Abstract

The aim of the study was to assess the levels of inhalable dust, endotoxins and (1–3)-β-d-glucans as agents harmful to the respiratory tract of workers of municipal waste sorting plants and interaction between these agents based on the measurements taken in two plants with different processing capacities. The study was conducted in summer season in two waste sorting plants (WSPs) differing in processing capacity. Samples of bioaerosol for inhalable dust (gravimetric method), endotoxins (LAL test in kinetic, chromogenic version) and (1–3)-β-d-glucans (Glucatell test in kinetic version) were collected from 42 sorting workers using individual aspirators with glass fiber filters during the work shift. Average geometric concentrations (geometric standard deviation; min–max) of inhalable dust, endotoxins and (1–3)-β-d-glucans were: WSP1: 1.7 mg m−3 (2.2; 0.6–6.9 mg m−3); 15.9 ng m−3 (2.1; 5.4–78.9 ng m−3), 55.1 ng m−3 (1.8; 20.7–188.6 ng m−3) and WSP2: 0.8 mg m−3 (2.2; 0.2–3.8 mg m−3), 9.8 ng m−3 (2.4; 1.6–29.7 ng m−3), 45.0 ng m−3 (3.2, 5.7–212.9 ng m−3), respectively. A significantly higher concentration of inhalable dust was recorded in WSP1 with bigger processing capacity compared to WSP2 (less processing capacity). Significant (p < 0.05) and very high correlations (Spearman rank R > 0.7) were found between the concentrations of all analyzed harmful agents. Processing capacity of waste sorting plants differentially affects the concentrations of inhalable dust, whereas concentrations of endotoxins and glucans are less clearly affected. This suggests that relative concentrations of endotoxin and glucan are depending on the waste sorting capacity.

Highlights

  • Municipal waste sorting plants are specific workplaces because of their workers’ frequent direct contact with the municipal mixed wastes

  • Processing capacity of waste sorting plants differentially affects the concentrations of inhalable dust, whereas concentrations of endotoxins and glucans are less clearly affected. This suggests that relative concentrations of endotoxin and glucan are depending on the waste sorting capacity

  • No statistical significance was shown for differences in endotoxin concentrations between WSP1 and WSP2 (p [ 0.05; 15.9 and 9.8 ng m-3, respectively)

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Summary

Introduction

Municipal waste sorting plants are specific workplaces because of their workers’ frequent direct contact with the municipal mixed wastes. Waste with a high content of organic fraction during earlier storage in containers undergoes some putrefactive processes depending on climatic conditions (temperature and humidity) (Wouters et al 2006). Microorganisms growing on organic residue are present at high concentration in the air surrounding the wastes storage in the form of bioaerosol (Douwes et al 2003; Wouters et al 2006). According to Poulsen et al (1995), workers of recycling plants may be exposed to complex, compound bioaerosols and volatile chemical compounds, where synergistic interactions may occur between particular components. Studies on the impact of seasonality on concentration of airborne biological agents indicate that such exposure reaches the highest values in summer (Oppliger et al 2005; Pinto et al 2015; Thorn 2001)

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