Plastics have become vital assets for humanity; these materials are used widely in pharmaceuticals, healthcare systems, and many other applications. The rising demand and uses of articles made wholly or partly from synthetic polymers, coupled with their non-biodegradability, contributes to the massive volume of plastic wastes across cities in most developing nations. Thistrend has become an issue of significant environmental concern. However, the fight against COVID-19 would look almost impossible without personal protective equipment (PPE) primarily made from various plastics which in turn, contribute enormously to the volume of waste streams. To circumvent this present challenge, research has been recommending solutions. The existing literature primarily focuses on the most developed countries, emphasising Asian countries with less attention to other developing countries like Nigeria and African countries. This study, therefore, reviewed the personal protective equipment used in healthcare, plastic types employed for their production, and the appropriate technology for managing their associated wastes. The application of proper disposal methods can reduce the toxic effects of discarded plastics on human health and the environment. In this review, the SWOT analysis approach was employed to unveil the benefits, limitations, opportunities, and threats associated with respective waste management approaches. As the coronavirus pandemic continues to intensifier, its adverse impacts on human health and the economy are increasing; authorities are encouraged to address waste management, including medical, household, and other hazardous waste, as an urgent and critical public service to minimize potential secondary health and environmental impacts.
Citation: Wilson U. Eze, Toyese Oyegoke, Jonathan D. Gaiya, Reginald Umunakwe, David I. Onyemachi. Review of personal protective equipment and their associated wastes, life-cycle and effective management during the Covid-19 pandemic in developing nations[J]. Clean Technologies and Recycling, 2022, 2(1): 1-31. doi: 10.3934/ctr.2022001
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Plastics have become vital assets for humanity; these materials are used widely in pharmaceuticals, healthcare systems, and many other applications. The rising demand and uses of articles made wholly or partly from synthetic polymers, coupled with their non-biodegradability, contributes to the massive volume of plastic wastes across cities in most developing nations. Thistrend has become an issue of significant environmental concern. However, the fight against COVID-19 would look almost impossible without personal protective equipment (PPE) primarily made from various plastics which in turn, contribute enormously to the volume of waste streams. To circumvent this present challenge, research has been recommending solutions. The existing literature primarily focuses on the most developed countries, emphasising Asian countries with less attention to other developing countries like Nigeria and African countries. This study, therefore, reviewed the personal protective equipment used in healthcare, plastic types employed for their production, and the appropriate technology for managing their associated wastes. The application of proper disposal methods can reduce the toxic effects of discarded plastics on human health and the environment. In this review, the SWOT analysis approach was employed to unveil the benefits, limitations, opportunities, and threats associated with respective waste management approaches. As the coronavirus pandemic continues to intensifier, its adverse impacts on human health and the economy are increasing; authorities are encouraged to address waste management, including medical, household, and other hazardous waste, as an urgent and critical public service to minimize potential secondary health and environmental impacts.
The theory of cellular algebra was first introduced by Graham and Lehrer [1]. K¨onig and Xi [2] later gave a more structural equivalent definition of cellular theory. Suppose K is a field and A is an associative unital free K-algebra. In the sense of Graham and Lehrer, A is cellular if it has a K-basis {cs,t|λ∈Λ, s,t∈T(λ)}, where (Λ,≥) is a poset (partially ordered set) and T(λ) are finite index sets, such that
(i) The K-linear map ∗:A⟶A defined by cst↦cts for all λ∈Λ, s,t∈T(λ) is an anti-isomorphism of A.
(ii) For any λ∈Λ, t∈T(λ), and a∈A, there exists ratv∈K such that for all s∈T(λ),
csta≡∑v∈T(λ)ratvcsvmodA>λ. |
The basis {cst|λ∈Λ, s,t∈T(λ)} is the so called cellular basis. The existence of a cellular basis implies rich information on representations of A. One of the main uses of a cellular basis is to give the complete set of simple modules of A. According to Graham and Lehrer's theory, the cellular basis determines a cell filtration (a two-sided ideal filtration) A(λ1)⊂A(λ2)⊂⋯⊂A(λk) of A with respect to a total ordering λ1,λ2,…,λk of the poset Λ. As an A-module, each quotient A(λi)/A(λi−1) of the filtration is a direct sum of |T(λi)| copies of cell module C(λi). Moreover, for each λ∈Λ, the cellular basis attaches C(λ) a bilinear form ⟨,⟩λ such that C(λ)/rad⟨,⟩λ is either 0 or an irreducible module. Denote by D(λ) the quotient C(λ)/rad⟨,⟩λ; all the nonzero D(λ)s consist of a complete set of non-isomorphic simple A-modules. For a cellular algebra, it may possess different constructions of cellular bases. By Graham and Lehrer's theory, different cellular bases may determine different parameterizations of simple modules. So the study of the relationship between different parameterizations of simple modules becomes an interesting topic.
