Organic chemicals that are persistent and mobile in the aquatic environment exhibit a hazard to contaminate drinking water resources. In this study an emission score model was developed to rank the potential of substances registered under the REACH legislation to be emitted into the environment. It was applied to a list of 2167 REACH registered substances that were previously identified to be persistent and mobile organic chemicals (PMOCs) in groundwater or to be hydrolyzed to form transformation products fulfilling the PMOC criteria. The emission score model is based on the tonnage placed on the European market and on seven emission-related use characteristics (high release to environment, wide dispersive use, intermediate use, closed system use, professional use, consumer use, and substance in article), reported in the companies' registrations under REACH. Applying the model resulted in a list of 1110 substances (936 PMOCs and 174 precursors to PMOCs) that were estimated to be released into the environment, while 1054 substances had indicators of negligible environmental emissions and 3 substances could not be evaluated due to severe data gaps. The 936 PMOCs and the 174 precursors were ranked in two lists with regard to their emission potential. The model was shown to be fit for purpose in terms of suggesting and prioritizing substances for scientific investigations with a focus on environmental water quality. Though targeted for PMOCs, the presented scoring system is illustrative of how REACH registration data can be used to assess the emission potential of various substances.
Persistent and mobile organic substances (PM substances) are a threat to the quality of our water resources. While screening studies revealed widespread occurrence of many PM substances, rapid trace analytical methods for their quantification in large sample sets are missing. We developed a quick and generic analytical method for highly mobile analytes in surface water, groundwater, and drinking water samples based on enrichment through azeotrope evaporation (4 mL water and 21 mL acetonitrile), supercritical fluid chromatography (SFC) coupled to high-resolution mass spectrometry (HRMS), and quantification using a compound-specific correction factor for apparent recovery. The method was validated using 17 PM substances. Sample preparation recoveries were between 60 and 110% for the vast majority of PM substances. Strong matrix effects (most commonly suppressive) were observed, necessitating a correction for apparent recoveries in quantification. Apparent recoveries were neither concentration dependent nor dependent on the water matrix (surface or drinking water). Method detection and quantification limits were in the single-to double-digit ng L −1 ranges, precision expressed as relative standard deviation of quadruplicate quantifications was on average < 10%, and trueness experiments showed quantitative results within ± 30% of the theoretical value in 77% of quantifications. Application of the method to surface water, groundwater, raw water, and finished drinking water revealed the presence of acesulfame and trifluoromethanesulfonic acid up to 70 and 19 μg L −1 , respectively. Melamine, diphenylguanidine, pdimethylbenzenesulfonic acid, and 4-hydroxy-1-(2-hydroxyethyl)-2,2,6,6-tetramethylpiperidine were found in high ng L −1 concentrations.
The
devastation to infrastructure in wildland urban interface (WUI)
communities caused by wildfires has brought attention to the dramatic
and unforeseen impacts of high fuel load density within these communities.
In the past three years, above-ground structures have been damaged
by wildfire and fire damage to underground water distribution system
components has caused contamination of the drinking water in affected
areas. To quantify the potential water contamination risks posed by
wildfire hazards on WUI communities, the risk is assessed on the basis
of burn severity. This study found that traditional methods of calculating
burn severity using satellite imagery were not appropriate for classifying
localized burn severity within WUI communities. Instead, local burn
severity within WUI communities can be quantified by the density of
damaged structures. This research uses water sampling data and results
from the City of Santa Rosa and the Town of Paradise to develop fragility
functions for estimating the probability of a water sample exceeding
California maximum contaminant levels given the number of damaged
structures surrounding the sample location. Results of this research
will provide useful information for WUI water utilities regarding
the implementation of mitigation strategies and location of vulnerabilities
throughout their water distribution systems to minimize damage.
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