Study of the chemical hazard in car body painting workshops in the city of Ouagadougou, Burkina Faso
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Study of the chemical hazard in car body painting workshops in the city of Ouagadougou, Burkina Faso Saybou Savadogo ( ssaybou0204@gmail.com ) Laboratoire National de Santé Publique, 09 BP: 24 Ouagadougou 09 Burkina Faso Salimata Traoré Laboratoire de toxicologie de l’environnement et santé, Université Joseph KI-ZERBO, 03 BP : 7021 Ouagadougou 03, Burkina Faso Sibiri Sylvain Rouamba Laboratoire National de Santé Publique, 09 BP: 24 Ouagadougou 09 Burkina Faso Abdoul Karim Sakira Laboratoire de toxicologie de l’environnement et santé, Université Joseph KI-ZERBO, 03 BP : 7021 Ouagadougou 03, Burkina Faso Adama Coulibaly Office de santé des travailleurs, 03 BP : 7021 Ouagadougou 03, Burkina Faso Boukary Sana Pharmacie Amirbouba, 07 BP : 5192 Ouagadougou 07, Burkina Faso Touridomon Issa Somé Laboratoire de toxicologie de l’environnement et santé, Université Joseph KI-ZERBO, 03 BP : 7021 Ouagadougou 03, Burkina Faso Research Article Keywords: Chemical hazard, paint, car bodywork, Burkina Faso Posted Date: April 25th, 2022 DOI: https://doi.org/10.21203/rs.3.rs-1573498/v1 License: This work is licensed under a Creative Commons Attribution 4.0 International License. Read Full License Page 1/10
Abstract Knowledge of the risks of chemicals remains low among most parts of the African population. This situation is further complicated by the widespread lack of reliable data and information on the toxicity and safe use of chemicals. The present study was conducted to describe the chemical hazards to which workers in auto body paint shops would be exposed. The cross-sectional and descriptive study was conducted in car body paint shops in the city of Ouagadougou. The data collection consisted of an inventory of the products, direct observation of the workers in the work situation, and interviews. A total of 17 chemical products were inventoried in all the car body paint shops. Of the 17 products inventoried, 15 were flammable solvents (88.23%), 2 (11.77%) were in paste form and 1 (5.88%) was an oxidizer. All the products were dangerous for health and among them 6 (35.29%) were dangerous for the environment according to their pictograms. These products were handled without special precautions. All these products present risks for human health and the environment. In view of the working conditions, there is a potential exposure of the workers to all the chemicals as well as the inhabitants of the nearby residential areas. Introduction Chemicals are used in a variety of products such as paints, inks, pesticides, degreasers, thinners and adhesives. These are used in many fields such as painting [1, 2]. According to the International Labour Organization (ILO), worker exposure to chemicals is estimated to cause 375,000 deaths each year [3], or more than 1,000 deaths per day worldwide. Two thirds of these deaths occur in developing countries [4]. In France, approximately 4.8 million tons of carcinogenic, mutagenic and reprotoxic substances were used in 2005 [5]. The 2002–2003 survey on medical surveillance of employee exposure to occupational risks showed that construction and public works workers were "more exposed to reprotoxic products, particularly lead and its derivatives" [6]. Knowledge of the hazards inherent to chemical products remains low in most components of the African population. This situation is more complicated by the general lack of reliable data and information on the toxicity and safe use of chemicals [7]. In Burkina Faso, there is an increase in the use and diversity of paint chemicals in auto body paint shops. This situation exposes workers to risks of acute intoxication, fire-explosion, or environmental pollution. They can also cause more insidious effects, after years of exposure of the worker to low doses, or even several years after the end of exposure [8]. Although the hazard of chemical intoxication is real, there are no data on chemical hazards among workers in car body paint shops in Burkina Faso. It therefore seems appropriate to carry out this study, the aim of which is to describe the chemical hazards to which workers in car body paint shops are exposed. Methods Type, period and study population This was a descriptive cross-sectional study that took place from June 20 to August 15, 2018. The study populations consisted of workers present in the auto body paint shops during our visit. Sampling In the absence of an official list of auto body paint shops in the informal sector, 6 districts (3, 6, 7, 9, 10, 11) of the 12 districts of the city of Ouagadougou were drawn at random. Five car body paint shops per district were selected, for a total of 30 shops in Page 2/10
