高级搜索

水体微量有机物被动监测技术研究进展

,  ,  ,  , 

downloadPDF

上一篇

下一篇

陈梦珂, 王传飞, 龚平, 任娇, 王小萍. 水体微量有机物被动监测技术研究进展[J]. 环境化学, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
引用本文: 陈梦珂, 王传飞, 龚平, 任娇, 王小萍. 水体微量有机物被动监测技术研究进展[J]. 环境化学, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
shu
CHEN Mengke, WANG Chuanfei, GONG Ping, REN Jiao, WANG Xiaoping. Passive sampling techniques for the monitoring of trace organic pollutants in water[J]. Environmental Chemistry, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
Citation: CHEN Mengke, WANG Chuanfei, GONG Ping, REN Jiao, WANG Xiaoping. Passive sampling techniques for the monitoring of trace organic pollutants in water[J]. Environmental Chemistry, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
shu

水体微量有机物被动监测技术研究进展

  • 1.

    中国科学院青藏高原研究所青藏高原地表过程与环境变化重点实验室, 北京, 100101;

  • 2.

    中国科学院大学, 北京, 100049;

  • 3.

    中国科学院青藏高原地球科学卓越中心, 北京, 100101;

  • 4.

    山西财经大学资源型经济转型发展研究院, 太原, 030006

  • 基金项目:

    国家自然科学基金（41671480，41701083）资助.

Passive sampling techniques for the monitoring of trace organic pollutants in water

  • 1.

    Key Laboratory of Tibetan Environment Changes and Land Surface Processes, Institute of Tibetan Plateau Research, CAS, Beijing, 100101, China;

  • 2.

    University of Chinese Academy of Sciences, Beijing, 100049, China;

  • 3.

    CAS Center for Excellence in Tibetan Plateau Earth Sciences, Beijing, 100101, China;

  • 4.

    Institute of Resource-based Economic Transformation and Development Research, Shanxi Finance and Economics University, Taiyuan, 030006, China

  • Fund Project: Supported by the National Natural Science Foundation of China(41671480,41701083).

