Applications for Passive Sampling of Hydrophobic Organic Contaminants in Water—A Review

Taylor, Adam; Fones, Gary R.; Vrana, Branislav; Mills, Graham A.

doi:10.1080/10408347.2019.1675043

Cited by 45 publications

(40 citation statements)

References 361 publications

(283 reference statements)

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“…The method developed here gives integrated sampling over time for the more frequently detected microorganisms, AllBac, NoV, and Vibrio spp., which is a characteristic of passive samplers in general (Taylor et al, 2019). These observations are consistent with our laboratory experiments in which we observed that the concentration of NoV on membranes increased with the duration of exposure (Vincent-Hubert et al, 2017).…”

Section: Discussionsupporting

confidence: 92%

Passive Samplers, a Powerful Tool to Detect Viruses and Bacteria in Marine Coastal Areas

Vincent-Hubert

Wacrenier

Morga³

et al. 2021

Front. Microbiol.

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The detection of viruses and bacteria which can pose a threat either to shellfish health or shellfish consumers remains difficult. The current detection methods rely on point sampling of water, a method that gives a snapshot of the microorganisms present at the time of sampling. In order to obtain better representativeness of the presence of these microorganisms over time, we have developed passive sampling using the adsorption capacities of polymer membranes. Our objectives here were to assess the feasibility of this methodology for field detection. Different types of membrane were deployed in coastal waters over 2 years and the microorganisms tested using qPCR were: human norovirus (NoV) genogroups (G)I and II, sapovirus, Vibrio spp. and the species Vibrio alginolyticus, V. cholerae, V. vulnificus, and V. parahaemolyticus, OsHV-1 virus, and bacterial markers of fecal contamination. NoV GII, Vibrio spp., and the AllBac general Bacteroidales marker were quantified on the three types of membrane. NoV GII and OsHV-1 viruses followed a seasonal distribution. All membranes were favorable for NoV GII detection, while Zetapor was more adapted for OsHV-1 detection. Nylon was more adapted for detection of Vibrio spp. and the AllBac marker. The quantities of NoV GII, AllBac, and Vibrio spp. recovered on membranes increased with the duration of exposure. This first application of passive sampling in seawater is particularly promising in terms of an early warning system for the prevention of contamination in oyster farming areas and to improve our knowledge on the timing and frequency of disease occurence.

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Section: Discussionsupporting

confidence: 92%

Passive Samplers, a Powerful Tool to Detect Viruses and Bacteria in Marine Coastal Areas

Vincent-Hubert

Wacrenier

Morga³

et al. 2021

Front. Microbiol.

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“…A recent review of passive sampling of hydrophobic organic compounds [48] presents the monitoring principles for non-polar pesticides. At present, knowledge of the theory underpinning passive sampling of polar organic compounds, such as polar pesticides, is less developed.…”

Section: Passive Sampling Of Polar Pesticidesmentioning

confidence: 99%

Trends in the use of passive sampling for monitoring polar pesticides in water

Taylor

Fones

Mills

2020

Trends in Environmental Analytical Chemistry

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The presence of polar pesticides in environmental waters is a growing problem. After application their migration into the aqueous phase is promoted by their high water solubility. Transport processes are usually complex and inputs are generally stochastic; this makes monitoring of this class of pesticides challenging using low volume spot samples of water. Recently there has been a trend to use passive samplers to monitor pesticides in river catchments as it is an in-situ time integrative sampling technique. The three main types of device used for this purpose are, Chemcatcher ® , POCIS and o-DGT. This article reviews the fate and current state-of-the-art for monitoring polar pesticides in aqueous matrices. Principles and the theory of passive sampling and strategies for passive sampler design and operation are presented. Advances in the application of passive sampling devices for measuring polar pesticides are extensively critiqued; future trends in their use are also discussed.

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“…In Figure 4, y-scale of Log C S /C M enabled researchers to observe the different accumulation trends of the active and passive samplers, and the black line at Log 10 indicates the equality of their concentrations. The upper part of the black line signifies that the metabolization of HOCs in the selected marine organism is higher, whereas the lower part of the black line indicates that the contaminants in the particular phase were higher than their dissolved forms, as a reminder that the dissolved phase of contaminants accumulated in the passive sampler (Bourgeault & Gourlay-Francé, 2013;Gourlay-Francé, Lor-geoux, & Tusseau-Vuillemin, 2008;Kim, Kim, Alvarez, Lee, & Oh, 2014;Lance et al, 2012;Luellen & Shea, 2002;Taylor, Fones, Vrana, & Mills, 2019;Zhao et al, 2018).…”

Section: Resultsmentioning

confidence: 99%

Contribution of Passive Sampling Devices on the Determination of Hydrophobic Organic Contaminant Bioaccumulation in Marine Organisms

Dündar¹

2020

ASE

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Applications for Passive Sampling of Hydrophobic Organic Contaminants in Water—A Review

Cited by 45 publications

References 361 publications

Passive Samplers, a Powerful Tool to Detect Viruses and Bacteria in Marine Coastal Areas

Passive Samplers, a Powerful Tool to Detect Viruses and Bacteria in Marine Coastal Areas

Trends in the use of passive sampling for monitoring polar pesticides in water

Contribution of Passive Sampling Devices on the Determination of Hydrophobic Organic Contaminant Bioaccumulation in Marine Organisms

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