Exposure Routes and Health Risks Associated with Pesticide Application.

human health risk assessment occupational health and safety pesticide application methods pesticide exposure

Journal

Toxics
ISSN: 2305-6304
Titre abrégé: Toxics
Pays: Switzerland
ID NLM: 101639637

Informations de publication

Date de publication:
19 Jun 2022
Historique:
received: 26 04 2022
revised: 09 06 2022
accepted: 13 06 2022
entrez: 23 6 2022
pubmed: 24 6 2022
medline: 24 6 2022
Statut: epublish

Résumé

Pesticides play an important role in agricultural development. However, pesticide application can result in both acute and chronic human toxicities, and the adverse effects of pesticides on the environment and human health remain a serious problem. There is therefore a need to discuss the application methods for pesticides, the routes of pesticide exposure, and the health risks posed by pesticide application. The health problems related to pesticide application and exposure in developing countries are of particular concern. The purpose of this paper is to provide scientific information for policymakers in order to allow the development of proper pesticide application technics and methods to minimize pesticide exposure and the adverse health effects on both applicators and communities. Studies indicate that there are four main pesticide application methods, including hydraulic spraying, backpack spraying, basal trunk spraying, and aerial spraying. Pesticide application methods are mainly selected by considering the habits of target pests, the characteristics of target sites, and the properties of pesticides. Humans are directly exposed to pesticides in occupational, agricultural, and household activities and are indirectly exposed to pesticides via environmental media, including air, water, soil, and food. Human exposure to pesticides occurs mainly through dermal, oral, and respiratory routes. People who are directly and/or indirectly exposed to pesticides may contract acute toxicity effects and chronic diseases. Although no segment of the general population is completely protected against exposure to pesticides and their potentially serious health effects, a disproportionate burden is shouldered by people in developing countries. Both deterministic and probabilistic human health risk assessments have their advantages and disadvantages and both types of methods should be comprehensively implemented in research on exposure and human health risk assessment. Equipment for appropriate pesticide application is important for application efficiency to minimize the loss of spray solution as well as reduce pesticide residuals in the environment and adverse human health effects due to over-spraying and residues. Policymakers should implement various useful measures, such as integrated pest management (IPM) laws that prohibit the use of pesticides with high risks and the development of a national implementation plan (NIP) to reduce the adverse effects of pesticides on the environment and on human health.

Identifiants

pubmed: 35736943
pii: toxics10060335
doi: 10.3390/toxics10060335
pmc: PMC9231402
pii:
doi:

Types de publication

Journal Article Review

Langues

eng

Subventions

Organisme : Chinese Academy of Sciences
ID : XDA23100400

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Auteurs

Muyesaier Tudi (M)

Key Laboratory of Land Surface Pattern and Simulation, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, No. 11 Datun Road, Beijing 100101, China.
School of Medicine, Griffith University, 170 Kessels Road, Nathan, Brisbane, QLD 4111, Australia.

Hairong Li (H)

Key Laboratory of Land Surface Pattern and Simulation, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, No. 11 Datun Road, Beijing 100101, China.

Hongying Li (H)

Foreign Environmental Cooperation Center, Ministry of Ecology and Environment, Beijing 100035, China.

Li Wang (L)

Key Laboratory of Land Surface Pattern and Simulation, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, No. 11 Datun Road, Beijing 100101, China.

Jia Lyu (J)

Key Laboratory of Land Surface Pattern and Simulation, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, No. 11 Datun Road, Beijing 100101, China.
China CDC Key Laboratory of Environment and Population Health, National Institute of Environmental Health, Chinese Center for Disease Control and Prevention, No. 29 Nanwei Road, Beijing 100050, China.

Linsheng Yang (L)

Key Laboratory of Land Surface Pattern and Simulation, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, No. 11 Datun Road, Beijing 100101, China.

Shuangmei Tong (S)

Key Laboratory of Land Surface Pattern and Simulation, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, No. 11 Datun Road, Beijing 100101, China.

Qiming Jimmy Yu (QJ)

School of Engineering and Built Environment, Nathan Campus, Griffith University, Brisbane, QLD 4111, Australia.

Huada Daniel Ruan (HD)

Environmental Science Program, Division of Science and Technology, Beijing Normal University-Hong Kong Baptist University United International College, 2000 Jintong Road, Tangjiawan, Zhuhai 519087, China.

Albert Atabila (A)

Department of Biological, Environmental & Occupational Health Sciences, School of Public Health, University of Ghana, Legon, Accra P.O. Box LG13, Ghana.

Dung Tri Phung (DT)

School of Medicine, Griffith University, 170 Kessels Road, Nathan, Brisbane, QLD 4111, Australia.

Ross Sadler (R)

School of Medicine, Griffith University, 170 Kessels Road, Nathan, Brisbane, QLD 4111, Australia.

Des Connell (D)

School of Environment and Science, Griffith University, 170 Kessels Road, Nathan, Brisbane, QLD 4111, Australia.

Classifications MeSH