Kinetic accumulation processes and models for 43 micropollutants in "pharmaceutical" POCIS

被引:42
作者
Morin, Nicolas A. O. [1 ,5 ]
Mazzella, Nicolas [2 ]
Arp, Hans Peter H. [3 ]
Randon, Jerome [4 ]
Camilleri, Julien [4 ]
Wiest, Laure [4 ]
Coquery, Marina [1 ]
Miege, Cecile [1 ]
机构
[1] Ctr Lyon Villeurbanne, Irstea, UR MALY, 5 Rue Doua,CS 20244, F-69625 Villeurbanne, France
[2] Ctr Bordeaux, Irstea, UR EABX, 50 Ave Verdun, F-33612 Cestas, France
[3] NGI, POB 3930, N-0806 Oslo, Norway
[4] Univ Claude Bernard Lyon 1, ISA, UMR CNRS 5280, 5 Rue Doua, F-69100 Villeurbanne, France
[5] Environm & Food Lab Vendee LEAV, Dept Chem, Rond Point Georges Duval CS 80802, F-85021 La Roche Sur Yon, France
关键词
Polar Organic Chemical Integrative Sampler (POCIS); Hydrophilic organic micropollutant; Waters; Membrane influence; Accumulation process modelling; SEMIPERMEABLE-MEMBRANE DEVICES; CHEMICAL INTEGRATIVE SAMPLERS; POLAR ORGANIC-COMPOUNDS; REFERENCE COMPOUND APPROACH; AQUATIC ENVIRONMENTS; PASSIVE SAMPLERS; SAMPLING RATES; IN-SITU; WATER; CONTAMINANTS;
D O I
10.1016/j.scitotenv.2017.08.311
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The "pharmaceutical" polar organic integrative sampler (POCIS) is a passive sampler composed of an outer polyethersulfone (PES) membrane and an inner receiving Hydrophilic-Lipophilic Balance (HLB) phase. Target micropollutants can accumulate in the POCIS HLB phase following different uptake patterns. Two of the most common ones are a first-order kinetic uptake (Chemical Reaction Kinetic 1, CRK1 model), and a first-order kinetic uptake with an inflexion point (CRK2 model). From a previous study, we identified 30 and 13 micropollutants following CRK1 and CRK2 accumulation model in the POCIS HLB phase, respectively. We hypothesized that uptake in the outer PES membrane of POCIS may influence the uptake pathway. Thus, novel measurements of uptake in PES membrane were performed for these micropollutants to characterise kinetic accumulation in the membrane with and without the HLB phase. We determined, for the first time, the membrane-water distribution coefficient for 31 micropolluants. Moreover, the lag times for molecules to breakthrough the POCIS membrane increased with increasing hydrophobicity, defined by the octanol-water dissociation constant D-ow. However, D-ow alone was insufficient to predict whether uptake followed a CRK1 or CRK2 model in the POCIS HLB phase. Thus, we performed a factorial discriminant analysis considering several molecular physico-chemical properties, and the model of accumulation for the studied micropollutants can be predicted with > 90% confidence. The most influent properties to predict the accumulation model were the log D-ow and the polar surface area of the molecule (> 70% confidence with just these two properties). Molecules exhibiting a CRK1 uptake model for the POCIS HLB phase tended to have log D-ow > 2.5 and polar surface area < 50 angstrom(2). (C) 2017 Elsevier B.V. All rights reserved.
引用
收藏
页码:197 / 207
页数:11
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