  • 摘要: 被动采样技术是一种待测物自发地由环境向采样器传输的采样方法，相对传统采样方法其装置小、成本低、检出限低，获得的监测结果为一段时间内的环境平均水平.该技术在水环境微量有机污染物的监测中具有极大优势，随水体中新型污染物的不断出现，被动采样技术在水体中的应用范围也不断扩大.本文概述了近40年来对水体被动采样技术的研究，介绍了该技术的发展、原理以及在不同水体中对新型污染物的应用，详细总结了应用中的不确定性因素和校正方法，分析了该技术目前存在的问题，并对其未来发展趋势和应用前景进行了展望.
    Abstract: Abstract Passive sampling, which works on the principle of the spontaneous transport of pollutants from the environment into the sampler, has a number of practical advantages by comparison with traditional grab sampling, including the simplicity of the device, cost effectiveness, low detection limit, and the yielding of results as time-weighted average concentrations. Passive sampling has been successfully applied in the detection of trace organic pollutants in water. However, with the emergence of newly occurring contaminants in water, the passive water sampling (PWS) technique have been applied more extensively. Here, we review the last 40 years of research on PWS, with a special focus on the development, principles and application of the technique in detecting emerging contaminants in different aquatic environments. Also detailed are the uncertainties and correction methods associated with PWS, before closing the paper with a discussion on the method's existing problems and its prospects in the future.
  • 加载中
  • [1] BAJWA A, ALI U, MAHMOOD A, et al. Organochlorine pesticides (OCPs) in the Indus River catchment area, Pakistan:Status, soil-air exchange and black carbon mediated distribution[J]. Chemosphere, 2016, 152:292-300.
    [2] SEETHAPATHY S, GORECKI T, LI X J. Passive sampling in environment analysis[J]. Journal of Chromatography A, 2008, 1184:234-253.
    [3] ALLAN I J, VRANA B, GREENWOOD R, et al. A "toolbox" for biological and chemical monitoring requirements for the European Union's Water Framework Directive[J]. Talanta, 2006, 69(2):302-322.
    [4] VRANA B, MILLS G A, ALLAN I J, et al. Passive sampling techniques for monitoring pollutants in water[J]. Trends in Analytical Chemistry, 2005, 24(10):845-868.
    [5] NOVIA A J, O'BRIEN D S, KASERZON S L, et al. Monitoring herbicide concentrations and loads during a flood event:A comparison of grab sampling with passive sampling[J]. Environmental Science & Technology, 2017, 51(7):3880-3891.
    [6] WU C C, YAO Y, BAO L J, et al. Fugacity gradients of hydrophobic organics across the air-water interface measured with a novel passive sampler[J]. Environmental Pollution, 2016, 218:1108-1115.
    [7] STUER-LAURIDSEN F. Review of passive accumulation devices for monitoring organic micropollutants in the aquatic environment[J]. Environmental Pollution, 2005, 136(3):503-524.
    [8] ASSOUMANI A, MARGOUM C, LOMBARD A, et al. How do PDMS-coated stir bars used as passive samplers integrate concentration peaks of pesticides in freshwater?[J]. Environmental Science and Pollution Research, 2017, 24(8):6844-6852.
    [9] O'BRIEN D, LEWIS S, DAVIS A, et al. Variability in pesticide exposure downstream of a heavily irrigated cropping area:Application of different monitoring techniques[J]. Journal of Agricultural and Food Chemistry, 2016, 64(20):3975-3989.
    [10] BOOP S K, MCLACHLAN M S, SCHIRMER K. Passive sampler for combined chemical and toxicological long-term monitoring of groundwater:The ceramic toximeter[J]. Environmental Science & Technology, 2007, 41(19):6868-6876.
    [11] KOT-WASIK A, ZABIEGALA B, URBANOWICZ M, et al. Advances in passive sampling in environmental studies[J]. Analytica Chimica Acta, 2007, 602(2):141-163.
    [12] 李亚男,陈宏,张居里,等. 薄膜梯扩散技术结合相研究进展[J]. 化学通报,2017,80(5):435-440.

    LI Y N, CHEN H, ZHANG J L, et al. Research progress in the binding phase of the diffusive gradients in thin-Films[J]. Chemistry, 2017, 80(5):435-440(in Chinese).

    [13] 罗婧,杨景富,张海全,等. 湖泊沉积物孔隙水磷酸盐含量原位监测技术研究进展[J]. 地球与环境,2014,42(5):688-694.

    LUO J, YANG J F, ZHANG H Q, et al. Progress in research on in-situ monitoring technology for determining the phosphate contents of sediment pore water[J]. Earth and Environment, 2014, 42(5):688-694(in Chinese).

    [14] 熊晶晶,李慧珍,马雪,等. 极性有机物整合采样技术在监测水环境中农药的应用[J]. 生态毒理学报,2017,12(4):2-14.

    XIONG J J, LI H Z, MA X, et al. Application of polar organic chemical integrative sampler on analyzing pesticides in water[J]. Asian Journal of Ecotoxicology, 2017, 12(4):2-14(in Chinese).

    [15] 谷云云,胡霞林,尹大强. 极性有机化合物整合采样技术在水环境有机污染物监测中的应用[J]. 环境化学,2013,32(7):1376-1386.

    GU Y Y, HU X L, YIN D J. Review:Applications of polar organic chemical integrative samplers in the monitoring of organic pollutants in the aquatic environment[J]. Environmental Chemistry, 2013, 32(7):1376-1386(in Chinese).

    [16] 范娟,周岩梅. LDPE膜被动采样技术预测模型的建立及其应用[J]. 中国环境科学,2015,35(11):3540-3545.

    FANG J, ZHOU Y M. The establishment and application of predict model for passive sampling technique with LDPE membranes[J]. China Environmental Science, 2015, 35(11):3340-3345(in Chinese).

