Airborne volatile organic compounds at an e-waste site in Ghana: Source apportionment, exposure and health risks

https://doi.org/10.1016/j.jhazmat.2021.126353Get rights and content

Highlights

  • This is the first study to assess both personal and ambient VOCs in e-waste site.

  • VOC levels in personal samples were much higher than that in fixed-site samples.

  • Local industrial use, fuel evaporation and combustion were the main sources.

  • VOC emissions from the e-waste site polluted the neighboring environment.

  • Health risks exceeded guideline levels and were mainly due to naphthalene and benzene.

Abstract

Informal e-waste recycling processes emit various air pollutants. While there are a number of pollutants of concern, little information exists on volatile organic compounds (VOCs) releases at e-waste sites. To assess occupational exposures and estimate health risks, we measured VOC levels at the Agbogbloshie e-waste site in Ghana, the largest e-waste site in Africa, by collecting both fixed-site and personal samples for analyzing a wide range of VOCs. A total of 54 VOCs were detected, dominated by aliphatic and aromatic compounds. Mean and median concentrations of the total target VOCs were 46 and 37 μg/m3 at the fixed sites, and 485 and 162 μg/m3 for the personal samples. Mean and median hazard ratios were 2.1 and 1.4, respectively, and cancer risks were 4.6 × 10-4 and 1.5 × 10-4. These risks were predominantly driven by naphthalene and benzene; chloroform and formaldehyde were also high in some samples. Based on the VOC composition, the major sources were industry, fuel evaporation and combustion. The concentration gradient across sites and the similarity of VOC profiles indicated that the e-waste site emissions reached neighboring communities. Our results suggest the need to protect e-waste workers from VOC exposure, and to limit emissions that can expose nearby populations.

Introduction

Electrical and electronic equipment (EEE) is indispensable and ubiquitous in modern societies. Globally, EEE production reached 53.6 million tons in 2019, or 7.3 kg/year per capita, and is estimated to increase by 2.5 million tons/year and reach 74.7 million tons by 2030 (Forti et al., 2020). This massive production has generated a parallel stream of EEE waste or e-waste. In the relatively small West African country of Ghana, e-waste recycling has become an important revenue source in the informal economy (Asibey et al., 2020). While Ghana has enacted e-waste legislation and is trying to adopt the Basel Convention that would restrict e-waste imports, as well as establish funds to support related facilities and support research and public education addressing recycling (Daum et al., 2017), e-waste imports have grown from about 149,000 tons in 2009 to an estimated 300,000–840,000 tons in 2020 (Amoyaw-Osei et al., 2011). Described as Africa's largest electronic waste dumpsite, Agbogbloshie in central Accra, the capital of Ghana, has attracted international attention. Approximately 4500–6000 workers and another 1600 indirectly work at this well-organized scrapyard (Grant and Oteng-Ababio, 2012), where e-waste is processed using rudimentary methods, e.g., manual stripping to remove electronic boards for resale, open burning of wires to recover metals (copper, aluminum, iron), and open dumping of bulk components such as cathode-ray tubes (CRTs) (Ackah, 2017). Enforcement of environmental and workplace health and safety regulations is largely absent.

EEE itself can contain hazardous substances, including toxic metals (e.g., mercury, cadmium, lead) and persistent organic pollutants (polychlorinated biphenyls or PCBs, flame retardants). Open burning at e-waste sites can emit these chemicals, as well as polycyclic aromatic hydrocarbons (PAHs), volatile organic compounds (VOCs) and particulate matter (PM) (An et al., 2014, Tue et al., 2017, Wang et al., 2020). Chemicals found at e-waste sites have been associated with DNA damage, tissue damage, increased glucose levels, reproductive and genital disorders, and carcinogenicity (Ji et al., 2010, Li et al., 2019, McDonald, 2002, Zani et al., 2013). Attention to pollutant exposure and health impacts associated with e-waste recycling has increased (Asante et al., 2012, Bruce-Vanderpuije et al., 2019, Feldt et al., 2014, Moeckel et al., 2020), and stress, body aches, shortness of breath, chest pain, cough and dizziness have been reported among e-waste workers and in neighboring communities (Amphalop et al., 2020, Burns et al., 2016, Li et al., 2008, Ma et al., 2013, Yu et al., 2017).

