Ma T H, Xu C, Liao S, McConnell H, Jeong B S, Won C D
Department of Biological Sciences, Western Illinois University, Macomb 61455, USA.
Mutat Res. 1996 Jan 16;359(1):39-52. doi: 10.1016/s0165-1161(96)90008-4.
A dual monitoring system composed of the Tradescantia-Micronucleus (Trad-MCN) and Tradescantia-Stamen-Hair-Mutation (Trad-SHM) bioassays was utilized to monitor directly the genotoxicity of the gaseous emission at a closed landfill site and around an incinerator. Four of the commonly emitted gaseous agents from the landfill flare pipes, i.e. toluene, ethylbenzene, trichloroethylene and ethyltoluene were also evaluated for their genotoxicity in the laboratory. The in situ monitoring trips (360 km one way) were carried out by transporting the plant cuttings in a clean air box or in an air-tight plastic bag to the site and exposing these test cuttings for 5-7 h. The exposed plant samples were examined for micronuclei frequencies or the pink mutation rate after the appropriate recovery periods (24 h for MCN, 7-11 days for SHM). A total of 20 monitoring trips were made to the landfill, and 8 to the nearby surroundings (100-500 m from the chimney) of the incinerator site in a two year period. The major findings of the Trad-MCN test on the clastogenicity of the gaseous emission from the flare pipe of the landfill site showed positive responses or toxic effects in 6 out of 20 trips, and that from the incinerator showed positive responses in 5 out of the 8 trips. These positive responses were closely associated with the weather, i.e. low wind velocity, high temperature and relative humidity, and especially the distance from the chimney of the incinerator. The MCN frequencies and mutation rates of the Elementary School site (E. Sch) which is about 200 m from the fence of the landfill site were mostly negative, except the test results of three trips. Trad-SHM tests on the mutagenicity of gaseous emissions from the flare pipe of the landfill showed 12 positive responses out of 20 trials and 2 positives out of 4 trials from the incinerator gaseous emissions. The average mutation rate from 20 Trad-SHM monitoring trips is positive when the ANOVA and Dunnett's t-statistic were applied to the consolidated data. There is a significant (0.01) difference between the lab control and the gas exposed groups, and between the field control and gas exposed groups. Results of the Trad-SHM test at the E. Sch. site were mostly negative except for one trip. In general, micronuclei frequencies and mutation rates of the field control groups were relatively higher than those of the lab controls. The Trad-MCN test on pure gases showed positive responses in all 3 repeated tests on toluene (50-892 ppm). The test results of ethylbenzene yielded positive responses at 172 ppm/min and 1549 ppm/min dosages and exhibited toxicity at higher concentrations. Trad-MCN tests on trichloroethylene and ethyltoluene yielded positive responses at around 100-200 ppm/min level. Three repeated Trad-SHM tests on toluene yielded no positive response at low concentrations (4.3-12.9 ppm).
利用由紫露草微核(Trad-MCN)和紫露草雄蕊毛突变(Trad-SHM)生物测定法组成的双重监测系统,直接监测封闭垃圾填埋场和焚烧炉周围气体排放的遗传毒性。还在实验室中评估了垃圾填埋场火炬管常见排放的四种气态物质,即甲苯、乙苯、三氯乙烯和乙基甲苯的遗传毒性。通过将植物插条放在清洁空气箱或密封塑料袋中运至现场,并将这些测试插条暴露5 - 7小时,进行现场监测行程(单程360公里)。在适当的恢复期后(微核检测为24小时,雄蕊毛突变检测为7 - 11天),检查暴露的植物样本的微核频率或粉色突变率。在两年时间里,共对垃圾填埋场进行了20次监测行程,对焚烧炉场地附近(距烟囱100 - 500米)进行了8次监测行程。对垃圾填埋场火炬管气体排放的致断裂性进行的Trad-MCN测试的主要结果显示,20次行程中有6次出现阳性反应或毒性效应,焚烧炉的测试结果在8次行程中有5次出现阳性反应。这些阳性反应与天气密切相关,即低风速、高温和相对湿度,特别是与距焚烧炉烟囱的距离有关。距离垃圾填埋场围栏约200米的小学场地(E. Sch)的微核频率和突变率大多为阴性,除了三次行程的测试结果。对垃圾填埋场火炬管气体排放的致突变性进行的Trad-SHM测试在20次试验中有12次阳性反应,对焚烧炉气体排放进行的4次试验中有2次阳性反应。当将方差分析和邓尼特t检验应用于合并数据时,20次Trad-SHM监测行程的平均突变率为阳性。实验室对照组与气体暴露组之间以及现场对照组与气体暴露组之间存在显著(0.01)差异。小学场地的Trad-SHM测试结果除一次行程外大多为阴性。一般来说,现场对照组的微核频率和突变率相对高于实验室对照组。对纯气体进行的Trad-MCN测试在甲苯的所有3次重复测试(50 - 892 ppm)中均显示阳性反应。乙苯的测试结果在剂量为172 ppm/分钟和1549 ppm/分钟时产生阳性反应,在较高浓度时表现出毒性。对三氯乙烯和乙基甲苯进行的Trad-MCN测试在约100 - 200 ppm/分钟水平产生阳性反应。对甲苯进行的3次重复Trad-SHM测试在低浓度(4.3 - 12.9 ppm)时未产生阳性反应。