the sample. Thus, auto body paint shops that were at least three months old and agreed to participate in the study when we visited were included in our study. Inventory of chemicals and characterization of their hazards The inventory of chemicals used for painting in car body paint shops in the city of Ouagadougou was done with the support of an inventory form developed for this study. From the labels of each chemical product, the name and pictograms were taken in order to characterize their danger for human health and the environment. Description of worker exposure conditions The data collection consisted of : - identifying the different workstations ; - then to verify the existence and use of collective and individual protection by direct observation of the personnel in real work situations ; - to verify the storage conditions of the products and the management of waste. Data collection tools and techniques An inventory form was used to list the products, a form describing the working conditions according to the workstations and an interview form were used to collect data related to the work environment. A pre-test was conducted to validate the data collection tools. The data collection technique consisted of an inventory of the products, direct observation of the workers in the work situation and interviews. Data processing and analysis The description of health and environmental hazards was based on the literature, because none of the car body paint shops had either a Safety Data Sheet (SDS) or a toxicological data sheet for the various products used. The data were analyzed using the epi info software in its version 7. Results Inventory of chemicals used in car body paint shops Twenty-one (21) workshops (67.75%) of the thirty-one workshops listed in our study area agreed to participate in the study. A total of 17 chemicals were inventoried in all the car body paint shops. Of the 17 products inventoried, 15 were flammable solvents (88.23%), 2 (11.77%) were in paste form and 1 (5.88%) was oxidizing (Table 1). All (100%) of the products were hazardous to human health and among them, 6 (35.29%) were hazardous to the environment according to their pictograms. Five (29.41%) products were made up of separate chemical substances against 12 (70.58%) mixtures of several chemical substances. Ninety-six (96) products repackaged in recovery boxes and not labelled were found in the workshops. Organization of the car body painting workshops and activities carried out per shift Three workstations were identified in all of the auto body paint shops: surface preparation (sanding, puttying, priming); paint coating and its components; and the secretary's station. However, only 3/21 (14.28%) of the auto body paint shops had a secretary position. Surface preparation exposure conditions Page 3/10
The work in this position primarily involves stripping of the old paint coating. This involves removing the old paint by scraping with abrasive paper. This operation produces dust which is inhaled by the operators. After stripping, the second step is to apply the filler and primer (containing styrene, bisphenol A, epoxy resin) and dibenzoyl peroxide to polish the bodywork to be painted. The operators work without any protection. The preparation of the surface of a vehicle in all the workshops varies between 5 to 7 days and the daily work lasts on average 9 hours. Exposure conditions at the paint coating station The paint coating of the prepared surfaces consists in the application of the paint. This application is done by the operator using a spray gun. The mixtures are made directly in the cup before their application. The spray gun releases solvent vapors and aerosols into the ambient work air. These vapors and aerosols are inhaled by the workers. The aerosols can also fall on the workers' skin. The paint coating takes 4 to 5 hours. In the 21 auto body paint shops, hand washing and equipment washing after work is done with organic solvents such as the mixture (Toluene-dichloromethane-methanol-tetrahydrofuran-acetone-ethyl acetate) used as a solvent for paint application. The average paint coating in all the workshops is one vehicle per week. This operation is carried out without wearing gloves, long-sleeved coats, chemical masks or goggles. However, only in 3 workshops out of 21, the operators used non-chemical masks of the nose-patch type adapted rather to the protection against the inhalation of microorganisms (F1 or KN95). Secretarial job exposure conditions The role of the secretaries is to receive customers, enter invoices and receipts. It existed in only 3 workshops out of the 21 at the time of our visit. These offices are adjacent to the other two workstations. The secretaries in the offices are not in direct contact with the chemicals. They are exposed through the ambient atmosphere containing solvent vapors and aerosols released during paint coating. The secretaries work 7 hours a day and 6 days a week. Storage of products in car body paint shops Of the 21 car body paint shops visited, 4 (19.04%) shops stored products in a warehouse on wooden shelves, 2 (9.52%) in metal boxes, 3 (14.28%) on wooden tables, 2 (9.52%) in used refrigerators, 4 (19.04%) in