In this paper, we fix n as a natural number and ℓ a positive integer. The cyclotomic Hecke algebras of G(ℓ,1,n) was introduced by Ariki, Koike [3] and Brouˊe, Malle [4] independently. Many authors have constructed different cellular bases of cyclotomic Hecke algebras of G(ℓ,1,n). For example, Dipper, James, and Mathas [5] constructed the cellular basis {mst|λ∈Pℓn and s,t∈Std(λ)} with respect to the poset (Pℓn,⊵), where Pℓn is the set of ℓ-partitions of n and ⊵ is the dominance order on Pℓn. Through the cellular basis mst, Ariki [6] proved that the simple modules of cyclotomic Hecke algebras of G(ℓ,1,n) are paramaterized by Kleshchev multipartitons. By Brundan–Kleshchev's isomorphism [7], Hu and Mathas [8] constructed the graded cellular basis {ψst|λ∈Pℓn and s,t∈Std(λ)} of cyclotomic Hecke algebras of G(ℓ,1,n) with respect to the poset (Pℓn,⊵). Different from mst and ψst, Bowman [9] constructed an integral graded cellular basis {cθst|λ∈Pℓn and s,t∈Stdθ(λ)} of cyclotomic Hecke algebras of G(ℓ,1,n) with respect to the poset (Pℓn,⊵θ), where ⊵θ is the θ-dominance order on Pℓn. Corresponding to Bowman's basis, the simple modules of cyclotomic Hecke algebra of G(ℓ,1,n) are labeled by Uglov multipartitions. We want to study the relationship between these different paramaterizations of simple modules of cyclotomic Hecke algebra of G(ℓ,1,n). To this aim, it's necessary for us to understand the relationship between dominance order and θ-dominance order on Pℓn.
The content of this paper is organized as follows; In Section 2, we introduce some notations and definitions. In Section 3, we give a combinatorial description of the neighbors with weak θ-dominance order whenever the loading θ is strongly separated. In Section 4, we give the main results of this paper: The relationship between weak θ-dominance order, θ-dominance order, and dominance order. Throughout this paper, we denote by N the set of natural numbers and Z the set of integers.
A partition of n is a finite non-increasing sequence λ=(λ1,λ2,…) of non-negative integers with |λ|=∑iλi=n. If λ is a partition of n, we write λ⊢n. Let Pn be the set of partitions of n. The Young diagram of λ is a set
[λ]={(i,j)|1≤j≤λi,∀i≥1}. |
The elements of [λ] are called the nodes of λ. The Young diagram can be identified with a tableau. For example, λ=(3,2,1) is a partition of 6; its Young diagram
[λ]={(1,1),(1,2),(1,3),(2,1),(2,2),(3,1)}, |
it can be identified with the tableau
![]() |
where (i,j) corresponds to the box in the i-th row and j-th column. For a partition λ, define its height h(λ)=max.
A multipartition of with components is an ordered sequence of partitions such that . We denote by the set of multipartitions of with components. For , we write and call an -partition of . When , it is clear . The Young diagram of is a set
The elements of are called the nodes of . The Young diagram can be identified with an ordered sequence of tableaux. For example, is a 3-partition of 9, the Young diagram
it can be identified with the following ordered sequence of tableaux;
![]() |
where corresponds to the box in the -th row and -th column of the -th tableau. For simplicity, we identify with its Young diagram .
Suppose . If and is a Young diagram of -partition of , then we call a removable node of . If and is a Young diagram of -partition of , then we call an addable node of .
Let be -partitions of ; write if
If and , we write . In particular, for , write if
We call the dominance order.
Let The elements of are also called nodes and the subsets of are called configurations of nodes. By definition, the Young diagrams of -partitions of are configurations of nodes.
We fix an element in and , where whenever . An -multicharge is a sequence . For , we define its residue to be . A loading is a sequence of integers such that for
Definition 2.1. [9, Definition 1.2] Let . We write if either
or
and .
Moreover, if , then we write .
Definition 2.2. [9, Definition 1.2] Let , we write if
We call the -dominance order.
Deleting the residue condition in the definition of -dominance order, we can get a weak version of it.
Definition 2.3. Let , we write if
We call the weak -dominance order.
Fix a loading , if for each , then we call a strongly separated loading.
Let be a configuration of nodes. For , we call the -diagonal of and the length of the -diagonal. Let be a node in the -diagonal of . We call the terminal node (respectively, head node) in the -diagonal of if (respectively, ) for each in the -diagonal of .
We give a rough description of the weak -dominance order by the length of diagonals.
Lemma 3.1. Let , then if and only if
Proof. Firstly, let us prove the necessity. Assume to be an integer such that
Since , hence there exists an integer such that
● the -diagonal of is non-empty, and
● , the -diagonal of is empty.
Let be the head node in the -diagonal of ; then we have
This contradicts to .
Next, let us prove the sufficiency. Suppose for all . Let be a node in the -diagonal of and be the head node in the -diagonal of . If , then
If , then
If , then
If , then
Therefore, .
Remark 3.2. Suppose are strongly separated and . Let be a node in the -diagonal of and be a node in the -diagonal of . Then . In fact, is a multipartition of , hence
That is, the -component is completely separated from the -component .
For , we say that and are neighbors with the weak -dominance order if and there is no such that .
In [[10], Theorem 1.4.10], there is a characterization of partitions that are neighbors with the usual dominance order. In the following lemma, let us prove a similar combinatorial description of neighbors with weak -dominance order on partitions. Consequently, it will be clear that the weak -dominance order coincides with the usual dominance order on partitions.
