Moriske H J, Freise R, Schneider C, Rüden H
Fachgebiet Hygiene der Technischen Universität Berlin.
Zentralbl Bakteriol Mikrobiol Hyg B Umwelthyg Krankenhaushyg Arbeitshyg Prav Med. 1987 Oct;185(1-2):72-104.
During April and May 1985, some emission samples from private coal firing (domestic fuel) were taken and were fired with two different kind of coal (bituminous and brown coal). Also, measurements were done under different combustion conditions (low and high concentrations of oxygenium during the combustion process). In June and November 1985, some emission samples from heavy diesel-engines were taken in a special tunnel equipment, at different engine conditions. During September 1985, also suspended particulates in a highway traffic tunnel were taken. All these samples were taken using high volume cascade impactors which give a fractionation of the suspended particulates into different particle sizes, according to their retention behaviour in the human respiratory system. The results of these emission samples and samples in the highway tunnel were compared with prior immission measurements of urban suspended particulates in Berlin-West, during January 1984. The etherextractable organic matter (= EEOM) of the total suspended particulate matter (= TPM) was determined using ultrasonic extraction method. The EEOM was separated into an acidic (= AF), a basic (= BF) and a neutral fraction (= NF) by dissolution in acidic and basic agents. Of the neutral fraction (NF), further separation was done into aliphatic compounds (= AIP), polycyclic aromatic hydrocarbons (= PAH) and polar neutral organic compounds (POCN) by using thin layer chromatography. From the PAH and POCN, single compounds were identified by gas chromatographic analysis with dual capillary collumns and internal standard method. All organic fractions were tested to their mutagenic activity in the Salmonella typhimurium mammalian microsome bioassay by Ames. The following results were gained: the neutral fraction (NF) made the highest part of the EEOM (greater than or equal to 60%) whereas the part of the AF amounted to 10-25% and of the basic fraction (BF) to approximatively 5-20%. Making further separation of the NF, some differences between the emission sources were gained. Now, the AIP amounted to a percentage of ca. 15% of the NF for coal firing emissions and to ca. 20-40% for diesel-emissions and samples in the highway tunnel. The percentages of the PAH and POCN varied in dependence of the combustion conditions on both emission sources and amounted to 20-50% for the PAH and 30-50% for the POCN. The gas chromatographic analysis showed also differences between the two emission sources. So, for coal firing emissions, higher concentrations for phenanthrene, benzo(a)-pyrene and dibenz(a.h)anthracene (for PAH) and 9-fluorenone (for POCN) were gained.(ABSTRACT TRUNCATED AT 400 WORDS)
1985年4月和5月,采集了一些私人燃煤(家用燃料)的排放样本,并用两种不同的煤(烟煤和褐煤)进行燃烧。同时,在不同的燃烧条件下(燃烧过程中氧气浓度低和高)进行了测量。1985年6月和11月,在特殊的隧道设备中,在不同的发动机工况下采集了一些重型柴油发动机的排放样本。1985年9月,还采集了公路交通隧道中的悬浮颗粒物。所有这些样本均使用大容量级联撞击器采集,该撞击器根据悬浮颗粒物在人体呼吸系统中的滞留行为,将其按不同粒径进行分级。将这些排放样本和公路隧道样本的结果与1984年1月西柏林城市悬浮颗粒物的先前暴露测量结果进行了比较。使用超声提取法测定了总悬浮颗粒物(TPM)中的可醚萃取有机物(EEOM)。通过在酸性和碱性试剂中溶解,将EEOM分离为酸性部分(AF)、碱性部分(BF)和中性部分(NF)。对于中性部分(NF),通过薄层色谱进一步分离为脂肪族化合物(AIP)、多环芳烃(PAH)和极性中性有机化合物(POCN)。通过双毛细管柱气相色谱分析和内标法,从PAH和POCN中鉴定出单一化合物。所有有机部分均在鼠伤寒沙门氏菌哺乳动物微粒体生物测定法(Ames法)中测试其致突变活性。得到了以下结果:中性部分(NF)在EEOM中所占比例最高(大于或等于60%),而AF部分占10 - 25%,碱性部分(BF)约占5 - 20%。对NF进一步分离后,发现排放源之间存在一些差异。现在,对于燃煤排放,AIP在NF中所占百分比约为15%,对于柴油排放和公路隧道样本,该比例约为20 - 40%。PAH和POCN的百分比因排放源的燃烧条件而异,PAH为20 - 50%,POCN为30 - 50%。气相色谱分析也显示了两种排放源之间的差异。因此,对于燃煤排放,菲、苯并(a)芘和二苯并(a,h)蒽(对于PAH)以及9 - 芴酮(对于POCN)的浓度较高。(摘要截断于400字)