cardboard boxes and 6 (28.57%) in used vehicles. Waste generated and its management The waste produced by the car body paint shops during their activities consists of empty cans of used chemicals, leftover chemicals, expired chemicals, cardboard boxes used as packaging, papers and newspapers for the protection of the windows during the paint coating. The waste products are stored in one place or in a jumble. They are transported to the nearest public dumping grounds. Discussion The inventory of car body paint shops in the city of Ouagadougou identified 17 chemicals that were hazardous to the health of exposed workers. Of these 17 products, 6 presented hazards to the environment. Biardeau et al. [6] in a multidisciplinary survey of chemical hazard assessment in paint companies found 175 distinct chemical substances with health hazards, physicochemical hazards and environmental hazards. Also in car body paint shops, 96 reconditioned products found could not be identified because these products were neither labeled nor in their original packaging. This could be explained not only by the fact that the acquisition of chemicals does not follow a formal circuit, but also by the lack of information and training of operators on the nature of the products and the conditions of use. Biardeau et al. [6] reported in France that 50% of products were not labeled. These unidentified products could be the same as those identified in the inventory because they are the same products used for automobile coating. They may be confusing to recognize and may be the cause of dangerous chemical reactions harmful to workers' health. Page 4/10
The results of this study identified three potential routes of worker exposure to chemicals in all 21 automotive body paint shops. These are the dermal, respiratory and ocular routes. In the case of skin exposure, work is carried out with bare hands without wearing gloves or a smock, and equipment and hands are washed with petroleum solvents. The deposition of aerosols on uncovered areas is a real source of exposure and entry of toxic substances into the body. Gargouri in his study on the assessment of the health impact of occupational exposure to organic solvents in the industry of glues and shoes in the region of Sfax-Tunisia had highlighted a lack of collective and individual protective equipment [1,9]. This lack of protection could cause effects such as irritation, skin sensitization, allergic reactions caused most often by substances such as bisphenol A, dibenzoyl peroxide, methyl acetate and dichloromethane [10,11,12,13]. Long-term manifestations such as defatting, peeling and sensitizing effects have been reported following prolonged exposures to dichloromethane, toluene, methanol and tetrahydrofuran [13,14,15,16]. In the eye, solvent vapors and aerosols have been the cause of eye irritation and blindness observed in workers using methyl ethyl ketone peroxide [17]. The volatility of the solvents, the dispersion of the aerosols in the ambient air combined with the non-use of chemical masks expose the workers to serious respiratory pathologies. Similar observations were made by Khayati in a study of the risk of exposure in leather processing in Tunis [9]. Respiratory pathologies due to exposure to chemicals used in paint shops are multiple and can be acute or chronic. The inhalation of these products can be the cause of irritation of respiratory mucosa [11, 14, 18, 19], psycho-organic syndromes (headaches, dizziness, narcosis, drowsiness or coma) [13, 14, 16, 17, 20, 22], toxicity on the central nervous system [22], sterility in particular in women and cancers [11, 13, 19, 22, 23]. Functional changes in the endocrine system, immune system, liver, kidney and other organ functions and hypersensitivity reactions have also been reported as hazards with unsafe use of paints [7]. The various components of the environment (air, soil, water) could be affected by the harmful effects of the chemicals used in automotive painting. Indeed, Biardeau et al. [6] reported in their study that 12% of the products inventoried in the painting companies were classified as "harmful to the environment" [6]. There is also air pollution due to the emission of solvent vapors and paint aerosols during the stripping of the old paint and the coating of the new paint. The car body paint shops being installed in residential areas, could constitute a risk of exposure to chemical products for the inhabitants of these shops. Some products like toluene contribute to the greenhouse effect [14]. Waste products such as leftover chemicals, expired chemicals and empty cans lying on the ground could lead to a spill of these products on the ground and with rainwater end up in the groundwater. Indeed, previous studies have shown a good bioaccumulation of these products in the soil [14]. Finally, through runoff or accidental spills, these products can end up in water reservoirs, rivers or streams. Some products such as cyclohexane, heptane, hexane, toluene and