Lemma 3.3. Suppose and , then are neighbors with the weak -dominance order if and only if there exist positive integers such that one of the following and occurs, where
,
.
Proof. Let and be different integers. For , we have if and only if . Therefore, for each , we have if and only if . Hence, for simplicity, we assume . By this assumption, node lies in the -diagonal.
First, let us prove the necessity. Assume to be partitions of and there exist no such that . Define . Then is well defined since . Define . Then is well defined since . By definition, . Combining with Lemma 3.1, we derive
(3.4) |
and
(3.5) |
We will give the proof of necessity in 3 steps:
Step 1. Let be the terminal node in the -diagonal of . Let us prove and is the last node in the -th row of .
If , let us prove . We should prove the -diagonal and -diagonal of is like
![]() |
where and are the -diagonal of and are the -diagonal of . If , then we derive , hence . Then the -diagonal and -diagonal of is like
![]() |
where , and are the -diagonal of , while and are the -diagonal of . This contradicts that is the terminal node in the -diagonal of ; therefore, . Similarly, one can prove . If , by (3.4), we have ; this contradicts , hence . If , then . Then the -diagonal and -diagonal of are like
![]() |
where and are the -diagonal of and are the -diagonal of . This contradicts to and . Therefore, . By (3.4), we have , hence . So we derive and . Hence, the -diagonal and -diagonal of are like
![]() |
where are the -diagonal of and , are the -diagonal of . The -diagonal and -diagonal of are like
![]() |
where , are the -diagonal of and are the -diagonal of . Therefore . Moreover, is the last node in the -th row of .
For the case when , the discussion is tedious and similar to that of , so we don't show it here again.
Step 2. Let be the terminal node in the -diagonal of . Let us prove and .
If , let us prove . We should prove the -diagonal and -diagonal of are like
![]() |
where and are the -diagonal of and are the -diagonal of . If , then , hence . The -diagonal and -diagonal of are like
![]() |
where , and are the -diagonal of and , are the -diagonal of . This contradicts that is the terminal node in the -diagonal of . Therefore, . Similarly, we can prove . If , by (3.5), we have This contradicts to . If , then Then the -diagonal and -diagonal of are like
![]() |
where and are the -diagonal of and are the -diagonal of . This contradicts to . Therefore, , by (3.5), we have Therefore, we derive Hence, Then the -diagonal and -diagonal of are like
![]() |
where and are the -diagonal of and are the -diagonal of . The -diagonal and -diagonal of are like
![]() |
where are the -diagonal of and are the -diagonal of . Therefore, we have . Next, let us prove . If , since and is the last node in the -th row of , so we have , hence , this contradicts to . If , since , then , where . Since is the last node in the -th row of , so . Moreover, since , so lies in the -diagonal of and , this contradicts to . Therefore, we derive .
For the case when , the discussion is also tedious and similar to that of , so we do not show it here again.
Step 3. Now we have proved , and . Hence
is a partition of . Let , and , . Then is the terminal node in the -diagonal of , and is the terminal node in the -diagonal of . We can obtain from by removing to . Since , , hence and . So we have . Next, let us prove . Since , so , hence and Since , so and . Hence . Therefore,
Combining with the choice of and Lemma 3.1, we derive . Hence . Since and are neighbors with , so we have .
Finally, let us prove or . Otherwise, suppose and , then and . Let . If , then , let . Since , hence, this contradicts that and are neighbors with . If , then , let
Since then , this contradicts that and are neighbors with . Therefore, or . Now we complete the proof of necessity.
Next, let us prove the sufficiency. Suppose and there exist positive integers satisfying
, or
.
Let such that and are neighbors with . Let us prove . Let , , it is clear . By assumption, can be obtained from by removing to . By Lemma 3.1 and the the choice of , we have
(3.6) |
By the necessity of this lemma, there exist integers such that
Let , it is clear . In other words, can be obtained from by removing to . Combining with (3.6), we know .
If occurs, , the -diagonal and -diagonal of are like
![]() |
where are the -diagonal and are the -diagonal. The -diagonal and -diagonal of are like
![]() |
where are the -diagonal and are the -diagonal. By the above arguments, we have , . Since the addable node and removable node are unique for the -diagonal and -diagonal of , respectively. Hence, and .
If occurs, and , the -diagonal and -diagonal of are like
![]() |
where are the -diagonal and nodes are the -diagonal. The -diagonal and -diagonal of are like
![]() |
where are the -diagonal and are the -diagonal. By the above arguments, we have . Since the addable node and removable node are unique for the -diagonal and -diagonal of respectively. Hence, , and .
Now we can give a combinatorial description of neighbors with weak -dominance order on multipartitions.
Proposition 3.7. Suppose be strongly separated, and be -partitions of with . Then are neighbors with the weak -dominance order if and only if one of , , and occurs, where
there exists such that
there exist and such that
there exist and such that
Proof. Let us prove the necessity. We assume and are -partitions of with and there exists no such that . Define
then and for all . Since and is strongly separated, combining with Lemma 3.1 and Remark 3.2, we have
(3.8) |
Hence .
