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Eingeladener Vortrag
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Since semi-volatile organic compounds (SVOCs), including biocides and polychlorinated biphenyls (PCBs), occur indoors as well as outdoors, air sampling adsorbents and measuring methods for all these compounds are indispensable. This paper presents the initial steps in the development of such a method, the aim of which is the analysis of selected compounds in the above-mentioned classes using low air sampling volumes and air-exchange rates close to zero, as is common in museum showcases. For measurements under easily controlled conditions, a micro-chamber system was used at different temperatures. A surface modified styrene divinylbenzene (SDVB) polymer was selected as the air sampling adsorbent for the elution experiments. After successfully performing pretests using the micro-chamber system with target compound solutions, the emissions of these compounds from self-soaked wood samples and con-taminated wood samples were investigated for method development.
Die meisten organischen Biozide gehören zu der Gruppe der schwerflüchtigen organischen Verbindungen (SVOC – semi volatile organic compounds). Zu den klassischen Bioziden zählen u.a. Lindan, Pentachlorphenol (PCP) und Dichlordiphenyltrichlorethan (DDT) und zu den neueren u.a. Dichlofluanid, Tebuconazol und Permethrin. Biozide kamen in Museen vor allem in den 50er und 60er Jahren zum Schutz der Exponate zum Einsatz, hauptsächlich in Depoträumen zum akuten und zum präventiven Schutz vor Schadorganismen.
Die meisten organischen Biozide gehören zu der Gruppe der schwerflüchtigen organischen Verbindungen (SVOC – semi volatile organic compounds). Zu den klassischen Bioziden zählen u.a. Lindan, Pentachlorphenol PCP) und Dichlordiphenyltrichlorethan (DDT) und zu den neueren u.a. Dichlofluanid, Tebuconazol und Permethrin. Biozide kamen in Museen vor allem in den 50er und 60er Jahren zum Schutz der Exponate zum Einsatz,1 wo sie hauptsächlich in Depoträumen zu finden sind, in welchen sie zum akuten und zum präventiven Schutz vor Schadorganismen eingesetzt wurden.2 Im Laufe der Zeit wurde jedoch festgestellt, dass sich der Einsatz von Bioziden negativ auf die menschliche Gesundheit auswirkt und auch zu Schäden an den behandelten Exponaten führen kann. 3 Verschiedene Möglichkeiten der Biozidanalytik und der Einfluss von Senkeneffekten auf die Analytik werden in diesem Beitrag vorgestellt.
A method for the determination of very volatile organic compounds (VVOC) in air was developed and successfully tested for methanol and ethanol. Carbotrap 300 (R) (a multi-bed tube using Carbopack C (R), Carbopack B (R) and Carbosive SIII (R)) was selected as sorption material for thermal desorption and tested for its suitability for emission test chamber measurements. The adsorption behaviour and the chromatographic results are influenced negatively by spiking aqueous solutions on the adsorption medium for calibration purposes. The latter effect can be reduced by blowing dry air across the adsorbent to remove the adsorbed water. Detection and quantification limits were determined for a GC-FID system and compared to GC-MS. The applicability of the method was tested with a methanol eliminating silane modified polymeric adhesive (SMP-adhesive for parquet) in an emission test chamber.
Volatile organic compounds (VOC) are ubiquitous in the indoor air, since they emit from materials used indoors. Investigations of these materials are mostly carried out in test chambers under controlled climatic conditions. Quality control of these test chamber measurements is important but there is a lack of commercially available homogenous reference materials. The approach of this study is to dope a supporting material with VOCs, which are then reproducibly released in measurable chamber air concentrations between 30 to 300 µg m ³. From several tested supporting materials vacuum grease (APIEZON M) was selected because of its very low own emissions. First tests were conducted with styrene. For the estimation of the initial emission and the emission over time FEM (finite element methods) modelling was used. Based on this, five samples with a surface of 7 cm2 and a thickness of 12 mm with a content of 1 ‰ styrene were investigated at (23 ± 2) °C and (50 ± 5) % relative humidity in the µ-chamber (3 samples) and 24 L test chambers (2 samples) for 28 days. Air samples were taken after 24 hours, 3, 7, 14, 21 and 28 days on Tenax TA® sorption tubes and analyzed by TD-GC-MS. The area specific emission rate (SERa) was calculated to compare the results from both chamber types. After 24 hours SERa was between 0.8 0.9 µg cm 2 h 1 (3800 4000 µg m 3) for the µ-chamber samples and between 0.9 1.1 µg cm 2 h 1 (300-370 µg m 3) for the 24 L test chamber samples. After 28 days the SERa was at 0.2 µg cm 2 h 1 for all samples. The relative standard deviation of the SERa was between 1 26 %. These results show the applicability of vacuum grease as supporting material and the favored starting concentration range could be achieved in the 24 L test chambers.