xylene have shown toxicity to aquatic organisms [14]. This situation still poses the problem of the management and disposal of waste from car body paint shops. Conclusion Our study has enabled us to identify all the chemical products used by painters in car body shops in the informal sector in the city of Ouagadougou. All these products present risks for human health and the environment. Given the working conditions, there is a potential exposure of workers to the chemicals used as well as the inhabitants of the surrounding residential areas. A toxicological and environmental hazard assessment in the car body painting workshops would allow us to know the degree of impregnation of the workers and the environment to the chemicals. Declarations Acknowledgements The authors appreciate all workers of the Kondor detergent factory who participated voluntarily in the study. Authors’ contributions Conceptualization: SS, ST. Data curation : SS, ST, TIS. Methodology : SS, ST, AKS. Writing-original draft: SS, ST, AC, BS. Writing- review & editing: SS, SSR, ST. All authors read and approved the final manuscript. Funding Page 5/10
Not applicable Availability of data and materials The datasets used and analysed during the current study are available from the corresponding author on reasonable request. Declarations Ethics Authorization for the survey was requested and obtained from each workshop manager and written informed consent was taken from all participants. Consent for publication All authors read and approved the final manuscript. Competing interests The authors have no conflicts of interest to declare for this study. References 1. Gargouri I. Évaluation de l’impact sanitaire des expositions professionnelles aux solvants organiques dans l’industrie des colles et des chaussures de la région de Sfax-Tunisie. Thèse de Doctorat, Université de Lille, France. 2009, 208p. available online at : https://tel.archives-ouvertes.fr/tel-00357479 2. INRS. Ventilation des ateliers d’encollage de petits objets (chaussures). Guide pratique de ventilation n° 5. ED 695, 2015 : 41p. available online at : https://www.esst-inrs.fr/3rb/ressources/ed695.pdf 3. International Labour Office, ILO Programme on Safety and Health at Work and the Environment. Safety and health in the use of chemicals at work: world day for safety and health at work, 28 April 2014. Geneva: ILO; 2013. available online at : https://www.ilo.org/global/topics/safety-and-health-at-work/lang--en/index.htm 4. SAICM/ICCM.3/24. Rapport de la Conférence internationale sur la gestion des produits chimiques sur les travaux de sa troisième session. available online at : https://www.who.int/ipcs/capacity_building/chemicals_management/saicm_iccm3_fr.pdf?ua=1 5. Certin J.F. Résultats de la campagne de contrôle 2006 « inspection du travail-prévention des risques professionnels des cram » (avec le soutien technique de l’inrs) sur l’utilisation des agents cancérogènes, mutagènes et toxiques pour la réproduction dans l’industrie. 2007, 8p. available online at: https://www.inrs.fr/media.html?refINRS=PR%2027 6. Biardeau B. Risques chimiques dans le B.T.P. 30èmes Journées nationales de santé au travail dans le bâtiment et les travaux publics. Blois, 2009, available online at: http://www.camip.info/colloques-congres/comptes-rendus/archives/Archives- 2009/Risques-chimiques-dans-le-B-T-P/Les-entreprises-de-peinture 7. Kitronza P.L. et al.. Identification des risques professionnels dans l’industrie textile en République Démocratique du Congo, pamj. 2014; 19:373. DOI: https://doi.org/doi:10.11604/pamj.2014.19.373.4186 Page 6/10
8. Vincent R., Bonthoux F., Larmoise C. Evaluation du risque chimique : hiérarchisation des risques potentiels, INRS, cahiers de notes documentaires, Hygiène et sécurité du travail n°178 2000 ; 34 p. available online at : https://www.inrs.fr/media.html? refINRS=ND%202121 9. Khayati N. Evaluation du risque de l’exposition aux solvants dans le secteur de la transformation du cuir (à propos de 84 cas). Mémoire Master spécialisé en medecine du travail; Université de Tunis EL Manar, Tunisie. 2004, 58p. available online at : https://www.memoireonline.com/07/08/1384/evaluation-risque-exposition-solvants-secteur-transformation-cuir.html. Accessed 03 August 2018 10. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°33 du Peroxyde de dibenzoyle. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_33. Accessed 08 August 2018 11. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°279 du Bisphenol A. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_279. Accessed 08 August 2018 12. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°34 du Dichlorométhane. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_34. Accessed 03 August 2018 13. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°88 de l’ Acétate de méthyl. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_88 Accessed 03 August 2018 14. Picot A., Montandon F. Ecotoxicochimie appliquée aux hydrocarbures. 2013, Lavoisier, Paris; 668 p. 15. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°5 du Méthanol. 2018, 9p. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_5 Accessed 23 January 2020 16. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°42 du Tétrahydrofurane. 2011, 10p. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_42 Accessed 03 August 2018 17. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°50 du Peroxyde de méthyléthylcétone. 2014, 7p. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html? Page 7/10