Suppose , then . Set , let us prove . Otherwise, assume . Let , where
Since , so . Let us prove . Let
Where . Define
can be obtained from by removing to . The Young diagrams of and are like
![]() |
By the construction of , we have for all . By Remark 3.2 and the choice of , we have
By Lemma 3.1, we derive
(3.9) |
(3.10) |
and
If , then there exists such that
(3.11) |
If , by (3.9)–(3.11), we have
hence . So and hence , this contradicts to . If , by (3.9)–(3.11), we have
then and ; this contradicts to . Therefore . Since , hence . So we derive
This contradicts that and are neighbors with . So we have .
Let , where
and , where
Let
and
Let , by Remark 3.2, we have . Since , so is the unique node in the -diagonal of and is the unique node in the -diagonal of . That is, can be obtained from by removing the node to . From the point of Young's diagram
![]() |
By Lemma 3.1, we have . Next, let us prove . By Lemma 3.1, we have
Moreover, by (3.8) and the assumption , we have
Combining with Remark 3.2 and the definition of , we derive
where . If , then we have proved
Therefore, . If , suppose , there exists some such that
On the other hand, by the definition of and , we have
this contradicts to the choice of .
So we derive , then . Since are neighbors with , we derive . That is, and satisfy .
Suppose . Let , then , so since and are neighbors with . Hence . Let , then and are partitions of with . If there exist partition of with , then , satisfy , this contradicts that and are neighbors with . So and are neighbors with . Applying the necessity of Lemma 3.3 to and , we derive that and satisfy either or .
Next, let us prove the sufficiency. Suppose and are -partitions of with and one of holds. Suppose be a -partition of with and are neighbors with . Now let us prove .
If holds, let and . We have . Moreover, by Remark 3.2, Lemma 3.1, and the choice of , we derive
Therefore,
(3.12) |
We claim for all ; otherwise, there must be or , this contradicts (3.12). If , then and ; this contradicts . Therefore , hence , and .
If or holds. Combining with the choice of , we have
Apply the sufficiency of Lemma 3.3 to and ; we derive and are neighbors with ; hence, and .
Now we can give the relationship between dominance order and weak -dominance order on multipartitions.
Theorem 4.1. Suppose and are strongly separated. Then if and only if .
Proof. The conclusion is clear by Proposition 3.7 and [11, Lemma 6.3].
For , we define to be a multi-set. According to Definitions 2.2 and 2.3, by a trivial discussion, one can prove and whenever . Finally, as a corollary of Theorem 4.1, we obtain the relationship between dominance order and -dominance order.
Theorem 4.2. Suppose and be strongly separated. If , then and .
We point out that the inverse of Theorem 4.2 is not true. We can give a counterexample as follows:
Example 4.3. Let , , , , is strongly separated. Let , , the Young diagrams with residue are as follows:
![]() |
On one hand, and . On another hand, let ; we have and
hence .
In this paper, we prove that the weak -dominance order coincides with the dominance order on multipartitions, whenever the loading is strongly separated. As a corollary, we prove that the -dominance order is stronger than the usual dominance order on multipartitions, whenever the loading is strongly separated.
The author declares he has not used Artificial Intelligence (AI) tools in the creation of this article.
The author was supported by the Natural Science Foundation of Shandong Province of China (No. ZR2023QA093) and the Doctoral Research Start-up Foundation of Shandong Jianzhu University (No. X22021Z). The author appreciates professor Jun Hu and Zhankui Xiao for their helpful discussions. The author also appreciates the reviewers for their helpful comments.
The author declares no conflicts of interest in this paper.
[1] | European Commission, Directive of the European Parliament and of the Council on the Reduction of the Impact of Certain Plastic Products on the Environment. The European Parliament and the Council of the European Union, 2019. Available from: https://www.legislation.gov.uk/eudr/2019/904. |
[2] | UK Government, A Green Future: Our 25 Year Plan to Improve the Environment. UK Government, 2018. Available from: https://assets.publishing.service.gov.uk/government/uploads/system/uploads/attachment_data/file/693158/25-year-environment-plan.pdf. |
[3] | Carrington D, India Will Abolish all Single-use Plastic by 2022, Vows Narendra Modi. The Guardian, 2018. Available from: https://www.theguardian.com/environment/2018/jun/05/india-will-abolish-all-single-use-plastic-by-2022-vows-narendra-modi. |
