“…Multiresidue methods allowing targeted (quantitative) and non-targeted (qualitative) screening should become standard procedures for CECs analysis as well as combining analytical methods with metabolomics for the identification of uncommon chemicals, metabolites, and degradation product(s); -To determine and predict trends, multivariate statistical methods (factor analysis of principal component analysis (PCA) were applied as well as indicators of pollution status, as Hazard Quotient (HQ), Enrichment Factor (EF), Geo-accumulation index (Igeo), and Ecological risk index (RI) were determined in several papers concerning persistent pollutants as PAHs, OCPs, and metals [2,46,51,84,100,107,121,144]; -Regarding CECs, the basis for risk assessment was rarely discussed. Risk coefficients (RQ) value based on the ratio of the Predicted/Measured Environmental Concentration (PEC/MEC) and Predicted No-Effect Concentration (PNEC) was performed in three papers for endocrine disruptors [61,68,69] and in one for pharmaceuticals, pesticides, and other CECs [26]; the fate of pesticides in sediments and risk assessment according to their physico-chemical properties was discussed in one paper [44]; -Spatial distribution of the contaminants was highlighted in several publications [45,49,53,61,100]; -Pollution emission sources were investigated for PAHs [96], OPCs [94], pharmaceuticals [51,53], and heavy metals [106,126,128,156]. Untreated and inadequate treated waste water was demonstrated as being the main source of organic pollution in the low Danube basin.…”