Zusammenfassung
Die Verfügbarkeit von qualitativ hochwertigem Wasser ist ein wichtiger Aspekt für den Schutz der belebten Umwelt und der Lebensqualität des Menschen. Bei der Überwachung der Qualität von Grund- und Oberflächenwasser kommt der Probennahme eine entscheidende Rolle zu. Dabei ist die zeitintegrierte Anreicherung von Schadstoffen in der Umwelt mittels passiver Probennehmer eine attraktive Alternative zur konventionellen Stichprobennahme. Durch einein situ Aufkonzentrierung ermöglichen passive Probennehmer das Erfassen auch gering konzentrierter Kontaminanten bei gleichzeitiger Reduzierung von Kosten und Aufwand für eine kontinuierliche Überwachung. Man erhält Informationen über den gesamten Beprobungszeitraum und vermeidet Transport und Lagerung großer Probenvolumina. Matrixeffekte werden durch die selektive Anreicherung verringert.
Verschiedene Passivsammler werden bisher zur Beprobung im aquatischen Bereich eingesetzt. Anfangs wurden wassergefüllte Dialyse-Schläuche verwendet, um Spurenelemente zu bestimmen. Später wurden Lösemittel-gefüllte Sammler und Trioleingefüllte “Semipermeable Membrane Devices” (SPMDs) eingesetzt. In neueren Entwicklungen werden als Sammler-Phase sorptive Festphasen verwendet. Beispiele hierzu sind die “Solid Phase Microextraction” (SPME) und das “Membrane Enclosed Sorptive Coating” System (MESCO). Neben der Miniaturisierung haben diese beiden Probennehmer den Vorteil, dass sie thermodesorbierbar sind und somit ohne den Einsatz von Lösemitteln chemisch analysiert werden können.
Gegenwärtig werden die gewonnenen Proben vom Probennehmer mittels Lösemitteln extrahiert oder thermodesorbiert und meist chemisch analysiert. Im Sinne einer kombinierten chemisch-biologischen Analyse wäre es jedoch wünschenswert, die passive Probennahme auch direkt mit toxikologischen Bewertungsverfahren zu verknüpfen. Es ist deshalb unser Ziel, einen passiven Probennehmer so zu konstruieren, dass die gesammelten sammelten Proben direkt, das heißt ohne Extraktion, in toxikologischen Tests untersucht werden können, wobei der Sammler als Expositionskammer dient. Das dem zu Grunde liegende Prinzip ist die Remobilisierung oder die direkte Verfügbarkeit adsorbierter Kontaminanten für die biologischen Testsysteme.
Abstract
The availability of high-quality water plays a pivotal role for the protection of the ecosystem and the quality of human life. An important step in assessing ground and surface water quality is sampling. The time-integrated accumulation of environmental contaminants by passive sampling is an attractive alternative to conventional snap-shot sampling. Thein situ accumulation during passive sampling allows the detection of even lowconcentrated contaminants and reduces cost and time for continuous monitoring. Passive sampling provides information on the whole sampling period and avoids the transport and storage of large sample volumes. Matrix effects are reduced due to the selective enrichment.
Various passive samplers have been developed for sampling in aqueous media. Early developments used water filled dialysis tubes for the sampling of trace elements. Later on, solvent filled devices and triolein-filled semipermeable membrane devices (SPMDs) were deployed. More recent developments use a solid rather than a liquid sorbent as the receiving phase. Examples of this are the solid phase microextraction (SPME) and the membrane enclosed sorptive coating (MESCO). In addition to comprising miniature devices, SPMEs as well as MESCO are thermodesorbable and, as such, no longer require solvent extraction.
Conventionally the sampled contaminants are removed from the passive sampling devices by solvent extraction or thermodesorption in order to be analyzed chemically. For an in-depth analysis of sampled analytes, however, it would be advantageous to modify passive sampling such that sampled contaminants can also be analyzed biologically. Thus, it is our goal to construct a passive sampling device that serves both as a sampling device as well as an exposure chamber for toxicity testing. The principle underlying this technology is the bioavailability of sorbed contaminants, thereby eliminating the need for solvent extraction.
