| Literature DB >> 35194403 |
Bashir Adelodun1,2, Fidelis Odedishemi Ajibade3,4,5, Rahmat Gbemisola Ibrahim6, Joshua O Ighalo7,8, Hashim Olalekan Bakare7, Pankaj Kumar9, Ebrahem M Eid10,11, Vinod Kumar9, Golden Odey1, Kyung-Sook Choi1,12.
Abstract
The recent emergence of the COVID-19 pandemic has contributed to the drastic production and use of healthcare and personal protective equipment, leading to the release of a huge quantity of hazardous medical and solid wastes in the environment. Meanwhile, these solid wastes may contribute to the spread of the SARS-CoV-2 viral particles when disposed of without proper treatment and care. Since SARS-CoV-2 could persist on different material surfaces including plastic, steel, paper, cardboard, cloth, and wood, proper management of these hazardous solid wastes has become a challenging task during the COVID-19 pandemic. In this paper, an overview of the consumption of COVID-19-related healthcare and personal protective equipment along with the production of hazardous solid waste is presented. The efficient management of these wastes is necessary to prevent the entering of SARS-CoV-2 in various environmental compartments. Therefore, some preventive measures including the use of biodegradable materials for manufacturing personal protective equipment, minimizing the use of non-biodegradable materials, efficient pre- and-post planning, careful segregation, and disposal are, therefore, proposed for their sustainable management. The findings reported in this paper contribute to tackling the problems associated with hazardous solid waste management, particularly for low- and middle-income countries. © Springer Japan KK, part of Springer Nature 2021.Entities:
Keywords: COVID-19; Coronavirus; Household waste; Medical waste; SARS-CoV-2; Waste management
Year: 2021 PMID: 35194403 PMCID: PMC8343211 DOI: 10.1007/s10163-021-01281-w
Source DB: PubMed Journal: J Mater Cycles Waste Manag ISSN: 1438-4957 Impact factor: 2.863
Estimated daily facemasks usage in some selected developing countries with the COVID-19 increase rate
| Country | aPopulation | aCOVID-19 cases (May 1, 2020) | aCOVID-19 cases (January 10, 2021) | Percentage increase of confirmed cases (%) | bEstimated daily facemasks usage (million) |
|---|---|---|---|---|---|
| Brazil | 212.56 | 92,109 | 80,75,998 | 8668 | 299.28 |
| India | 1380.00 | 37,257 | 1,04,51,346 | 27,952 | 772.80 |
| Iran | 83.99 | 95,646 | 12,80,438 | 1239 | 102.14 |
| Pakistan | 220.89 | 18,092 | 1,76,617 | 2677 | 123.70 |
| Bangladesh | 164.69 | 8238 | 1,12,306 | 6229 | 102.77 |
| South Africa | 59.31 | 5951 | 92,681 | 20,303 | 63.58 |
| Columbia | 50.88 | 7006 | 65,633 | 25,184 | 0.65 |
| Egypt | 102.33 | 5895 | 53,758 | 2424 | 70.41 |
| Indonesia | 273.52 | 10,551 | 45,891 | 7656 | 245.08 |
| Argentina | 45.20 | 4532 | 41,204 | 37,729 | 0.67 |
| Philippines | 109.58 | 8772 | 30,052 | 5438 | 82.40 |
| Oman | 5.11 | 2447 | 29,471 | 5215 | 7.11 |
| Iraq | 40.22 | 2153 | 29,222 | 27,876 | 46.98 |
| Afghanistan | 38.81 | 2335 | 28,833 | 2191 | 15.53 |
| Bolivia | 11.67 | 1167 | 23,512 | 14,707 | 0.13 |
| Nigeria | 206.14 | 2170 | 19,808 | 4465 | 171.51 |
| Ghana | 31.07 | 2074 | 13,717 | 2589 | 28.34 |
| Algeria | 43.85 | 4154 | 11,631 | 2353 | 51.22 |
| Cameroon | 26.55 | 1832 | 11,610 | 1366 | 23.79 |
| Morocco | 36.91 | 4569 | 9957 | 9785 | 37.80 |
| Sudan | 43.85 | 442 | 8580 | 5175 | 24.56 |
| Ivory Coast | 26.38 | 1333 | 7276 | 1662 | 21.52 |
| Uzbekistan | 33.47 | 2086 | 6272 | 3619 | 26.78 |
| Senegal | 16.74 | 1024 | 5888 | 1951 | 13.13 |
| DR Congo | 89.56 | 604 | 5826 | 3072 | 65.92 |
| Ethiopia | 114.96 | 133 | 4532 | 95,984 | 38.63 |
| Kenya | 53.77 | 411 | 4478 | 23,789 | 24.09 |
| Sri Lanka | 21.41 | 690 | 1950 | 6833 | 6.17 |
| Paraguay | 7.13 | 266 | 1362 | 43,143 | 0.07 |
| Yemen | 29.83 | 7 | 922 | 29,957 | 18.13 |
aSource: Worldometer [16]
bCalculation method was adapted from Nzediegwu and Chang [15]
Fig. 1Solid waste associated with COVID-19 spread with potential sustainable measures
Recent research findings on hospital solid waste (HSW) management
| Location | Key findings | Reference |
|---|---|---|
| Ogbomoso, Nigeria | The government did not assist in the waste disposal and there was no recycling of waste. Disposal was majorly by incineration/burning and landfill | [ |
| Swath district, Pakistan | Pyrolysis or chemical disinfection was more effective in dealing with HSW than incineration and landfilling | [ |
| Aligarh, India | Most hospitals in the region did not have an HSW management system | [ |
| Gujranwala, Pakistan | Landfill and incineration were less effective than incineration for dealing with HSW from an environmental perspective | [ |
| Nablus, Palestine | System dynamics modeling was used to develop a comprehensive and sophisticated prediction of hospital waste generation | [ |
| Developing countries | Most developing countries have a high level of hazardous waste in their HSW beyond the WHO standards | [ |
| Sant’Ana do Livramento, Brazil | Most of the health professionals at the hospital were aware of the risks of the wastes and handled them carefully for disposal | [ |
| Lagos, Nigeria | In most hospitals in the area, there were no internal policies or guidelines in place for managing the wastes | [ |
| Hormozgan province, Iran | About 9.45% of the waste generated is hazardous and there are still serious disposal issues | [ |
| Tehran, Iran | In most hospitals, the waste was properly segregated and disinfected and only a few hospitals (20%) had HSW storage | [ |
| Patiala city, Punjab, India | There was an absence of proper waste management and a general lack of awareness of the hazards of HSW | [ |
| Rajshahi City, Bangladesh | The unsafe practice of open dumping was still practiced and clinical waste was not separated from non-hospital waste | [ |
| Pokhara, Nepal | Hazardous wastes in the HSW were above WHO limits and awareness of safe disposal techniques was low | [ |
| Jogyakarta, Indonesia | The waste was properly handled but recycling has not been considered | [ |
| Mazandaran province, Iran | 36.1% of the HSW generated was hazardous and over half the hospitals considered disposal of their waste by incineration | [ |
| Anambra, Nigeria | The key issue in the disposal chain was the unavailability of suitable materials for waste segregation | [ |
| Ile-Ife, Nigeria | The methods used and materials employed in storage and disposal was not in agreement with WHO standards | [ |
| Shimla City, India | HSW generation was properly handled and the practitioners were aware of its risk | [ |