Afshari A, Gunnarsen L, Clausen P A, Hansen V
Danish Building and Urban Research, PO Box 119, DK-2970 Hørsholm, Denmark.
Indoor Air. 2004 Apr;14(2):120-8. doi: 10.1046/j.1600-0668.2003.00220.x.
The main objective of this study was to generate quantitative and qualitative emission data on phthalates from different materials. To achieve this the existing (Chamber for Laboratory Investigations of Materials, Pollution and Air Quality) Climpaq-based procedure for simplified measurements of emissions of plasticizer from PVC and other plasticized materials was modified. It was applied to a range of products. Some of them were suspected of contributing to the indoor concentration of plasticizers. The emissions from PVC flooring, polyolefine flooring, a refrigerator list, two electric cables, PVC skirting and floor wax were studied in separate Climpaqs. The emission from the PVC flooring in the Climpaq was compared with results from the ultra-small chamber Field and Laboratory Emission Cell (FLEC). Sampling and analysis methods were optimized to measure plasticizers. Samples were taken in exhaust air from the chambers after 6, 35, 62, 105, and 150 days from the start of the experiment. PVC flooring was tested for an additional 100 days. Polyolefine covered with wax resulted in an air concentration of 22 microg/m3 of dibutylphthalate (DBP), which is two orders of magnitude larger than any other materials, but did not emit di(2-ethylhexyl)phthalate (DEHP). The other materials resulted in max concentration of approximately 1 microg/m3 of DEHP and low emissions of DBP. The concentration of DEHP in each chamber increased slowly to a rather stable level which was reached after 150 days. DBP concentrations in the chambers with PVC skirting, PVC flooring, polyolefine and floor wax reached their quasi-static equilibrium after 60 days. The modified method did not create sufficient data for the calculation of emission rates. Adsorption of emission on chamber surfaces made it impossible to use the first part of the experiment for emission rate calculation. When the concentration had stabilized, it was found to be almost identical and independent of chamber and ventilation rate. Emission rates were reduced at high concentrations probably because the concentration in the material was near equilibrium with the concentration in the chamber air.
本研究的主要目的是生成不同材料中邻苯二甲酸盐的定量和定性排放数据。为实现这一目标,对现有的基于Climpaq(材料、污染和空气质量实验室调查室)的程序进行了修改,该程序用于简化PVC和其他增塑材料中增塑剂排放的测量。它被应用于一系列产品。其中一些产品被怀疑会导致室内增塑剂浓度升高。在单独的Climpaqs中研究了PVC地板、聚烯烃地板、冰箱内胆、两根电缆、PVC踢脚板和地板蜡的排放情况。将Climpaq中PVC地板的排放结果与超小型腔室现场和实验室排放池(FLEC)的结果进行了比较。对采样和分析方法进行了优化以测量增塑剂。在实验开始后的第6、35、62、105和150天,从腔室的废气中采集样品。对PVC地板进行了额外100天的测试。涂蜡的聚烯烃导致空气中邻苯二甲酸二丁酯(DBP)浓度为22微克/立方米,比任何其他材料高出两个数量级,但未排放邻苯二甲酸二(2-乙基己基)酯(DEHP)。其他材料导致DEHP的最大浓度约为1微克/立方米,DBP排放量较低。每个腔室中DEHP的浓度缓慢增加至相当稳定的水平,这一水平在150天后达到。带有PVC踢脚板、PVC地板、聚烯烃和地板蜡的腔室中DBP浓度在60天后达到准静态平衡。修改后的方法没有产生足够的数据来计算排放率。排放物在腔室表面的吸附使得无法使用实验的第一部分来计算排放率。当浓度稳定后,发现其几乎相同且与腔室和通风速率无关。在高浓度下排放率降低,可能是因为材料中的浓度与腔室空气中的浓度接近平衡。