Antibiotics (ABs) in the aquatic environment is a major problem due to the emergence of antibiotic resistance. The long-term ecological impact on the aquatic environment is unknown. Many sources allow entry of ABs into the environment, including Wastewater Treatment Plants (WWTPs), agricultural run-off, hospital effluent and landfill leachate. Concentrations of ABs in the aquatic environment vary significantly, studies have shown fluoroquinolones, tetracycline, macrolides, sulphonamides and penicillins to reach 2900, 1500, 9700, 21400 and 1600 ngL -1 in wastewater effluent samples, however, concentrations are highly variable between different countries and depend on several factors including seasonally variation, prescription, and WWTP operating procedures. Likewise, the reported concentrations that cause environmental effects varies greatly between ABs, even within the same This article is protected by copyright. All rights reserved. Accepted Articleclass, however, this predicted concentration for the ABs considered was frequently <1000 ngL -1 indicating that when discharged into the environment along with treated effluent, these have a potential detrimental effect on the environment. Antibiotics are generally quite hydrophilic in nature; however, they can ionise in the aquatic environment to form charged structures, such as cations, zwitterions, and anions.Certain classes, particularly fluoroquinolones and tetracyclines, can adsorb onto solid matrices, including soils, sediment, and sludge, making it difficult to fully understand their chemical fate in the aquatic environment. The adsorption coefficient (K d ) varies between different classes of ABs, where tetracyclines and fluoroquinolones show the highest K d values. Adsorption coefficients values for fluoroquinolones, tetracyclines, macrolides and sulphonamides have been reported as 54600, 7600, 130 and 1.37 Lkg -1 . Factors such as pH of the environment, solid matrix (sediment/soil sludge) and ionic strength can influence the K d , therefore, several values exist in literature for the same compound.

A newly available dataset on pharmaceuticals used in Scottish hospitals enabled an environmental risk assessment that includes hospital consumption of pharmaceuticals, as previous United Kingdom rankings have been based on community prescriptions only. Although health and the environment are devolved issues for the Scottish government, it is merited to consider a Scottish ranking separately; regional differentiation is particularly relevant in the spatial context of the European Commission's Water Framework Directive. Nine pharmaceuticals are identified as having a risk quotient greater than 1. Four of these, the antibacterials piperacillin, tazobactam, flucloxacillin, and ciprofloxacin, had high hospital contributions and had not been highlighted previously in rankings based on community prescriptions. Some drugs with a risk quotient < 0.1 are used almost exclusively in hospitals and could be more concentrated near effluents carrying hospital wastewater, where they may be of local concern. Although treating hospital effluents separately is a policy option, specifically including hospital consumption is important. Continually increasing the availability of ecotoxicological data and trends in consumption further contributes to a substantially different prioritization than in previous rankings. This leads the authors to conclude that regular review of risk is necessary.

The resultant degradants from omeprazole and 5-hydroxyomeprazole were analogous to each other, differing only by an oxygen atom. This investigation determined the degradation products of omeprazole and 5-hydroxyomeprazole and proposed structures based on the accurate mass and isotope information. The product ions from the degradation products are also reported.

Perfluorinated alkyl substances (PFAS) are anthropogenic substances and can only come from polluted sources. There are many classes of PFAS which can be transformed to perfluoalkyl carboxylic acids and perfluoroalkyl sulfonic acids in the environment. Once they are in this form, they are environmentally mobile and extremely stable with half-lives of decades. These compounds are not innocuous and are implicated in causing many different diseases. In this publication, a method for the extraction and quantitation of perflurocarboxylic acids and perfluorosulfonic acids, using high-resolution liquid chromatography mass spectrometry (HRMS), is evaluated. A QuEChERS extraction method was performed on tomatoes, strawberries and milk purchased from different supermarkets on different days. Recoveries from milk and tomatoes were between 80 and 120%. Matrix effects were significant for strawberries and tomatoes and stable isotope internal standards were required to compensate. PFBA was found in all 3 food types. The total PFAS was 0.68 ng g−1 in milk, 0.20 ng g−1 in strawberries and 0.36 ng g−1 in tomatoes. This study demonstrates the importance of using a robust analytical method to investigate the PFAS content of complex food matrices and in particular the contribution of short-chain PFAS to overall dietary consumption.

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