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Abstract: Over the past 20 years, oil sands exploration and processing in Canada have grown steadily, leading to the development of intensive large-scale operations in Alberta, Canada. Naphthenic acids (NAs), a complex mixture of aliphatic and alicyclic carboxylic acids, are by-products of oil sands processing and are known to be toxic. While oil sands processing water (OSPW) is contained in tailings ponds, potential seepage and leaking of OSPW and its contaminants into surrounding surface water systems is a concern. The ability to quantify NAs and their isomers in OSPW surrounding water is essential for monitoring these spills. Unfortunately, quantification of NAs and their isomers is challenging due to the complexity of the NA mixtures, the lack of commercially available standards, and interference from naturally occurring NA compounds. Techniques such as FT-IR and GC/MS are currently used to analyse NAs, but are limited by poor sensitivity and specificity in the case of FT-IR and long sample preparation and instrument run time for GC/MS. To tackle these issues, a rapid LC/MS method was developed which can quickly quantify NAs in surface water with much better sensitivity and specificity than current methods. This method uses large volume injection, ESI negative mode and a Poroshell LC column to improve the method limits of detection (LOD) and quantitation (LOQ). The method is robust and has no complicated sample preparation steps. The method detection limit (MDL) is 0.01mg/L (10ppb) and low limit of quantitation (LLOQ) of 0.1mg/L (100ppb), both for surface water. The developed method was tested with samples from the oil sands producing region, and demonstrated its applicability for fast screening of surface water samples before resorting to costly high accuracy and high resolution mass spectrometry determination. This is the first very rapid LC/MS method using large volume single column direct injection for quantitative determination of naphthenic acids in surface water. [Copyright &y& Elsevier]

• Rapid, direct injection LC/MS-QTOF method for resin acids without derivatization. • MDL in range 0.05 to 0.07 µgL−1 for six resin acids in aqueous alkaline matrix. • Precision and accuracy from 1 µgL−1 to 40 µgL−1 in matrix. • Isopimaric as calibrant for six C 20 H 30 O 2 resin acids. • Transferred to LC/MS/MS and successfully applied to environmental samples. A rapid and sensitive liquid chromatography (LC) quadrupole time of flight (QTOF) method has been developed for the determination of resin acid concentrations in aqueous pulp and paper effluent related samples. Calibration R2 of ≥0.995 for twelve resin acids, namely dehydroabietic, 8(14)-abietenic, dihydroisopimaric, levopimaric, neoabietic, pimaric, sandaracopimaric, abietic, isopimaric, palustric, chlorodehydroabietic, and dichlorodehydroabietic acids, was demonstrated in the range 1 µgL−1 to 40 µgL−1. An improved lower limit of quantitation was achieved without use of complex sample extraction and clean-up procedures undertaken by other published methods. Excellent precision and accuracy results were achieved for dehydroabietic, chlorodehydroabietic, dichlorodehydroabietic, isopimaric (integrated inclusive of all C 20 H 30 O 2 resin acids), dihydroisopimaric and 8(14)-abietenic resin acids, with t-99 percentile detection limits spanning the range 0.05 to 0.07 µgL−1. While measurement for the C 20 H 30 O 2 resin acids by isopimaric equivalence is considered semi-quantitative and could be an under estimate for the abietic acid component, the developed method demonstrated clear advantage over time consuming, hazardous, and unstable derivatization procedures used for gas chromatography and capillary electrophoresis. The developed LC/QToF method was successfully transferred to an LC triple quadrupole mass spectrometer for routine high throughput trace level analysis. Real world samples, including sea water and estuary water, demonstrated excellent spike recoveries by this procedure, indicating that the method is well suited to the monitoring of industrially derived resin acids in environmental surface waters. While no interferences were observed during routine sample analysis using myristic-1-13C acid and palmitic-1-13C acid internal standards, these were later substituted by myristic-d 27 and palmitic-d 31 acid in order to improve method robustness for environmental samples where endogenous parent fatty acids could be present. [ABSTRACT FROM AUTHOR]