[4] |
Eze WU, Madufor IC, Onyeagoro GN, et al. (2020) The effect of Kankara zeolite-Y-based catalyst on some physical properties of liquid fuel from mixed waste plastics (MWPs) pyrolysis. Polym Bull 77: 1399–1415. https://doi.org/10.1007/s00289-019-02806-y doi: 10.1007/s00289-019-02806-y
![]() |
[5] | Akter N, Acott RE, Sattar MG, et al. (1997) Medical waste disposal at BRAC health centres: an environmental study. Res Rep 13: 151–179. |
[6] | Asante B, Yanful E, Yaokumah B (2014) Healthcare waste management; its impact: a case study of the Greater Accra Region, Ghana. IJSTR 3: 106–112. |
[7] | WHO, Guidelines for Safe Disposal of Unwanted Pharmaceuticals in and after Emergencies. World Health Organization, 1999. Available from: https://apps.who.int/iris/handle/10665/42238. |
[8] |
Tsakona M, Anagnostopoulou E, Gidarakos E (2007) Hospital waste management and toxicity evaluation: a case study. Waste Manage 27: 912–920. https://doi.org/10.1016/j.wasman.2006.04.019 doi: 10.1016/j.wasman.2006.04.019
![]() |
[9] |
Hantoko D, Li X, Pariatamby A, et al. (2021) Challenges and practices on waste management and disposal during COVID-19 pandemic. J Environ Manage 286: 112140. https://doi.org/10.1016/j.jenvman.2021.112140 doi: 10.1016/j.jenvman.2021.112140
![]() |
[10] |
Vanapalli KR, Sharma HB, Ranjan VP, et al. (2021) Challenges and strategies for effective plastic waste management during and post COVID-19 pandemic. Sci Total Environ 750: 141514. https://doi.org/10.1016/j.scitotenv.2020.141514 doi: 10.1016/j.scitotenv.2020.141514
![]() |
[11] |
Yousefi M, Oskoei V, Jafari AJ, et al. (2021) Municipal solid waste management during COVID-19 pandemic: effects and repercussions. Environ Sci Pollut R 28: 32200–32209. https://doi.org/10.1007/s11356-021-14214-9 doi: 10.1007/s11356-021-14214-9
![]() |
[12] |
Mahmood QK, Jafree SR, Mukhtar S, et al. (2021) Social media use, self-efficacy, perceived threat, and preventive behavior in times of COVID-19: results of a cross-sectional study in Pakistan. Front Psychol 12: 2354. https://doi.org/10.3389/fpsyg.2021.562042 doi: 10.3389/fpsyg.2021.562042
![]() |
[13] |
Van Fan Y, Jiang P, Hemzal M, et al. (2021) An update of COVID-19 influence on waste management. Sci Total Environ 754: 142014. https://doi.org/10.1016/j.scitotenv.2020.142014 doi: 10.1016/j.scitotenv.2020.142014
![]() |
[14] |
Singh N, Tang Y, Ogunseitan OA (2020) Environmentally sustainable management of used personal protective equipment. Environ Sci Technol 54: 8500–8502. https://doi.org/10.1021/acs.est.0c03022 doi: 10.1021/acs.est.0c03022
![]() |
[15] | CDC, Guidelines for Selection and Use of Personal Protective Equipment (PPE) in Health Settings. Centers for Disease Control, 2020. Available from: https://www.cdc.gov/hai/pdfs/ppe/ppeslides6-29-04.pdf. |
[16] | Revoir WH (1997) Respiratory Protection Handbook, New York: Lewis Publisher. |
[17] | CDRH, Guidance for Industry and FDA Staff: Surgical Masks—Premarket Notification (510(k)) Submissions. Center for Devices and Radiological Health, 2004. Available from: https://www.fda.gov/files/medical%20devices/published/Guidance-for-Industry-and-FDA-Staff--Surgical-Masks---Premarket-Notification-%5B510(k)%5D-Submissions--Guidance-for-Industry-and-FDA-(PDF-Version).pdf. |
[18] | Maturaporn T (1995) Disposable face mask with multiple liquid resistant layers. U.S. Patent, US5467765A. |
[19] | Herrick R, Demont J (1994) Industrial hygiene, In: Rosenstock L, Cullen MR, Textbook of Clinical Occupational and Environmental Medicine, 1 Ed., Philadelphia: WB Saunders Company, 169–193. |
[20] |
Mooibroek H, Cornish K (2000) Alternative sources of natural rubber. Appl Microbiol Biot 53: 355–365. https://doi.org/10.1007/s002530051627 doi: 10.1007/s002530051627
![]() |
[21] |
Wei Y, Zhang H, Wu L, et al. (2017) A review on characterization of molecular structure of natural rubber. MOJ Polym Sci 1: 197–199. https://doi.org/10.15406/mojps.2017.01.00032 doi: 10.15406/mojps.2017.01.00032
![]() |
[22] | Barbara J (2002) Single use vs reusable gowns and drapes. Infection Control Today 1: 3234–3237. |
[23] | Leonas KK (2005) Microorganism protection, In: Scott RA, Textiles for Protection, 1 Ed., Boca Raton: Woodhead Publishing-CRC Press, 441–464. https://doi.org/10.1533/9781845690977.2.441 |
[24] |
Whyte W, Carson W, Hambraeus A (1989) Methods for calculating the efficiency of bacterial surface sampling techniques. J Hosp Infect 13: 33–41. https://doi.org/10.1016/0195-6701(89)90093-5 doi: 10.1016/0195-6701(89)90093-5