    [17] 余益军,戴玄吏,董黎静,等. 被动采样在水体中有机污染监测的应用:以PAHs为例[J]. 环境监控与预警,2014,6(4):17-21.

    YU Y J, DAI X S, DONG L J, et al. Application of SPMD in monitoring and assessment of organic pollutants in water (take PAH as example)[J]. Environmental Monitoring and Forewarning, 2014, 6(4):17-21(in Chinese).

    [18] 张杰,张勇. SPMD技术的应用与研究进展[J]. 海洋环境科学,2001,20(4):67-74.

    ZHANG J, ZHANG Y. Development and application of SPMD technology in environmental research[J]. Marine Environmental Science, 2001, 20(4):67-74(in Chinese).

    [19] 董佳,孙挺,范洪涛. 一种新型动力学被动采样技术-化学捕收器[J]. 化学通报,2011,74(10):936-941.

    DONG J, SUN T, FAN H T. A new kinetic passive sampling technique-chemcatcher[J]. Chemistry, 2011, 74(10):936-941(in Chinese).

    [20] 黄润,戴飞鸿,陈少瑾. PDMS半透膜采样装置的制作研究[J]. 生态环境,2008,17(2):495-499.

    HUANG R, DAI F H, CHEN S J. The making and characterization of a semipermeable PDMS passive sampler[J]. Ecology and Environment, 2008, 17(2):495-499(in Chinese).