Abbreviations
- MESCO:
-
Membrane Enclosed Sorptive Coating
- POCIS:
-
Polar Organic Chemical Integrative Sampler
- SPMD:
-
Semipermeable Membrane Devices
- SPME:
-
Solid Phase Microextraction
Literatur
Alvarez DA, Huckins JN, Petty JD (1999): Progress towards the development of a passive, in situ, SPMD-like sampler for hydrophilic organic contaminants in aquatic environment. 20th Annual National Meeting of the Society of Environmental Toxicology and Chemistry, November, 1999, Philadelphia, PA, PWA096.
Arthur CL, Pawliszyn J (1990): Solid phase microextraction with thermal desorption using fused silica optical fibers. Analytical Chemistry62, 2145–2148
Baun B, Jensen SD, Bjerg PL, Christensen TH, Nyholm N (2000): Toxicity of organic chemical pollution in groundwater downgradient of a landfill (Grinsted, Denmark). Environmental Science and Technology34, 1647–1652
Benes P, Steinnes E (1974): In situ dialysis for the detemination of the stat of trace elements in natural waters. Water Research8, 947–953
Booij K, Sleiderink HM, Smedes F (1998): Calibrating the uptake kinetics of semipermeable membrane devices using exposure standards. Environmental Toxicology and Chemistry17, 1236–1245
Brack W, Altenburger R, Ensenbach U, Möder M, Segner H, Schüürmann G (1999): Bioassay-directed identification of organic toxicants in river sediment in the industrial region of Bitterfeld (Germany) — A contribution to hazard assessment. Archives of Environmental Contamination and Toxicology37, 164–174
Brown RS, Akhtar P, Akerman J, Hampel L, Kozin IS, Villerius LA, Klamer HJC (2001): Partition controlled delivery of hydrophobic substances in toxicity tests using poly(dimethylsiloxane) (PDMS) films. Environmental Science and Technology35, 4097–4102
Burmaster DE, Menzie CA, Freshman JS (1991): Assessment of methods for estimating aquatic hazards at superfund-type sites: a cautionery tale. Environmental Toxicology and Chemistry10, 827–842
Davison W, Fones G, Harper M, Teasdale P, Zhang H (2000): Dialysis, DET and DGT: in situ diffusional techniques for studying water, sediments and soils. In: Buffle J, Horvai G (Hrsg): In situ monitoring of aquatic systems — chemical analysis and speciation. Wiley, pp. 495–569
Davison W, Zhang H (1994): In situ speciation measurements of trace components in natural waters using thin-film gels. Nature367, 546–548
DiGiano FA, Elliot D, Leith D (1988): Application of passive dosimetry to the detection of trace organic contaminants in water. Environmental Science and Technology22, 1365–1367
Effenberger M, Weiss H, Popp P, Schirmer M (2001): Untersuchungen zum Benzininhaltstoff Methyl-tertiär-butylether (MTBE) in Grund- und Oberflächenwasser in Deutschland. Grundwasser6, 51–60
Einfeld W, Koglin EN (2000): Groundwater sampling technologies — Gore-Sorber® water quality monitoring, Environmental Technology Verification Report. EPA/600/R-00/091
Grathwohl P (1999): Dosimeter Deutsches Patent [DE 198 30 413 A1]
Haas R, Oeste FD (2001): Passivsammler zur Wasseruntersuchung. UWSF — Z Umweltchem Ökotox13, 2–4
Helma C, Eckl P, Gottmann E, Kassie F, Rodinger W, Steinkeller H, Windpassinger C, Schulte-Hermann R (1998): Genotoxic and ecotoxic effects of groundwaters and their relation to routinely measured chemical parameters. Environmental Science and Technology32, 1799–1805
Hesslein RH (1976): Anin situ sampler for close interval pore water studies. Limnology and Oceanography21, 912–914
Huckins JN, Petty JD, Lebo J, Almeida FV, Alvarez DA, Cranor WL, Clark RC (2000): Overview of the Permeability/Perfomance Reference Compound (PRC) approach forin situ recalibration/ calibration of SPMD environments. 21th Annual National Meeting of the Society of Environmental Toxicology and Chemistry, November, 2000, Nashville, PMP025