![]() |
[25] |
Kilinc FS (2015) A review of isolation gowns in healthcare: fabric and gown properties. J Eng Fibers Fabr 10: 180–190. https://doi.org/10.1177/155892501501000313 doi: 10.1177/155892501501000313
![]() |
[26] | Gupta BS (1988) Effect of structural factors on absorbent characteristics of non-wovens. Tappi J 71: 147–152. |
[27] | Africa News of Sunday, Man Carelessly Disposing PPE by Roadside. GhanaWeb, 2020. Available from: https://www.ghanaweb.com/GhanaHomePage/audio/Abba-Kyari-Everyone-at-the-burial-to-be-tested-for-coronavirus-Public-Health-Dept-928402. |
[28] | Isaac K, Africas pressing need for waste management. DW Report, 2017. Available from: https://www.dw.com/en/africas-pressing-need-for-waste-management/a-39623900. |
[29] | SCMP, Coronavirus Leaves China with Mountains of Medical Waste. South China Morning Post, 2020. Available from: https://amp.scmp.com/news/china/society/article/3074722/coronavirus-leaves-china-mountains-medical-waste. |
[30] | James M, Could the U.S., Like China, Face a Medical Waste Crisis? E & E Newsreporter, 2020. Available from: https://www.eenews.net/articles/could-the-u-s-like-china-face-a-medical-waste-crisis/. |
[31] |
Jang YC, Lee C, Yoon OS, et al. (2006) Medical waste management in Korea. J Environ Manage 80: 107–115. https://doi.org/10.1016/j.jenvman.2005.08.018 doi: 10.1016/j.jenvman.2005.08.018
![]() |
[32] |
Wu A, Peng Y, Huang B, et al. (2020) Genome composition and divergence of the novel coronavirus (2019-nCoV) originating in China. Cell Host Microbe 27: 325–328. https://doi.org/10.1016/j.chom.2020.02.001 doi: 10.1016/j.chom.2020.02.001
![]() |
[33] | World Health Organization, Preferred Product Characteristics for Personal Protective Equipment for the Health Worker on the Frontline Responding to Viral Hemorrhagic Fevers in Tropical Climates. WHO, 2018. Available from: https://apps.who.int/iris/bitstream/handle/10665/272691/9789241514156-eng.pdf. |
[34] | World Health Organization, WHO Director-General's Opening Remarks at the Media Briefing on Covid-19—19 June 2020. WHO, 2020. Available from: https://www.who.int/director-general/speeches/detail/who-director-general-s-opening-remarks-at-the-media-briefing-on-covid-19---19-june-2020. |
[35] | World Health Organization, Shortage of Personal Protective Equipment Endangering Health Workers Worldwide. WHO, 2020. Available from: https://www.who.int/news/item/03-03-2020-shortage-of-personal-protective-equipment-endangering-health-workers-worldwide. |
[36] | World Health Organization, Health-care Waste. WHO, 2018. Available from: https://www.who.int/news-room/fact-sheets/detail/health-care-waste. |
[37] | Ugom M (2020) Managing medical wastes during the Covid-19 pandemic in Nigeria. Int J Waste Resour 10: 386. |
[38] |
Amasuomo E, Baird J (2016) Solid waste management trends in Nigeria. JMS 6: 35. https://doi.org/10.5539/jms.v6n4p35 doi: 10.5539/jms.v6n4p35
![]() |
[39] | Babs-Shomoye F, Kabir R (2016) Health effects of solid waste disposal at a dumpsite on the surrounding human settlements. JPHDC 2: 268–275. |
[40] |
Eze WU, Madufor IC, Onyeagoro GN, et al. (2021) Study on the effect of Kankara zeolite-Y-based catalyst on the chemical properties of liquid fuel from mixed waste plastics (MWPs) pyrolysis. Polym Bull 78: 377–398. https://doi.org/10.1007/s00289-020-03116-4 doi: 10.1007/s00289-020-03116-4
![]() |
[41] |
Eze WU, Umunakwe R, Obasi HC, et al. (2021) Plastics waste management: A review of pyrolysis technology. Clean Technol Recy 1: 50–69. https://doi.org/10.3934/ctr.2021003 doi: 10.3934/ctr.2021003
![]() |
[42] |
Kaminsky W, Mennerich C, Zhang Z (2009) Feedstock recycling of synthetic and natural rubber by pyrolysis in a fluidized bed. J Anal Appl Pyrol 85: 334–337. https://doi.org/10.1016/j.jaap.2008.11.012 doi: 10.1016/j.jaap.2008.11.012
![]() |
[43] |
Wang J, Jiang J, Wang X, et al. (2019) Catalytic conversion of rubber wastes to produce aromatic hydrocarbons over USY zeolites: Effect of SiO2/Al2O3 mole ratio. Energ Convers Manage 197: 111857. https://doi.org/10.1016/j.enconman.2019.111857 doi: 10.1016/j.enconman.2019.111857
![]() |
[44] |
Abbas-Abadi MS, Haghighi MN, Yeganeh H, et al. (2014) Evaluation of pyrolysis process parameters on polypropylene degradation products. J Anal Appl Pyrol 109: 272–277. https://doi.org/10.1016/j.jaap.2014.05.023 doi: 10.1016/j.jaap.2014.05.023
![]() |
[45] |