    [21] GORECKI T, NAMIESNIK J. Passive sampling[J]. Trends in Analytical Chemistry, 2002, 21(4):276-291.
    [22] BENES P. In situ dialysis for the determination of the state of trace elements in natural waters[J]. Water Research, 1974, 8(11):947-953.
    [23] DAVLSON W, ZHANG H. In situ speciation measurements of trace components in natural waters using thin-film gels[J]. Nature, 1994, 367(6463):546-548.
    [24] MORRISON G M P. Bioavailable metal uptake rate determination in polluted waters by dialysis with receiving resins[J]. Environmental Technology Letters, 1987, 8(8):393-402.
    [25] COURTENY K D, ANDREWS J E. Teratogenic evaluation and fetal deposition of hexabromobenzene (HBB) and hexafluorobenzene (HFB) in CD-1 mice[J]. Journal of Environmental Science and Health, Part B, 1984, 19(1):83-94.
    [26] SÖDERGREN A. Solvent-filled dialysis membranes simulate uptake of pollutants by aquatic organisms[J]. Environmental Science & Technology, 1987, 21(9):855-859.
    [27] DIGIANO F A, ELLIOT D, LEITH D. Application of passive dosimetry to the detection of trace organic contaminants in water[J]. Environmental Science & Technology, 1988, 22(11):1365-1367.
    [28] HUCKINS J N, TUBERGEN M W, MANUWEERA G K. Semipermeable membrane devices containing model lipid:A new approach to monitoring the bioavailability of lipophilic contaminants and estimating their bioconcentration potential[J]. Chemosphere, 1990, 20(5):533-552.
    [29] BOOIJ K, SLEIDERINK H M, SMEDES F. Calibrating the uptake kinetics of semipermeable membrane devices using exposure standards[J]. Environmental Toxicology and Chemistry, 1998, 17(7):1236-1245.
    [30] MULLER J F, MANOMANⅡ K, MORTIMER M R, et al. Partitioning of polycyclic aromatic hydrocarbons in the polyethylene/water system[J]. Fresenius' Journal of Analytical Chemistry, 2001, 371(6):816-822.
    [31] ALVAREZ D A, PETTY J D, HUCKINS J N, et al. Development of a passive, in situ, integrative sampler for hydrophilic organic contaminants in aquatic environments[J]. Environmental Toxicology and Chemistry, 2004, 23(7):1640-1648.
    [32] KINGSTON J K, GREENWOOD R, MILLS G A, et al. Development of a novel passive sampling system for the time-averaged measurement of a range of organic pollutants in aquatic environments[J]. Journal of Environmental Monitoring, 2000, 2(5):487-495.
    [33] GUO C S, ZHANG T T, HUO S, et al. Investigation and application of a new passive sampling technique for in situ monitoring of illicit drugs in waste waters and rivers[J]. Environmental Science & Technology, 2017, 51(16):9101-9108.
    [34] CHEN C E, ZHANG H, JONES K C. Jones, A novel passive water sampler for in situ sampling of antibiotics[J]. Journal of Environmental Monitoring, 2012, 14(6):1523-1530.
    [35] ZHANG H, DAVISON W. Diffusional characteristics of hydrogels used in DGT and DET techniques[J]. Analytica Chimica Acta, 1999, 398:329-340.
    [36] MIEGE C, MAZZELLA N, SCHIAVONE S, et al. An in situ inter-comparison exercise on passive samplers for monitoring metals, polycyclic aromatic hydrocarbons and pesticides in surface waters[J]. Trends in Analytical Chemistry, 2012, 36:128-143.
    [37] PETTY J D, HUCKINS J N, ALVAREZ D A, et al. A holistic passive integrative sampling approach for assessing the presence and potential impacts of waterborne environmental contaminants[J]. Chemosphere, 2004, 54(6):695-705.
    [38] BAO L J, XU S P, LIANG Y, et al. Development of a low-density polyethylene-containing passive sampler for measuring dissolved hydrophobic organic compounds in open waters[J]. Environmental Toxicology and Chemistry, 2012, 31(5):1012-1018.
    [39] LOHMANN R, MUIR D. Global Aquatic Passive Sampling (AQUA-GAPS):using passive samplers to monitor POPs in the waters of the world[J]. Environmental Science & Technology, 2010, 44(3):860-864.
    [40] BOOIJ K, BOMMEL R V, AKEN H M V, et al. Passive sampling of nonpolar contaminants at three deep-ocean sites[J]. Environmental Pollution, 2014, 195:101-108.
    [41] HUCKINS J N, MANUWEERA G K, PETTY J D, et al. Lipid-containing semipermeable membrane devices for monitoring organic contaminants in water[J]. Environmental Science & Technology, 1993, 27(12):2489-2496.
    [42] KOT A B, ZABIEGALA B, NAMIESNIK J. Passive sampling for long-term monitoring of organic pollutants in water[J]. Trends in Analytical Chemistry, 2000, 19(7):446-459.
    [43] VROBLESKY D A, LORAH M M, TRIMBLE S P. Mapping zones of contaminated ground-water discharge using creek-bottom-sediment vapor samplers, aberdeen proving ground, maryland[J]. Ground Water, 1991, 29(1):7-12.