Huckins JN, Tubergen MW, Manuweera GK (1990): Semipermeable membrane devices containing model lipid: a new approach to monitoring the bioavailability of lipophilic contaminants and estimating their bioconcentration potential. Chemosphere20, 533–552
Kingston JK, Greenwood R, Mills GA, Morrison GM, Persson LB (2000): Development of a passive sampling system for the timeaveraged measurement of a range of organic pollutants in aquatic environments. Journal of Environmental Monitoring2, 487–495
Lefkovitz L, Crecelius E (1996): The use of SPMDs consisting of polyethylene alone to predict dissolved-phase organics in the Columbia River. Poster presented at the 17th Annual Meeting of the SETAC, Washington D.C., USA (Abstract P0523)
Litten S, Mead B, Hassett J (1993): Application of passive samplers (PISCES) to locating a source of PCBs on the Black River, New York. Environmental Toxicology and Chemistry12, 639–647
Mayer LM (1976): Chemical water sampling in lakes and sediments with dialysis bags. Limnology and Oceanography21, 909–912
Mayer P, Wernsing J, Tolls J, DeMaagd PG-J, Sijm DTHM (1999): Establishing and controlling dissolved concentrations of hydrophobic organics by partitioning from a solid phase. Environmental Science and Technology33, 2284–2290
Müller L, Górecki T, Pawliszyn J (1999): Optimization of the SPME device design for field applications. Fresenius Journal of Analytical Chemistry364, 610–616
NAVFAC (2000): Diffusion membrane samplers — A low-cost alternative groundwater monitoring tool for VOCs. TechData Sheet, NFESC TDS-2085-ENV
Negrào MR, Alpendurada MF (2001): Solvent-free method for the determination of polynuclear aromatic hydrocarbons in waste water by solid-phase microextraction-high-performance liquid chromatography with photodiode-array detection. Journal of Chromatography A823, 211–218
Nilsson T, Montanarella L, Baglio D, Tilio R, Bidoglio G, Facchetti S (1998): Analysis of volatile organic compounds in environmental water samples and soil gas by solid-phase microextraction. Journal of Environmental Analytical Chemistry69, 217–226
Parrott JL, Backus SM, Borgmann AL, Swyripy M (1999): The use of semipermeable membrane devices to concentrate chemicals in oil refinery effluents on the Mackenzie River. Arctic52, 125–138
Pawliszyn J (1997): Solid Phase Microextraction — Theory and Practive. Wiley-VCH, New York
Peterson SM, Apte SC, Batley GE, Coade G (1995): Passive samplers for chlorinated pesticides in estuarine waters. Chemical speciation and bioavailability7, 83–88
Petty JD, Jones SB, Huckins JN, Cranor WL, Parris JT, McTague TB, Boyle TP (2000b): An approach for assessment of water quality using semipermeable membrane devices (SPMDs) and bioindicator tests. Chemosphere41, 311–321
Petty JD, Orazio CE, Huckins JN, Gale RW, Lebo JA, Meadows JC, Echols KR, Cranor WL (2000a): Considerations involved with the use of semipermeable membrane devices for monitoring environmental contaminants (Review). Journal of Chromatography A879, 83–95
Puls RW, Paul CJ (1997): Multi-layer sampling in conventional monitoring wells for improved estimation of vertical contaminant distribution and mass. Journal of Contaminant Hydrology25, 85–111
Sabaliunas D, Ellington J, Sabaliuniene I (1999): Screening bioavailable hydrophobic toxicants in surface waters with semipermeable membrane devices: role of inherent oleic acid in toxicity evaluation. Ecotoxicology and Environmental Safety44, 160–167
Sabaliunas D, Södergren A (1996): Uptake of organochlorine pesticides by solvent-filled cellulose and polyethylene membranes. Ecotoxicology and Environmental Safety35, 150–155
Schirmer K, Altenburger R, Weiss H, Schüürmann G (2001): Toxicological monitoring of a contaminant plume for implementing Natural Attenuation as a remediation option. 11th Annual Meeting of the Society of Environmental Toxicology and Chemistry (SETAC) Europe, Madrid, Spain, May 6–10, #338