Ahmad I, Khan MI, Khan H, et al. (2015) Pyrolysis study of polypropylene and polyethylene into premium oil products. Int J Green Energy 12: 663–671. https://doi.org/10.1080/15435075.2014.880146 doi: 10.1080/15435075.2014.880146
![]() |
[46] |
Fakhrhoseini S, Dastanian M (2013) Pyrolysis of LDPE, PP and PET plastic wastes at different conditions and prediction of products using NRTL activity coefficient model. J Chem 2013: 487676. https://doi.org/10.1155/2013/487676 doi: 10.1155/2013/487676
![]() |
[47] |
Eze WU, Madufor IC, Onyeagoro GN, et al. (2020) The effect of Kankara zeolite-Y-based catalyst on some physical properties of liquid fuel from mixed waste plastics (MWPs) pyrolysis. Polym Bull 77: 1399–1415. https://doi.org/10.1007/s00289-019-02806-y doi: 10.1007/s00289-019-02806-y
![]() |
[48] |
Donaj PJ, Kaminsky W, Buzeto F, et al. (2012) Pyrolysis of polyolefins for increasing the yield of monomers' recovery. Waste Manage 32: 840–846. https://doi.org/10.1016/j.wasman.2011.10.009 doi: 10.1016/j.wasman.2011.10.009
![]() |
[49] |
Pratama NN, Saptoadi H (2014) Characteristics of waste plastics pyrolytic oil and its applications as alternative fuel on four cylinder diesel engines. Int J Renewable Energy Dev 3: 13–20. https://doi.org/10.14710/ijred.3.1.13-20 doi: 10.14710/ijred.3.1.13-20
![]() |
[50] |
Li H, Jiang X, Cui H, et al. (2015) Investigation on the co-pyrolysis of waste rubber/plastics blended with a stalk additive. J Anal Appl Pyrol 115: 37–42. https://doi.org/10.1016/j.jaap.2015.07.004 doi: 10.1016/j.jaap.2015.07.004
![]() |
[51] |
Hussain Z, Khan A, Naz MY, et al. (2021) Borax-catalyzed valorization of waste rubber and polyethylene using pyrolysis and copyrolysis reactions. Asia-Pac J Chem Eng 16: e2696. https://doi.org/10.1002/apj.2696 doi: 10.1002/apj.2696
![]() |
[52] |
Park J, Díaz-Posada N, Mejía-Dugand S (2018) Challenges in implementing the extended producer responsibility in an emerging economy: The end-of-life tire management in Colombia. J Cleaner Prod 189: 754–762. https://doi.org/10.1016/j.jclepro.2018.04.058 doi: 10.1016/j.jclepro.2018.04.058
![]() |
[53] |
Banguera LA, Sepúlveda JM, Ternero R, et al. (2018) Reverse logistics network design under extended producer responsibility: The case of out-of-use tires in the Gran Santiago city of Chile. Int J Prod Econ 205: 193–200. https://doi.org/10.1016/j.ijpe.2018.09.006 doi: 10.1016/j.ijpe.2018.09.006
![]() |
[54] |
Zarei M, Taghipour H, Hassanzadeh Y (2018) Survey of quantity and management condition of end-of-life tires in Iran: a case study in Tabriz. J Mater Cycles Waste Manage 20: 1099–1105. https://doi.org/10.1007/s10163-017-0674-5 doi: 10.1007/s10163-017-0674-5
![]() |
[55] |
Yagboyaju DA, Akinola AO (2019) Nigerian state and the crisis of governance: A critical exposition. SAGE Open 9: 1–10. https://doi.org/10.1177/2158244019865810 doi: 10.1177/2158244019865810
![]() |
[56] | Leguil-Bayart JF (2009) The State in Africa: the Politics of the Belly, Oxford: Polity Press. |
[57] | Uzodikeo UO (2009) Leadership and governance in Africa. AFFRIKA Journal of Politics, Economics and Society 1: 3–9. |
[58] | Renault V (2022) SWOT analysis: strengths, weaknesses, opportunities, and threats, Community Tool Box: Assessing Community Needs and Resources. Kansas: The University of Kansas. |
[59] | Muniafu M, Kimani NN, Mwangi J (2013) Renewable Energy Governance: Complexities and Challenges, New York: Springer, 397. |
[60] |
Patil DP, Bakthavachalu B, Schoenberg DR (2014) Poly (A) polymerase-based poly (A) length assay. Methods Mol Biol 1125: 13–23. https://doi.org/10.1007/978-1-62703-971-0_2 doi: 10.1007/978-1-62703-971-0_2
![]() |
[61] | Lino FAM, Ismail KAR (2017) Recycling and thermal treatment of MSW in a developing country. IOSRJEN 7: 2278–8719. |
[62] |
Aubert J, Husson B, Saramone N (2006) Utilization of municipal solid waste incineration (MSWI) fly ash in blended cement: Part 1: Processing and characterization of MSWI fly ash. J Hazard Mater 136: 624–631. https://doi.org/10.1016/j.jhazmat.2005.12.041 doi: 10.1016/j.jhazmat.2005.12.041
![]() |
[63] |
Panda AK, Singh RK, Mishra DK (2010) Thermolysis of waste plastics to liquid fuel: A suitable method for plastic waste management and manufacture of value added products—A world prospective. Renewable Sustainable Energy Rev 14: 233–248. https://doi.org/10.1016/j.rser.2009.07.005 doi: 10.1016/j.rser.2009.07.005
![]() |
[64] | Alonso-Torres B, Rodrigez-Martinez A, Domínguez-Patino ML (2010) Design of municipal solid waste incinerator based on hierarchical methodology. Chem Eng Trans 21: 1471–1476. |
