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Quarterly Publication

Beyond soil contamination: Lead occurrence in playground paints of public parks in Bolivia

Document Type : Original Article

Authors

1 Centro de Ecología y Pueblos Andinos (CEPA), Oruro, Bolivia

2 Facultad de Ciencias y Tecnología, Universidad Mayor de San Simón (UMSS), Cochabamba, Bolivia

Abstract
Lead (Pb) remains a persistent environmental contaminant and a significant public health concern, particularly for children who are more vulnerable to its neurotoxic effects. While contaminated soils and industrial emissions are recognized exposure pathways, the contribution of lead-containing paints on playground structures in public recreational areas has been less frequently investigated. This study assessed Pb concentrations in paints applied to playground equipment and other painted structures in public parks and plazas of the city of Torreón, Bolivia, and evaluated their relationship with Pb levels in nearby surface soils. Between July 2022 and February 2023, thirteen public recreational sites were examined. Lead concentrations in painted surfaces were measured using a portable X-ray fluorescence (XRF) analyzer, while composite surface soil samples were collected and analyzed to determine Pb content. The United States Department of Housing and Urban Development (HUD) guideline of 1 mg/cm² was used as the reference threshold for Pb in painted surfaces. Pb concentrations exceeding this limit were detected in 36% of the analyzed paint measurements and were identified across multiple structural elements and paint colors. In contrast, most soil samples showed Pb concentrations below the remediation guideline of 400 ppm. A significant negative correlation was observed between soil Pb concentrations and distance from the smelting facility, suggesting the influence of historical industrial emissions. However, no statistically significant association was found between Pb concentrations in playground paints and those measured in surrounding soils. These findings indicate that lead-containing paints in public recreational spaces may represent an additional exposure pathway for children and underscore the importance of strengthening regulatory oversight and routine monitoring of Pb in public infrastructure.

