Pimenta A S, Bayona J M, García M T, Solanas A M
Department of Forestry Engineering, Laboratory of Wood Energy and Technology, Federal University of Viçosa, Campus Universitário, 36571-000, Viçosa (MG), Brazil.
Arch Environ Contam Toxicol. 2000 Feb;38(2):169-75. doi: 10.1007/s002449910022.
Slow pyrolysis of Eucalyptus grandis wood was performed in an oven laboratory, and smoke was trapped and condensed to yield liquid products. Polycyclic aromatic hydrocarbons (PAHs) and phenolic fractions were isolated from the former liquid products using adsorption column chromatography (ACC) and identified by GC/MS. Concentrations of PAH and phenolic fractions in total pyrolysis liquids were respectively 48.9 microg/g and 8.59% (w/w). Acute toxicity of total samples of pyrolysis liquids and the phenolic fraction was evaluated by means of two bioassays, namely, 24-h immobilization bioassay with Daphnia magna and Microtox bioassays, the latter employing the luminescent bacteria Photobacterium phosphoreum. Total pyrolysis liquids and the PAH fraction were evaluated for genotoxicity by the Microtox bioassay conducted using rehydrated freeze-dried dark mutant of the luminescent bacteria Vibrio fisheri strain M169. Total pyrolysis liquids and the phenolic fraction, respectively, in concentrations of 170 and 68 mg/L were able to immobilize 50% (EC(50)) of the D. magna population following 24-h exposure. Concentrations of 19 and 6 mg/L, respectively, for total pyrolysis liquids and phenolic fraction were the effective concentrations that resulted in a 50% (EC(50)) reduction in light produced by bacteria in the Microtox bioassay. Accordingly, the Microtox bioassay was more sensitive to toxic effects of both kind of samples than the D. magna bioassay, particularly for the phenolic fraction. Regarding to the genotoxicity evaluation, the results achieved by Microtox bioassay showed that total pyrolysis liquids had no genotoxic effects with and without exogenous metabolic activation using rat liver homogenate (S9). However, the PAH fraction showed toxic effects with rat liver activation and had a dose-response number (DRN) equal to 1.6, being in this way suspected genotoxic. The lowest detected concentration (LDC) of the PAH fraction able to cause genotoxic effects was 375 microg/L.
在实验室烘箱中对巨桉木材进行慢速热解,并将烟雾捕获并冷凝以获得液体产物。使用吸附柱色谱法(ACC)从先前的液体产物中分离出多环芳烃(PAHs)和酚类馏分,并通过气相色谱/质谱联用仪(GC/MS)进行鉴定。热解液体中PAH和酚类馏分的浓度分别为48.9μg/g和8.59%(w/w)。通过两种生物测定方法评估热解液体和酚类馏分总样品的急性毒性,即使用大型溞进行的24小时固定生物测定和微毒性生物测定,后者采用发光细菌费氏弧菌。通过使用发光细菌费氏弧菌菌株M169的复水冻干暗突变体进行的微毒性生物测定,评估热解液体和PAH馏分的遗传毒性。暴露24小时后,浓度分别为170和68mg/L的热解液体和酚类馏分能够使50%(EC50)的大型溞群体固定。在微毒性生物测定中,热解液体和酚类馏分的浓度分别为19和6mg/L时,是导致细菌产生的光减少50%(EC50)的有效浓度。因此,微毒性生物测定对这两种样品的毒性作用比大型溞生物测定更敏感,特别是对于酚类馏分。关于遗传毒性评估,微毒性生物测定的结果表明,无论有无使用大鼠肝匀浆(S9)的外源代谢激活,热解液体均无遗传毒性作用。然而,PAH馏分在大鼠肝激活时显示出毒性作用,剂量反应数(DRN)等于1.6,因此被怀疑具有遗传毒性。能够引起遗传毒性作用的PAH馏分的最低检测浓度(LDC)为375μg/L。