    [44] KAPLAN E, BANERJEE S, RONEN D, et al. Multilayer sampling in the water-table region of a sandy aquifer[J]. Ground Water, 1991, 29(2):191-198.
    [45] VRANA B, PASCHKE A, POPP P, et al. An integrative passive sampler for monitoring organic contaminants in water[J]. Analytical Chemistry, 2001, 73(21):5191-5200.
    [46] BALTUSSEN E C, CRAMERS C A, SANDRA P J. Sorptive sample preparation——a review[J]. Analytical and Bioanalytical Chemistry, 2002, 373:3-22.
    [47] WENNRICH L, VRANA B, POPP P, et al. Development of an integrative passive sampler for the monitoring of organic water pollutants[J]. Journal of Environmental Monitoring, 2003, 5(5):813-822.
    [48] MAYER P, TOLLS J, HERMENS J L M, et al. Peer reviewed:Equilibrium sampling devices[J]. Environmental Science & Technology, 2003, 37(9):184A-191A.
    [49] STGEORGE T, VLAHOS P, HARNER T, et al. A rapidly equilibrating, thin film, passive water sampler for organic contaminants; characterization and field testing[J]. Environmental Pollution, 2011, 159(2):481-486.
    [50] VERBRUGGEN E M J, VAES W H J, PARKERTON T F, et al. Polyacrylate-coated SPME fibers as a tool to simulate body residues and target concentrations of complex organic mixtures for estimation of baseline toxicity[J]. Environmental Science & Technology, 2000, 34(2):324-331.
    [51] KRAAIJ R, MAYER P, BUSSER F J M, et al. Measured pore-water concentrations make equilibrium partitioning work a data analysis[J]. Environmental Science & Technology, 2003, 37(2):268-274.
    [52] PARROTT J, BACKUS S M, BORGMANN A, et al. The use of semipermeable membrane devices to concentrate chemicals in oil refinery effluent on the Mackenzie River[J]. Arctic, 1999, 52(2):125-138.
    [53] CHANG W T, FANG M D, LEE C L, et al. Measuring bioavailable PAHs in estuarine water using semipermeable membrane devices with performance reference compounds[J]. Marine Pollution Bulletin, 2014, 89:376-383.
    [54] LISSALDE S, MAZZELLA N, MAZELLIER P. Polar organic chemical integrative samplers for pesticides monitoring:impacts of field exposure conditions[J]. Science of the Total Environment, 2014, 488-489:188-196.
    [55] MAZZELLA N, LISSALDE S, MOREIRA S, et al. Evaluation of the use of performance reference compounds in an Oasis-HLB adsorbent based passive sampler for improving water concentration estimates of polar herbicides in freshwater[J]. Environmental Science & Technology, 2010, 44(5):1713-1719.
    [56] MAGI E, CARRO M D, MIRASOLE C, et al. Combining passive sampling and tandem mass spectrometry for the determination of pharmaceuticals and other emerging pollutants in drinking water[J]. Micro-chemical Journal, 2018, 136:56-60.
    [57] BAZ-LOMBA J A, HARMAN C, REID M, et al. Passive sampling of wastewater as a tool for the long-term monitoring of community exposure:Illicit and prescription drug trends as a proof of concept[J]. Water Research, 2017, 121:221-230.
    [58] SHI X, ZHOU J L, ZHAO H, et al. Application of passive sampling in assessing the occurrence and risk of antibiotics and endocrine disrupting chemicals in the Yangtze Estuary, China[J]. Chemosphere, 2014, 111:344-351.
    [59] CHEN W, LI Y Y, CHEN C E, et al. DGT Passive sampling for quantitative in situ measurements of compounds from household and personal care products in waters[J]. Environmental Science & Technology, 2017, 51(22):13274-13281.
    [60] VRANA B, MILLS G A, KOTTERMAN M, et al. Modelling and field application of the Chemcatcher passive sampler calibration data for the monitoring of hydrophobic organic pollutants in water[J]. Environmental Pollution, 2007, 145(3):895-904.
    [61] SHAW M, FURNAS M, FABRICIUS K, et al. Monitoring pesticides in the Great Barrier Reef[J]. Marine Pollution Bulletin, 2010, 60(1):113-122.
    [62] KENNEDY K, SCHROEDER T, SHAW M, et al. Long term monitoring of photosystem Ⅱ herbicides——correlation with remotely sensed freshwater extent to monitor changes in the quality of water entering the Great Barrier Reef, Australia[J]. Marine Pollution Bulletin, 2012, 65(4-9):292-305.
    [63] SMITH R, MIDDLEBROOK R, TURNER R, et al. Large-scale pesticide monitoring across great barrier reef catchments——paddock to reef integrated monitoring, modelling and reporting program[J]. Marine Pollution Bulletin, 2012, 65:117-127.
    [64] MOSCHET C, VERMEIRSSEN E L M, SINGER H, et al. Evaluation of in-situ calibration of chemcatcher passive samplers for 322 micropollutants in agricultural and urban affected rivers[J]. Water Research, 2015, 71:306-317.
    [65] CASTLE G D, MILLS G A, BAKIR A, et al. Calibration and field evaluation of the Chemcatcher(R) passive sampler for monitoring metaldehyde in surface water[J]. Talanta, 2018, 179:57-63.