refINRS=FICHETOX_50 Accessed 03August 2018 18. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°162 de l’Isocyanate de méthyle. 2014, 10p. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html? refINRS=FICHETOX_162 Accessed 03 August 2018 19. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°3 de l’Acétone. 2018, 9p. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_3 Accessed on 23 January 2020 20. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°48 de l’Ethanol. 2019, 11p. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_48 Accessed 23 January2020 21. Institut National de Recherche et de sécurité, France. Base de données fiches toxicologiques : fiche toxicologique n°266 de l’Ethylbenzène. 2018, 10p. available online at : https://www.inrs.fr/publications/bdd/fichetox/fiche.html?refINRS=FICHETOX_266. Accessed 03 August 2018 22. Lauwerys R., Haufroid V., Hoet P., Lison D. Toxicologie industrielle et intoxications professionnelles, 5ème édition, Ed Masson, Paris, 2007 ; 1253 p. 23. Ametra06 la santé au travail. Guide à l’usage des carrossiers et des peintres ; 2018, 36p. available online at : https://www.ametra06.org/sites/default/files/2018-05/Carrossier_Peintre_Guide_0.pdf Accessed 05 February 2019. Table Table 1 : List of chemicals inventoried in auto body paint shops Page 8/10
N° Chemical name Trade name Physical Identifier Nature of state of the hazard the product (quantity) 01 Dibenzoyl peroxide HARDENER Paste 94-36-0 Noxious or BPO (20g) irritating, flammable, dangerous for the environment 02 Polyester, styrene 5- Extra/ Paste (5 UP : 0648 Noxious or 23%, bisphenol A and Polygard et 2,5 L) irritant epoxy resin health hazard 03 Methyl ethyl ketone Plastikit Non 1338-23-4 Corrosive, peroxide volatile Oxidizing liquid (20mL) 04 Xylene UPOL Volatile 1330-20-7 Noxious or liquid irritant, (1L) flammable 05 Isocyanate ICL Super Volatile 624-83-9 Noxious or liquid irritant, (1L) flammable 06 Urethane Hiq : DR Volatile Noxious or 421S liquid irritant, (1L) flammable 07 Toluene, xylene, Nitrocellulose Volatile UN :3A1/Y/140/17/GB/1267 Noxious or methanol (1-5%) Thinner/ liquid (5 irritant, champ L) flammable 08 Acetone, methanol, Nitrocellulose Volatile UN :3A1/Y1,2/100/16/I/CSI453150CMO2 Noxious or methyl acetate, ethyl Thinner liquid (5 irritant, acetate, L) health dichloromethane, hazard, ethanol, toluene, flammable propan-2-ol, methyl ketone, hexane, heptane, butanol, 4- methylpentan-2-one, butyl acetate 09 Toluene, butanone, Standard Volatile UN :3A1/Y12/150/16/F/HP6/LRM/M027 Flammable, butane-2-ol, heptane, thinners liquid Corrosive, N-hexane, (5L) noxious or ethylbenzene, xylene, irritant, PA, propane-1-ol, N- Dangerous butyl acetate, for health, cyclohexane, ethyl dangerous acetate, methyl for the acetate, environment methylisobutylketone, methanol, propyl acetate, acetone, N- butanol, H225 10 Acrylic, epoxy resin Appocoat Volatile Flammable, liquid (1 noxious or L) irritating dangerous for the environment Page 9/10
11 Toluene, N-butyl Stainless Volatile UN :3A1/Y1,2/150/16L/07058/SNCH- Noxious or acetate, acetone 1- liquid (5 IGRA07I/CSI12222/ASAR13 irritant, methoxy-2-propanol L) health hazard, flammable 12 Xylene, butyl acetate Standard volatile UN :3A1/Y1,2/100/17GN/3209070DPTCPI010 Noxious or thinner liquid (5 irritant, L) dangerous for health, dangerous for the environment, flammable 13 Toluene, cyclohexane, Standard volatile UN :3A1/Y/140/17GB/1267 Noxious or heptane, n-hexane, cellulose liquid (5 irritant, tetrahydrofuran thinners L) dangerous for health, dangerous for the environment, flammable 14 Polyisocyanate, ethyl SENIOR Car volatile UN : 1263 Flammable, acetate, n-butyl Paint liquid (1 noxious or acetate, propoxyl L) irritant glycol methyl ether acetate, methyl isobutyl ketone 15 Acétate éthyle, SENIOR Car Volatile UN : 1263 Noxious or acétate de n-butyle, Paint liquid (1 irritant, acétate d'éther L) flammable méthylique de propoxylglycol, méthylisobutylcétone 16 Toluene, ethyl Nitrocellulose Volatile UN : 1263 Dangerous acetate, methyl Thinner liquid to the acetate, acetone, (5L) environment methanol, butyl noxious or acetate standard, irritant, butanol standard, health hexane standard, hazard, heptane, butanone, flammable isopropyl acetate, propan-2-ol 17 Toluene, FIDEA Volatile UN :3A1/Y 1,4/120/17/F/FA/LRM AE06 Noxious or dichloromethane, liquid irritant, methanol, (5L) health tetrahydrofuran, hazard, acetone, ethyl acetate flammable Page 10/10
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