Keywords

Subjects
Agency for Toxic Substances and Disease Registry (ATSDR). (2020). Toxicological profile for lead. https://stacks.cdc.gov/view/cdc/95222
Albalak, R., Hart, M. R., Noonan, G., Buchanan, S., Jones, R. L., Flanders, D. W., Gotway-Crawford, C., Kim, D., Dignam, T., Daley, W. R., Jarrett, J., Eduardo, E., & McGeehin, M. A. (2003). Blood lead levels and risk factors for lead poisoning among children in a Mexican smelting community. Archives of Environmental Health, 58(3), 172–183.
Bautista-Arredondo, L. F., Trejo-Valdivia, B., Estrada-Sánchez, D., Tamayo-Ortiz, M., Cantoral, A., Figueroa, J. L., Romero-Martínez, M., Gómez-Acosta, L. M., Cuevas-Nasu, L., & Téllez-Rojo, M. M. (2023). Intoxicación infantil por plomo en México: Otras fuentes de exposición más allá del barro vidriado (Ensanut 2022). Salud Pública de México, 65(1), S197–S203. https://doi.org/10.21149/14798
Benin, A. L., Sargent, J. D., Dalton, M., & Roda, S. (1999). High concentrations of heavy metals in neighborhoods near ore smelters in northern Mexico. Environmental Health Perspectives, 107(4), 279–284. https://doi.org/10.1289/EHP.99107279
Calderón-Salinas, J. V., Valdez-Anaya, B., Charles-Mazúñiga, A., & Albores-Medina, A. (1996). Lead exposure in a population of Mexican children. Human and Experimental Toxicology, 15(4), 305–311. https://doi.org/10.1177/096032719601500406
Caravanos, J., Dowling, R., Téllez-Rojo, M. M., Cantoral, A., Kobrosly, R., Estrada, D., Orjuela, M., Gualtero, S., Ericson, B., Rivera, A., & Fuller, R. (2014). Blood lead levels in Mexico and pediatric burden of disease implications. Annals of Global Health, 80(4), e1–e11. https://doi.org/10.1016/j.aogh.2014.10.005
Clark, C. S., Kumar, A., Mohapatra, P., Rajankar, P., Nycz, Z., Hambartsumyan, A., Astanina, L., Roda, S., Lind, C., Menrath, W., & Peng, H. (2014). Examination of lead concentrations in new decorative enamel paints in four countries with different histories of activity in lead paint regulation. Environmental Research, 132, 233–243. https://doi.org/10.1016/j.envres.2014.03.006
Fondo Nacional para el Fomento de las Artesanías (FONART). (2024). Fonart trabaja desde hace más de 30 años con la comunidad artesanal y diversas instituciones para erradicar el uso de plomo en la alfarería. https://www.gob.mx/fonart/articulos/fonart-trabaja-desde-hace-mas-de-30-anos-con-la-comunidad-artesanal-y-diversas-instituciones-para-erradicar-el-uso-de-plomo-en-la-alfareria
García-Vargas, G. G., Rothenberg, S. J., Silbergeld, E. K., Weaver, V., Zamoiski, R., Resnick, C., Rubio-Andrade, M., Parsons, P. J., Steuerwald, A. J., Navas-Acién, A., & Guallar, E. (2014). Spatial clustering of toxic trace elements in adolescents around the Torreón, Mexico lead–zinc smelter. Journal of Exposure Science & Environmental Epidemiology, 24(6), 634–642. https://doi.org/10.1038/jes.2014.11
García-Vargas, G. G., Rubio, A. M., del Razo, L. M., Borja, A. V., Vera, A. E., & Cebrián, M. E. (2001). Lead exposure in children living in a smelter community in Región Lagunera, Mexico. Journal of Toxicology and Environmental Health, Part A, 62(6), 417–429. https://doi.org/10.1080/00984100150501150
Gottesfeld, P., & Jacobs, D. E. (2016). Letter to the editor: Re: Lead and other toxic metals in playground paints from South West England. Science of the Total Environment, 562, 996–997. https://doi.org/10.1016/j.scitotenv.2016.02.124
Instituto Nacional de Estadística y Geografía (INEGI). (2020). Presentación de resultados: Coahuila de Zaragoza. https://www.inegi.org.mx/contenidos/programas/ccpv/2020/doc/cpv2020_pres_res_coah.pdf
International Pollutants Elimination Network (IPEN). (2018). Lead in solvent-based paints for household use in Mexico. https://ipen.org/sites/default/files/documents/ipen-mexico-lead-report-v1_4-es.pdf
International Pollutants Elimination Network (IPEN). (2019). Lead in children’s playground equipment in Mexico. https://casacem.com/upload/9a8ecff8e308717d824834588b39a3e1.pdf
Kessler, R. (2014). Lead-based decorative paints: Where are they still sold and why? Environmental Health Perspectives, 122(4), A96–A103. https://doi.org/10.1289/ehp.122-A96
Lanphear, B. P., & Roghmann, K. J. (1997). Pathways of lead exposure in urban children. Environmental Research, 74(1), 67–73. https://doi.org/10.1006/enrs.1997.3726
Laperche, V., & Lemière, B. (2021). Possible pitfalls in the analysis of minerals and loose materials by portable XRF, and how to overcome them. Minerals, 11(1), 33–57. https://doi.org/10.3390/min11010033
McIntosh, K. G., Guimarães, D., Cusack, M. J., Vershinin, A., Chen, Z. W., Yang, K., & Parsons, P. J. (2016). Evaluation of portable XRF instrumentation for assessing potential environmental exposure to toxic elements. International Journal of Environmental Analytical Chemistry, 96(1), 15–37. https://doi.org/10.1080/03067319.2015.1114104
O’Connor, D., Hou, D., Ye, J., Zhang, Y., Ok, Y. S., Song, Y., Coulon, F., Peng, T., & Tian, L. (2018). Lead-based paint remains a major public health concern: A critical review of global production, trade, use, exposure, health risk, and implications. Environment International, 121, 85–101. https://doi.org/10.1016/j.envint.2018.08.052
Recio-Vega, R., Valdez-Abrego, C., Adame-López, B., & Gurrola-Méndez, A. (2012). Surveillance of elevated blood lead levels in children in Torreón, Coahuila, Mexico (1998–2010). International Journal of Hygiene and Environmental Health, 215(5), 507–513. https://doi.org/10.1016/j.ijheh.2011.10.009
Rubio-Andrade, M., Valdés-Pérezgasga, F., Alonso, J., Rosado, J. L., Cebrián, M. E., & García-Vargas, G. G. (2011). Follow-up study on lead exposure in children living in a smelter community in northern Mexico. Environmental Health, 10(66), 1–7. https://doi.org/10.1186/1476-069X-10-66
Safruk, A. M., McGregor, E., Aslund, M. L. W., Cheung, P. H., Pinsent, C., Jackson, B. J., Hair, A. T., Lee, M., & Sigal, E. A. (2017). The influence of lead content in drinking water, household dust, soil, and paint on blood lead levels of children in Flin Flon, Manitoba and Creighton, Saskatchewan. Science of the Total Environment, 593–594, 202–210. https://doi.org/10.1016/j.scitotenv.2017.03.141
Turner, A., Kearl, E. R., & Solman, K. R. (2016). Lead and other toxic metals in playground paints from South West England. Science of the Total Environment, 544, 460–466. https://doi.org/10.1016/j.scitotenv.2015.11.078
U.S. Department of Housing and Urban Development (HUD). (2012). Guidelines for the evaluation and control of lead-based paint in housing. https://www.hud.gov/program_offices/healthy_homes/lbp/hudguidelines
U.S. Environmental Protection Agency (USEPA). (2024). EPA strengthens safeguards to protect families and children from lead in contaminated soil at residential sites in Region 7. https://www.epa.gov/newsreleases/epa-strengthens-safeguards-protect-families-and-children-lead-contaminated-soil
World Health Organization (WHO). (2023). Update on the global status of legal limits on lead in paint. https://www.who.int/publications/i/item/9789240078093
  • Receive Date 08 May 2026
  • Revise Date 21 May 2026
  • Accept Date 08 June 2026
  • Publish Date 09 June 2026