While PM and metals measurements have been reported at e-waste sites in Ghana and elsewhere (Ackah, 2019, Kwarteng et al., 2020, Laskaris et al., 2019), information on VOCs is scarce. VOCs include a diverse set of chemicals, e.g., formaldehyde, benzene, chloroform, toluene, and ethylbenzene, and they include many known or suspected toxicants that cause irritation to eyes, skin and nose, damage to the respiratory system, liver and kidney; reproductive effects, and cancer (Anderson et al., 2007, Wolkoff et al., 2000, Wolkoff et al., 2006). Several e-waste recycling processes, especially heating and burning, have been reported to produce extremely high concentrations of VOCs, especially aromatic hydrocarbons (An et al., 2014).

This study focuses on VOC exposures at e-waste sites with the overall objective of characterizing levels and exposures to a wide set of VOCs at the Agbogbloshie e-waste site. We used both fixed-site and personal measurements at the e-waste site, as well as measurements at up- and down-wind sites, to identify background levels and evaluate possible effects on neighboring communities. We examined the distributions of VOC concentrations, identified possible sources, and assessed exposure and health risks.

Section snippets

Sampling sites and subject recruitment

The Agbogbloshie e-waste site and scrap yard is about 1 km from central Accra (Ghana’s capital, 2.5 million inhabitants), and it forms part of the city’s South Industrial Area. The site is adjacent to densely populated residential and commercial areas, and ~144,000 residents live in the 16 km2 Asiedu Keteke sub-metropolitan area, a commercial hub. Another light industrial area is located north of Accra, and a heavy industrial area is ~41 km to the east. More details are provided elsewhere (

VOC levels in samples

A total of 54 VOCs was detected (Table S1). The mean ± standard deviation (sd) and median TTVOC levels were 102 ± 289 and 43 μg/m3 respectively, suggesting a right-skewed distribution. Detection frequencies (DF) exceeded 50% for 18 VOCs, including alkanes and aromatics (n-hexane, benzene, n-heptane, toluene, ethylbenzene, p- and m -xylene, n-nonane, styrene, o-xylene, 1,3,5-trimethylbenzene, n-decane, 1,2,4-trimethylbenzene, n-undecane, naphthalene, n-tridecane, and n-tetradecane), as well as

Comparison to VOCs levels in literature

Relatively few studies have utilized personal monitoring of VOCs in community settings, and no such monitoring was identified for e-waste workers globally. Table S3 summarizes studies in several countries utilizing personal monitoring. BTEX exposures averaged 34–43 µg/m3 among women in Cape Town, South Africa (Everson et al., 2019), much lower than in this study. In contrast, street cooks in Nigeria using biomass fuels experienced much higher levels of benzene and toluene than in the present

Conclusion

Informal e-waste recycling activities emit VOCs that expose workers and nearby communities. We detected a total of 54 VOCs in personal and fixed-site samples collected at the Agbogbloshie waste site in Ghana. VOC levels in personal samples from e-waste workers considerably exceeded levels at the fixed sites and resulted in risks that far exceeded reference levels, especially for cancer, largely due to naphthalene and benzene, and occasionally from chloroform and formaldehyde. The dominant VOC

CRediT authorship contribution statement

Nan Lin: Software, Validation, Formal analysis, Investigation, Data curation, Writing - original draft, Writing - review & editing, Visualization. Lawrencia Kwarteng: Software, Investigation, Data curation, Writing - review & editing. Christopher Godwin: Methodology, Investigation, Writing - review & editing. Sydni Warner: Writing - original draft, Writing - review & editing. Thomas Robins: Conceptualization, Methodology, Resources, Writing - review & editing, Supervision, Project

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

Funding for this research was from the West Africa-Michigan CHARTER in GEOHealth which is supported by the United States National Institutes of Health (NIH)/Fogarty International Center grants 1U2RTW010110–01 and 5U01TW010101, and from Canada’s International Development Research Center grant 108121–001. Additional support for this research was provided by grant P30ES017885 from the National Institute of Environmental Health Sciences, NIH. The content is solely the responsibility of the authors

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