    [66] HOFELT C S, SHEA D. Accumulation of organochlorine pesticides and pcbs by semipermeable membrane devices and mytilus edulisin new bedford harbor[J]. Environmental Science & Technology, 1997, 31(1):154-159.
    [67] GRANMO A, EKELUND R, BERGGEN M, et al. Temporal trend of organochlorine marine pollution indicated by concentrations in mussels, semipermeable membrane devices, and sediment[J]. Environmental Science & Technology, 2000, 34(16):3323-3329.
    [68] BERGQVIST P, STRANDBERG B, EKELUND R. Temporal monitoring of organochlorine compounds in seawater by semipermeable membranes following a flooding episode in western Europe[J]. Environmental Science & Technology, 1998, 32(24):3887-3892.
    [69] AMINOT Y, BELLES A, ALARY C, et al. Near-surface distribution of pollutants in coastal waters as assessed by novel polyethylene passive samplers[J]. Marine Pollution Bulletin, 2017, 119(1):92-101.
    [70] BUENO M M J, HERRERA S, MUNARON D, et al. POCIS passive samplers as a monitoring tool for pharmaceutical residues and their transformation products in marine environment[J]. Environmental Science and Pollution Research, 2016, 23(6):5019-5029.
    [71] BRUMOVSKY M, BECANOVA J, KOHOUTEK J, et al. Contaminants of emerging concern in the open sea waters of the western mediterranean[J]. Environment Pollution, 2017, 229:976-983.
    [72] MARTIN H, PATTERSON B M, DAVIS G B. Field trial of contaminant groundwater monitoring:Comparing time-integrating ceramic dosimeters and conventional water sampling[J]. Environmental Science & Technology, 2003, 37(7):1360-1364.
    [73] BOPP S, WEISS H, SCHIRMER K. Time-integrated monitoring of polycyclic aromatic hydrocarbons (PAHs) in groundwater using the ceramic dosimeter passive sampling device[J]. Journal of Chromatography A, 2005, 1072(1):137-147.
    [74] GUSTAVSON K E, HARKIN J M. Comparison of sampling techniques and evaluation of semipermeable membrane devices (SPMDs) for monitoring polynuclear aromatic hydrocarbons (PAHs) in groundwater[J]. Environmental Science & Technology, 2000, 34(20):4445-4451.
    [75] SACKS V P, LOHMANN R. Freely dissolved PBDEs in water and porewater of an urban estuary[J]. Environmental Pollution, 2012, 162:287-293.
    [76] SOULIER C, COUREAU C, TOGOLA A. Environmental forensics in groundwater coupling passive sampling and high resolution mass spectrometry for screening[J]. Science of the Total Environment, 2016, 563-564:845-854.
    [77] MALI N, CERAR S, KOROSA A, et al. Passive sampling as a tool for identifying micro-organic compounds in groundwater[J]. Science of the Total Environment, 2017, 593-594:722-734.
    [78] CERAR S, MALI N. Assessment of presence, origin and seasonal variations of persistent organic pollutants in groundwater by means of passive sampling and multivariate statistical analysis[J]. Journal of Geochemical Exploration, 2016, 170:78-93.
    [79] ESTEVE-TURRILLAS F A, PASTOR A, YUSA V, et al. Using semi-permeable membrane devices as passive samplers[J]. Trends in Analytical Chemistry, 2007, 26(7):703-712.
    [80] BOOIJ K, VANBOMMEL R, METS A, et al. Little effect of excessive biofouling on the uptake of organic contaminants by semipermeable membrane devices[J]. Chemosphere, 2006, 65(11):2485-2492.
    [81] BOOIJ K, HOFMANS H, FISCHER C, et al. Temperature-dependent uptake rates of nonpolar organic compounds by semipermeable membrane devices and low-density polyethylene membranes[J]. Environmental Science & Technology, 2003, 37(2):361-366.
    [82] ESTOPPEY N, SCHOPFER A, OMLIN J, et al. Effect of water velocity on the uptake of polychlorinated biphenyls (PCBs) by silicone rubber (SR) and low-density polyethylene (LDPE) passive samplers:an assessment of the efficiency of performance reference compounds (PRCs) in river-like flow conditions[J]. Science of the Total Environment, 2014, 499:319-326.
    [83] BOOIJ K, SMEDES F, VANWEERLEE E M. Spiking of performance reference compounds in low density polyethylene and silicone passive water samplers[J]. Chemosphere, 2002, 46(8):1157-1161.
    [84] BOOIJ K, VANDROOGE B L. Polychlorinated biphenyls and hexachlorobenzene in atmosphere, sea-surface microlayer, and water measured with semi-permeable membrane devices (SPMDs). Chemosphere, 2001, 44(2):91-98.
    [85] VRANA B, MILLS G A, DOMINIAK E, et al. Calibration of the Chemcatcher passive sampler for the monitoring of priority organic pollutants in water[J]. Environmental Pollution, 2006, 142(2):333-343.
