environmentally sustainable management of used personal protective equipment. Environ Sci Technol 54(14):8500–8502
Somani M, Srivastava AN et al (2020) Indirect implications of COVID-19 towards sustainable environment: an investigation in Indian context. Bioresour Technol Rep 11:100491
Sridharan S, Kumar M et al (2021) Microplastics as an emerging source of particulate air pollution: a critical review. J Hazard Mater 418:126245
Tavares DC, da Costa LL et al (2016) Nests of the brown booby (Sula leucogaster) as a potential indicator of tropical ocean pollution by marine debris. Ecol Ind 70:10–14
Thakur V (2021) Framework for PESTEL dimensions of sustainable healthcare waste management: learnings from COVID-19 outbreak. J Clean Prod 287:125562
Thiessen T (2020) How clean air cities could outlast COVID-19 lockdowns. https://www.forbes.com/sites/tamarathiessen/2020/04/10/how-clean-air-cities-could-outlast-covid-19-lockdowns/?sh=44bbeca06bb5. Accessed on 12 June 2022
Thompson DL, Ovenden TS et al (2020) The prevalence and source of plastic incorporated into nests of five seabird species on a small offshore island. Mar Pollut Bull 154:111076
Tripathi A, Tyagi VK et al (2020) Challenges, opportunities and progress in solid waste management during COVID-19 pandemic. Case Stud Chem Environ Eng 2:100060
Vanapalli KR, Sharma HB et al (2021) Challenges and strategies for effective plastic waste management during and post COVID-19 pandemic. Sci Total Environ 750:141514
Vasquez MI, Lambrianides A et al (2014) Environmental side effects of pharmaceutical cocktails: what we know and what we should know. J Hazard Mater 279:169–189
Wan Y, Wu C et al (2019) Effects of plastic contamination on water evaporation and desiccation cracking in soil. Sci Total Environ 654:576–582
Wang J, Peng C et al (2021a) The impact of microplastic-microbe interactions on animal health and biogeochemical cycles: a mini-review. Sci Total Environ 773:145697
Wang J, Xu X et al (2021b) Heterogeneous effects of COVID-19 lockdown measures on air quality in Northern China. Appl Energy 282:116179
Wang W, Ge J et al (2020) Environmental fate and impacts of microplastics in soil ecosystems: progress and perspective. Sci Total Environ 708:134841
WHO (2020a) Water, sanitation, hygiene and waste management for COVID-19: technical brief, 03 March 2020a, World Health Organization. https://apps.who.int/iris/handle/10665/331305. Accessed on 12 Jul 2022
WHO (2020b) Water, sanitation, hygiene, and waste management for SARS-CoV-2, the virus that causes COVID-19: interim guidance, 29 July 2020b, World Health Organization. https://www.who.int/publications/i/item/WHO-2019-nCoV-IPC-WASH-2020.4. Accessed on 12 Jul 2022
Woodall LC, Sanchez-Vidal A et al (2014) The deep sea is a major sink for microplastic debris. Royal Soc Open Sci 1(4):140317
Yang S, Cheng Y et al (2021) In vitro evaluation of nanoplastics using human lung epithelial cells, microarray analysis and co-culture model. Ecotoxicol Environ Saf 226:112837
Ye S, Cheng M et al (2020) Insights into catalytic removal and separation of attached metals from natural-aged microplastics by magnetic biochar activating oxidation process. Water Res 179:115876
Yunus AP, Masago Y et al (2020) COVID-19 and surface water quality: improved lake water quality during the lockdown. Sci Total Environ 731:139012
Zambrano-Monserrate MA, Ruano MA et al (2020) Indirect effects of COVID-19 on the environment. Sci Total Environ 728:138813
Zhang EJ, Aitchison LP, Phillips N, Shaban RZ, Kam AW (2021) Protecting the environment from plastic PPE. BMJ 372:n109
Zhang M, Zhao Y et al (2019) Microplastics from mulching film is a distinct habitat for bacteria in farmland soil. Sci Total Environ 688:470–478
Author information
Authors and Affiliations
Contributions
Jiban Kumar Behera: data curation; analysis; investigation; original draft—writing and figure development. Pabitra Mishra: analysis, validation, and figure development. Anway Kumar Jena: validation, analysis. Manojit Bhattacharya: supervision, reviewing and editing, validation. Bhaskar Behera: validation and reviewing.
Corresponding author
Ethics declarations
Ethical approval
Not required.
Consent to participate
Not required.
Consent for pulication
Not required.
Competing interests
The authors declare no competing interests.
Additional information
Responsible Editor: Philippe Garrigues
Publisher's note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Rights and permissions
Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.
About this article
Cite this article
Behera, J.K., Mishra, P., Jena, A.K. et al. Understanding of environmental pollution and its anthropogenic impacts on biological resources during the COVID-19 period. Environ Sci Pollut Res (2022). https://doi.org/10.1007/s11356-022-24789-6
Received:
Accepted:
Published:
DOI: https://doi.org/10.1007/s11356-022-24789-6