Schirmer K, Bols N, Schirmer M (2001): Sampling and toxicity monitoring device and method. US patent application, submitted July 2001 [No. 09/908, 690]
Schirmer K, Bols NC (1999): Adsorption, distribution and bioavailability of fluoranthene in microwell plates. 9th Annual Meeting of the Society of Environmental Toxicology and Chemistry, Leipzig, Germany, May 25–29, 2e/P005
Schirmer K, Chan AGJ, Greenberg BM, Dixon DG, Bols NC (1997): Methodology for demonstrating and measuring the photocytotoxicity of fluoranthene to fish cells in culture. Toxicology In Vitro11, 107–119
Schirmer K, Herbrick JS, Greenberg BM, Dixon DG, Bols NC (1999): The use of fish gill cells in culture to evaluate the cytotoxicity and photocytotoxicity of intact and photomodified creosote. Environmental Toxicology and Chemistry18, 1277–1288
Schirmer K, Tom DJ, Bols NC, Sherry JP (2001b): Ability of fractionated petroleum refinery effluent to elicit cyto- and photocytotoxic responses and to induce 7-ethoxyresorufin-odeethylase activity in fish cell lines. The Science of the Total Environment271, 61–78
Snyder SA, Villeneuve DL, Snyder EM, Giesy JP (2001): Identification and quantification of estrogen receptor agonists in waste water effluents. Environmental Science and Technology35, 3620–3625
Sorge H, Götzelmann P, Nallinger M (1994): Passives Adsorptionsverfahren zur Erkundung von Organischen Kontaminationen. Terra Tech8
Södergren A (1987): Solvent-filled dialysis membranes simulate uptake of pollutants by aquatic organisms. Environmental Science and Technology21, 855–859
Södergren A (1990): Monitoring of persistent, lipophilic pollutants in water and sediment by solvent-filled dialysis membranes. Ecotoxicology and Environmental Safety19, 143–149
Vrana B, Popp P, Paschke A, Schüürmann G (2001): Membrane enclosed sorptive coating (MESCO). An integrative passive sampler for monitoring organic contaminants in water. Analytical Chemistry73 (21) 5191–5200
Vrana B, Schüürmann G (2002): Calibrating the uptake kinetics of semipermeable membrane devices in water: the impact of hydrodynamics. Environmental Science and Technology36 (2), 290–296
Whyte JJ, Karrow NA, Boehrmann HJ, Dixon DG, Bols NC (2000): Combined methodologies for measuring exposure of rainbow trout (Oncorhynchus mykiss) to polycyclic aromatic hydrocarbons (PAHs) in creosote contaminated microcosms. Polycyclic Aromatic Compounds18, 71–98
Zabik JM, Aston LS, Seiber JN (1992): Rapid characterization of pesticide residues in contaminated soils by passive sampling devices. Environmental Toxicology and Chemistry11, 765–770
Author information
Authors and Affiliations
Corresponding author
Additional information
OnlineFirst: 20. 02. 2002
Stephanie Bopp studierte Geoökologie an der Universität Bayreuth mit den Schwerpunkten Umweltchemie und Ökotoxikologie. SeitApril 2001 arbeitet sie rn Rahmen einer Promotion an der Umsetzung des passiven Probennahmegerätes, welches ein kombiniertes chemisch-toxikologisches Monitoring von kontaminiertem Grundwasser ermoglichen soll.
Kristin Schirmerist seit Juli 2001 Leiterin der Nachwuchsgruppe für Molekulare Tierzelltoxikologie am UFZ-Umweltforschungszentrum in Leipzig. Ihre Forschungsinteressen liegen in der Etablierung vonin vitro-Systemen zur Aufklärung von Schadstoffwirkungen in Vertebratenzellen und in der Entwicklung von Technologien zur frühzeitigen Detektion dieser Schadstoffwirkungen in der Umwelt.
Rights and permissions
About this article
Cite this article
Bopp, S.K., Schirmer, K. Passivsammler für die zeitintegrierte chemische und toxikologische Überwachung des Schadstoffgehaltes in Grund- und Oberflächenwasser. UWSF - Z Umweltchem Ökotox 14, 45–51 (2002). https://doi.org/10.1007/BF03038658
Received:
Accepted:
Issue Date:
DOI: https://doi.org/10.1007/BF03038658