    [86] CRISTALE J, KATSOYIANNIS A, CHEN C E, et al. Assessment of flame retardants in river water using a ceramic dosimeter passive sampler[J]. Environmental Pollution, 2013, 172:163-169.
    [87] ARDITSOGLOU A, VOUTSA D. Passive sampling of selected endocrine disrupting compounds using polar organic chemical integrative samplers[J]. Environmental Pollution, 2008, 156(2):316-324.
    [88] MULLER R, TANG J Y M, THEIR R, et al. Combining passive sampling and toxicity testing for evaluation of mixtures of polar organic chemicals in sewage treatment plant effluent[J]. Journal of Environmental Monitoring, 2007, 9(1):104-109.
    [89] O'BRIEN D S, BARTKOW M, MUELLER J F. Determination of deployment specific chemical uptake rates for SDB-RPD Empore disk using a passive flow monitor (PFM)[J]. Chemosphere, 2011, 83(9):1290-1295.
    [90] O'BRIEN D S, CHISWELL D B, MUELLER J F. A novel method for the in situ calibration of flow effects on a phosphate passive sampler[J]. Journal of Environmental Monitoring, 2009, 11:212-219.
    [91] POULIER G, LISSALDE S, CHARRIAU A, et al. Can POCIS be used in water framework directive (2000/60/EC) monitoring networks? A study focusing on pesticides in a French agricultural watershed[J]. Science of the Total Environment, 2014, 497-498:282-292.
    [92] SCHAFER R B, PASCHKE A, LIESS M. Freely dissolved PBDEs in water and porewater of an urban estuary[J]. Journal of Chromatography A, 2008, 1203(1):1-6.
    [93] GUNOLD R, SCHAFER R B, PASCHKE A, et al. Calibration of the Chemcatcher passive sampler for monitoring selected polar and semi-polar pesticides in surface water[J]. Environmental Pollution, 2008, 155(1):52-60.
    [94] BAO L J, YOU J, ZENG E Y. Sorption of PBDE in low-density polyethylene film:implications for bioavailability of BDE-209[J]. Environmental Toxicology and Chemistry, 2011, 30(8):1731-1738.
    [95] BIANCO-PREVOT A, FABBRI D, PRAMAURO E, et al. Continuous monitoring of photocatalytic treatments by flow injection. Degradation of dicamba in aqueous TiO2 dispersions[J]. Chemosphere, 2001, 44(2):249-255.
    [96] LOHMANN R, BOOIJ K, SMEDES F, et al. Use of passive sampling devices for monitoring and compliance checking of POP concentrations in water[J]. Environmental Science and Pollution Research, 2012, 19(6):1885-1895.
    [97] BOOIJ K, SMEDES F. An improved method for estimating in situ sampling rates of nonpolar passive samplers[J]. Environmental Science & Technology, 2010, 44(17):6789-6794.
    [98] PASCHKE A, SCHWAB K, BRUMMER J, et al. Rapid semi-continuous calibration and field test of membrane-enclosed silicone collector as passive water sampler[J]. Journal of Chromatography A, 2006, 1124:187-195.
    [99] HUCKINS J N, PETTY J, ORAZIO C E, et al. Determination of uptake kinetics (Sampling rates) by lipid-containing semipermeable membrane devices (SPMDs) for polycyclic aromatic hydrocarbons (PAHs) in water[J]. Environmental Science & Technology, 1999, 33(21):3918-3923.
    [100] VRANA B, SCHUURMANN G. Calibrating the uptake kinetics of semipermeable membrane devices in water:Impact of hydrodynamics[J]. Environmental Science & Technology, 2002, 36(2):290-296.
    [101] PREST H F, JARMAN W M, BURNS S A, et al. Passive water sampling via semipermeable membrane devices (SPMDS) in concert with bivalves in the Sacramento/San Joaquin River Delta[J]. Chemosphere, 1992, 25(12):1811-1823.
    [102] RICHARDSON B J, LAM P K S, ZHENG G J, et al. Biofouling confounds the uptake of trace organic contaminants by semi-permeable membrane devices (SPMDs)[J]. Marine Pollution Bulletin, 2002, 44(12):1372-1379.
    [103] HUCKINS J N, PETTY J, LEBO J A, et al. Development of the permeability/performance reference compound approach for in situ calibration of semipermeable membrane devices[J]. Environmental Science & Technology, 2002, 36(1):85-91.
  • 加载中
WeChat 点击查看大图
计量
  • 文章访问数:  1897
  • HTML全文浏览数:  1861
  • PDF下载数:  195
  • 施引文献:  0
出版历程
  • 收稿日期:  2017-12-25
  • 刊出日期:  2018-08-15
陈梦珂, 王传飞, 龚平, 任娇, 王小萍. 水体微量有机物被动监测技术研究进展[J]. 环境化学, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
引用本文: 陈梦珂, 王传飞, 龚平, 任娇, 王小萍. 水体微量有机物被动监测技术研究进展[J]. 环境化学, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
shu
CHEN Mengke, WANG Chuanfei, GONG Ping, REN Jiao, WANG Xiaoping. Passive sampling techniques for the monitoring of trace organic pollutants in water[J]. Environmental Chemistry, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
Citation: CHEN Mengke, WANG Chuanfei, GONG Ping, REN Jiao, WANG Xiaoping. Passive sampling techniques for the monitoring of trace organic pollutants in water[J]. Environmental Chemistry, 2018, 37(8): 1831-1841. doi: 10.7524/j.issn.0254-6108.2017122504
shu

