- P-ISSN 1225-0163
- E-ISSN 2288-8985
건축자재에서 방출되는 오염물질을 평가하는 20 L 시험챔버법은 챔버 내부에 노출되는 시료의 표면방출만을 측정한다. 일정한 크기로 절단한 시편을 알루미늄 호일로 감싼 후 시편홀더에 고정시켜 20 L 시험챔버 내에 위치시킨 후 방출시험을 실시한다. 이때 시편홀더의 기밀성이 보장되지 못한다면 시료절단면에서 방출되는 오염물질로 인하여 정확한 평가가 이루어질 수 없다. 이러한 절단면의 영향은 표면처리를 하여 표면에서 보다 절단면에서 더 많은 오염물질이 방출되는 판상재(합판, 장판) 시료의 경우 더 크다. 이 연구에서는 바닥재로 사용되는 장판을 대상으로 20 L 시험챔버와 1 L 시험챔버의 방출시험결과를 비교하여 시편홀더의 기밀성을 확인하였다. 또한 가구재로 사용되는 LPM 양면처리한 MDF를 대상으로 현행의 시험방법과 시료절단면을 VOC 저방출 tape으로 밀봉한 방법을 비교하여 시편홀더의 부족한 기밀성의 개선이 가능하지 확인하였다. LPM 양면처리한 MDF의 7일 경과 후 방출강도는 TVOC의 경우 Tape 사용 유무에 따라 각각 <TEX>$0.009mg/m^2h$</TEX>, <TEX>$0.003mg/m^2h$</TEX>로 기밀성을 보완할 수 있었다. 또한 n
The 20 L small chamber test method is to evaluate pollutants such as TVOC, formaldehyde emitted from building materials. This method was only designed to evaluate the surface emission of sample exposed in the chamber. In this method, building materials cut with a fixed standard size are fixed in a sample sealing box. The sample sealing box is put into the 20 L test chamber. This chamber is ventilated at a standard air change rate with purified air for 7 days then the sample from the chamber is collected and analyzed to measure the emission rate of TVOC and formaldehyde. In this method, however, if the sealing box does not guarantee airtightness, accurate evaluation for the building materials can not be achieved due to the pollutants emitted from edge of the sample so called, edge effect. This edge effect can be much greater when evaluating panels such as plywood, flooring due to their surface treatment. In this study, flooring was tested to check airtightness of the sample sealing box with analytic results between 1L and 20 L test chamber. Furniture materials like LPM coated one side surface treatment and MDF coated both sides surface treatment with LPM were tested to identify whether the improvement of the sample sealing box airtightness is possible with the comparison between existing and improved test method that low VOC emission tape was used to seal the sample edge. After 7 days, MDF TVOC emission rate was different according to the existence and nonexistence of tape. The emission rate of the existing test method was <TEX>$0.009mg/m^2h$</TEX> and that of improved test method was <TEX>$0.003mg/m^2h$</TEX>. Relative standard deviation for the existing test method was <TEX>$0.004mg/m^2h$</TEX> and relative standard deviation for the improved test method was <TEX>$0.002mg/m^2h$</TEX> when the same sample was analyzed three times. The improved test method in this study using low VOC emission tape was effective and able to reduce the heterogeneous effect of the edge from the sample sealing box.
환경부, (2002) 실내공간 실내공기오염 특성 및 관리방법연구, 환경부
JIS A 1901, (2003) シックハウス對策に役立つ 小形チャン バ法, JIS A 1901
최상웅, (2006) 건축자재의 휘발성유기화합물 방출시험에 이용되는 소형시험챔버법들의 평가,
ISO 16000-6, (1994) Determination of volatile organic compoundsin indoor and test chamber air by active samplingon Tenax TA sorbent, thermal desorption and gaschromatography using MS/FID
EUR 13593 EN, (1991) Guidline for the characterization of volatileorganic compounds emitted from indoor materials andproducts using small emission test chambers,
김현진, (2005) 건축자재의 휘발성 유기화합물과 알데하이드 방출시험을 위한 1 리터 시험챔버 개발,
ISO 16000-9, (2006) Determination of the emssion of volatileorganic compounds from building products and furnishing-Emission chamber method, ISO 16000-9
Zeli Que, (2005) Evaluationof three test methods in determination of formaldehydeemission from particleboard bonded with differentmole ratio in the urea-formaldehyde resion,