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. 2023 Dec 22;14(1):31-50.
doi: 10.3390/jox14010003.

An Initial Survey on Occurrence, Fate, and Environmental Risk Assessment of Organophosphate Flame Retardants in Romanian Waterways

Affiliations

An Initial Survey on Occurrence, Fate, and Environmental Risk Assessment of Organophosphate Flame Retardants in Romanian Waterways

Iuliana Paun et al. J Xenobiot. .

Abstract

Organophosphate ester flame retardants (OPFRs) are ubiquitous organic pollutants in the environment and present an important preoccupation due to their potential toxicity to humans and biota. They can be found in various sources, including consumer products, building materials, transportation industry, electronic devices, textiles and clothing, and recycling and waste management. This paper presents the first survey of its kind in Romania, investigating the composition, distribution, possible sources, and environmental risks of OPFRs in five wastewater treatment plants (WWTPs) and the rivers receiving their effluents. Samples from WWTPs and surface waters were collected and subjected to extraction processes to determine the OPFRs using liquid chromatography with mass spectrometric detection. All the target OPFRs were found in all the matrices, with the average concentrations ranging from 0.6 to 1422 ng/L in wastewater, 0.88 to 1851 ng/g dry weight (d.w.) in sewage sludge, and 0.73 to 1036 ng/L in surface waters. The dominant compound in all the cases was tri(2-chloroisopropyl) phosphate (TCPP). This study observed that the wastewater treatment process was inefficient, with removal efficiencies below 50% for all five WWTPs. The environmental risk assessment indicated that almost all the targeted OPFRs pose a low risk, while TDCPP, TCPP, and TMPP could pose a moderate risk to certain aquatic species. These findings provide valuable information for international pollution research and enable the development of pollution control strategies.

Keywords: LC-MS/MS; OPFRs; environmental risk; sewage sludge; surface water; wastewater.

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Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
Concentration levels of OPFRs in wastewater samples: (a) influents and (b) effluents.
Figure 2
Figure 2
Composition of OPFRs in wastewater samples: (a) influents and (b) effluents.
Figure 3
Figure 3
The removal efficiencies determined for individual compounds in WWTPs: (a) S1; (b) S2; (c) S3; (d) S4; (e) S5; and (f) sum of OPFRs.
Figure 4
Figure 4
Composition of OPFRs in sewage sludge samples (a), and the OPFR distribution between the aqueous and solid components of WWTPs (b).
Figure 5
Figure 5
Composition of OPFRs in samples collected upstream (a) and downstream (b) of the WWTPs.
Figure 6
Figure 6
OPFR occurrence in wastewater and surface water samples (a), and percentage distribution of OPFRs in surface water, waste water, and sludge samples (b).

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