水体微量有机物被动监测技术研究进展

  • 1.  中国科学院青藏高原研究所青藏高原地表过程与环境变化重点实验室, 北京, 100101;
  • 2.  中国科学院大学, 北京, 100049;
  • 3.  中国科学院青藏高原地球科学卓越中心, 北京, 100101;
  • 4.  山西财经大学资源型经济转型发展研究院, 太原, 030006
  • 收稿日期:  2017-12-25
基金项目:

国家自然科学基金（41671480，41701083）资助.

摘要: 被动采样技术是一种待测物自发地由环境向采样器传输的采样方法，相对传统采样方法其装置小、成本低、检出限低，获得的监测结果为一段时间内的环境平均水平.该技术在水环境微量有机污染物的监测中具有极大优势，随水体中新型污染物的不断出现，被动采样技术在水体中的应用范围也不断扩大.本文概述了近40年来对水体被动采样技术的研究，介绍了该技术的发展、原理以及在不同水体中对新型污染物的应用，详细总结了应用中的不确定性因素和校正方法，分析了该技术目前存在的问题，并对其未来发展趋势和应用前景进行了展望.

English Abstract

    全文HTML

参考文献 (103)

返回顶部

目录

/

返回文章
返回

Copyright © 2019 中国科学院生态环境研究中心