Abstract
In this study, three different passive sampling receiving phases were evaluated, with a main focus on the comparability of established styrene-divinylbenzene reversed phase sulfonated (SDB-RPS) sampling phase from Empore™ (E-RPS) and novel AttractSPE™ (A-RPS). Furthermore, AttractSPE™ hydrophilic-lipophilic balance (HLB) disks were tested. To support sampling phase selection for ongoing monitoring needs, it is important to have information on the characteristics of alternative phases. Three sets of passive samplers (days 1–7, days 8–14, and days 1–14) were exposed to a continuously exchanged mixture of creek and rainwater in a stream channel system under controlled conditions. The system was spiked with nine pesticides in two peak scenarios, with log KOW values ranging from approx. − 1 to 5. Three analytes were continuously spiked at a low concentration. All three sampling phases turned out to be suitable for the chosen analytes, and, in general, uptake rates were similar for all three materials, particularly for SDB-RPS phases. Exceptions concerned bentazon, where E-RPS sampled less than 20% compared with the other phases, and nicosulfuron, where HLB sampled noticeably more than both SDB-RPS phases. All three phases will work for environmental monitoring. They are very similar, but differences indicate one cannot just use literature calibration data and transfer these from one SDB phase to another, though for most compounds, it may work fine.Graphical abstract
Highlights
Passive sampling is considered to be an important tool to further improve water monitoring
Nicosulfuron and propiconazole show slightly higher amounts in the hydrophilic-lipophilic balance (HLB) sorbent phase compared with the styrene-divinylbenzene reversed phase sulfonated (SDB-RPS) phases, possibly indicating a higher partitioning coefficient towards HLB compared with SDBRPS
The difference between the two SDB-RPS phases is intriguing, as all other substances are sampled fairly equal by both SDB-RPS type phases
Summary
Passive sampling is considered to be an important tool to further improve water monitoring. It is a recommended approach for future application in the EU Water Framework Directive (EU-WFD) (Brack et al 2017). It enriches compounds in situ so that extraction of (large) water sample volumes prior to analysis is not necessary. This is useful for hydrophobic organic compounds such as polychlorinated biphenyls (Smedes et al 2010) or some insecticides (Moschet et al 2015) and allows for low detection limits. Passive sampling provides a time-weighted average concentration.
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