From: NORMAN guidance on suspect and non-target screening in environmental monitoring
Screening for | Prioritisation approach | Methods | References |
---|---|---|---|
Contamination with regulated, highly used or emerging substances (suspects) | Screening with appropriate suspects lists (e.g., all registered pesticides; industrial compounds with high use; predicted TPs) | Selection or compilation of an appropriate suspect list (see Sect. “Candidate structure search and selection”) and screening of exact mass in samples and blank samples | |
Contamination spots (often local) | High intensity in few samples from specific sites but not in samples from reference sites | Statistical analysis, e.g., density estimation, probability distribution, pairwise comparisons | |
Widespread contamination | High frequency of occurrence in samples from different sites | Statistical analysis, e.g., density estimation, probability distribution | |
Contamination with compounds that produce high seasonal or intraday fluctuation | Comparison of samples over time (e.g., industrial wastewater during different production processes) | Time series analysis using, e.g., (non)linear regression, (non)-parametric, uni-/multivariate statistical approaches | |
Similarly or differently contaminated sites/ contamination profiles | Comparison of the MS pattern of samples from different sites | Clustering (e.g., hierarchical), unsupervised PCA or supervised PLS, selection of masses in the loading plots | |
Contamination with homologues of a substance class (e.g., PFAS, surfactants) | Characteristic mass (e.g., CF2) and RT difference | Homologue series search, Kendrick mass defect and other mass defect plots | |
Substance classes with specific functional groups (aldehydes, conjugates) | Neutral loss, specific fragments in MS2 spectra from compound or derivative (e.g., –SO3) | Fragment search in MS2 spectra | |
Anthropogenic compounds with specific isotope pattern | Isotope pattern (especially relevant for Cl = Br > S > Si) | Isotope search in MS1 | |
Compounds causing effect | Effect-directed selection of masses in samples or fractions of samples using effect data or bioassays; Fractionation is often necessary to reduce candidate masses and chemical complexity | Comparison of masses in samples/fractions causing effect with those causing no effect using direct comparison or statistical methods | |
Compounds potentially causing effects | Annotation of signals with in vivo or in vitro hazard characteristics | In silico prediction of toxicity based on chemical fingerprints produced from MS2 spectra by SIRIUS | |
Persistent compounds | Comparison of samples before and after processes (e.g., water treatment) or along time scales (e.g., river stretch) | Statistical methods, such as clustering, PCA, PLS, fold change | |
Bioaccumulative compounds | Comparison of the MS pattern of samples along the trophic chain | Clustering (e.g., hierarchical), trend analysis | |
Formed TPs | Comparison of samples before and after processes (e.g., water treatment) or along time scales (e.g., along river stretch) for specific mass differences due to transformation reaction | Search for specific mass differences in mass lists of before and after samples or statistically (PCA, clustering, time series) separated groups (e.g., 15.9949 for addition of O) | |
Formed disinfection by-products (DBPs) | Comparison of samples before and after water treatment, then isotopic pattern analysis (Cl, Br) | Isotope search in MS1 and MS2 for formed signals with specific isotope pattern | |
Isotope-supported detection of TPs, by-products | Lab experiments with isotopically labelled reagents, screening for isotope mass differences (e.g., reaction with 15NO3−, screening for Δm = 0.9970) | Search for specific mass differences in mass lists of lab experiments with mixtures of isotopes (e.g., 14NO3− and 15NO3−) or of two sample series with single isotopes |