[65] | World Health Organization, Findings of an Assessment of Small-scale Incinerators for Healthcare Waste. WHO, 2004. Available from: https://apps.who.int/iris/handle/10665/68775. |
[66] |
Das AK, Islam N, Billah M, et al. (2021) COVID-19 pandemic and healthcare solid waste management strategy—A mini-review. Sci Total Environ 778: 146220. https://doi.org/10.1016/j.scitotenv.2021.146220 doi: 10.1016/j.scitotenv.2021.146220
![]() |
[67] | Tsukiji M, Gamaralalage PJD, Pratomo ISY, et al. (2020) Waste management during the COVID-19 pandemic from response to recovery. United Nations Environment Programme, International Environmental Technology Centre (IETC) IGES Center Collaborating with UNDP on Environmental Technologies (CCET). |
[68] | Chu LM (2008) Landfills, In: Jorgensen SE, Fath B, Encyclopedia of Ecology, Netherlands: Elsevier, 2099–2103. https://doi.org/10.1016/B978-008045405-4.00345-1 |
[69] | Stauffer B, Landfills, SSWM—Find Tools for Sustainable Sanitation and Water Management. International Solid Waste Association Report, 2020. Available from: https://sswm.info/water-nutrient-cycle/wastewater-treatment/hardwares/solid-waste/landfills. |
[70] | Waste Management Bioreactor Program Report, The Bioreactor Landfill—Next Generation Landfill Technology. EPA, 2004. Available from: https://www.epa.gov/landfills/bioreactor-landfills. |
[71] | UNEP, A Directory of Environmentally Sound Technologies for the Integrated Management of Solid, Liquid and Hazardous Waste for Small Island Developing States (SIDS) in the Pacific Region. International Waters Learning Exchange & Resource Network Report, 2021. Available from: https://iwlearn.net/documents/3901. |
[72] |
Fereja WM, Chemeda DD (2021) Status, characterization, and quantification of municipal solid waste as a measure towards effective solid waste management: The case of Dilla Town, Southern Ethiopia. J Air Waste Manage 72: 187–201. https://doi.org/10.1080/10962247.2021.1923585 doi: 10.1080/10962247.2021.1923585
![]() |
[73] |
Okwesili J, Iroko C (2016) Urban solid waste management and environmental sustainability in Abakaliki Urban, Nigeria. Eur Sci J 12: 160. https://doi.org/10.19044/esj.2016.v12n23p155 doi: 10.19044/esj.2016.v12n23p155
![]() |
[74] |
Ojuri OO, Ajijola TO, Akinwumi II (2018) Design of an engineered landfill as possible replacement for an existing dump at Akure, Nigeria. African J Sci Technol Innov Dev 10: 835–843. https://doi.org/10.1080/20421338.2018.1523827 doi: 10.1080/20421338.2018.1523827
![]() |
[75] | Sonia A, Many in Northern Syria Live off Rubbish Dumps. The Pulse of the Middle East, Al-Monitor, 2020. Available from: https://www.al-monitor.com/originals/2020/03/syria-north-chidlren-women-begging-garbage-collect-poverty.html. |
[76] |
De Feo G, De Gisi S, Williams ID (2013) Public perception of odour and environmental pollution attributed to MSW treatment and disposal facilities: A case study. Waste Manage 33: 974–987. https://doi.org/10.1016/j.wasman.2012.12.016 doi: 10.1016/j.wasman.2012.12.016
![]() |
[77] |
Kumar S, Gaikwad SA, Shekdar AV, et al. (2004) Estimation method for national methane emission from solid waste landfills. Atmos Environ 38: 3481–3487. https://doi.org/10.1016/j.atmosenv.2004.02.057 doi: 10.1016/j.atmosenv.2004.02.057
![]() |
[78] |
Njoku PO, Edokpayi JN, Odiyo JO (2019) Health and environmental risks of residents living close to a landfill: A case study of Thohoyandou Landfill, Limpopo Province, South Africa. Int J Environ Res Public Health 16: 2125. https://doi.org/10.3390/ijerph16122125 doi: 10.3390/ijerph16122125
![]() |
[79] | Toyese O, Ademola O, Olusanya JJ (2021) Preliminary investigation on the screening of selected metallic oxides, M2O3 (M = Fe, La, and Gd) for the capture of carbon monoxide using a computational approach. JESC 3: 1–14. |
[80] | Pakistan Today, WB to Assist in Making Landfill Site for Karachi. Pakistan Today, 2019. Available from: https://archive.pakistantoday.com.pk/2019/10/09/wb-to-assist-in-making-landfill-site-for-karachi/. |
[81] | WOIMAD, Rowning in Waste—Case Accra, Ghana. WOIMA Corporation, 2021. Available from: https://woimacorporation.com/drowning-in-waste-case-accra-ghana/. |
[82] |
Galadima A, Garba ZN, Ibrahim BM, et al. (2011) Biofuels production in Nigeria: The policy and public opinions. J Sustain Dev 4: 22–31. https://doi.org/10.5539/jsd.v4n4p22 doi: 10.5539/jsd.v4n4p22
![]() |
[83] | Toyese O, Jibiril BEY (2016) Design and feasibility study of a 5MW bio-power plant in Nigeria. Int J Renew Energy Res 6: 1496–1505. |