首页> 外文期刊>Water, Air, and Soil Pollution >BIOACCUMULATION OF TOTAL MERCURY AND MONOMETHYLMERCURY IN THE EARTHWORM EISENIA FETIDA
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BIOACCUMULATION OF TOTAL MERCURY AND MONOMETHYLMERCURY IN THE EARTHWORM EISENIA FETIDA

机译:FET叶艾森病中总汞和单甲汞的生物累积

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Bioaccumulation factors (BAFs) for inorganic mercury in earthworms are usually < 1; however, factors up to ~10 have been reported. Little information is available concerning the bioac-cumulation of organic mercury in earthworms from actual contaminated soils and thus there has been uncertainty in the risk characterization phase of ecological risk assessments of mercury-contaminated sites. This study was initiated to determine the rate of uptake and bioaccumulation of total mercury (T-Hg) and monomethylmercury (MMHg) in Eisenia fetida from soils which have been contaminated with mercury for approximately 30 years. The study consisted of a 28-day uptake phase in three mercury-contaminated soils and one soil with background concentrations of mercury followed by a 14-day depuration phase in background soil only. Total mercury concentrations in the study soils ranged from 85 to 11,542 μg kg~(-1) dry weight soil; MMHg concentrations ranged from 1.12 to 7.35 μg kg~(-1) dry weight soil. Time to 90% steady states for T-Hg ranged from 36 to 42 days. A steady state did not occur for any of the MMHg exposures during the 42-day study; estimated time to 90% steady state varied from 97 to 192 days. BAFs for T-Hg ranged from 0.6 to 3.3. BAFs for MMHg ranged from 175 to 249. The BAFs for T-Hg and MMHg were larger in earthworms exposed to the lower contaminated soils and smaller in the higher mercury-contaminated soils. The absolute concentrations of T-Hg and MMHg bioaccumulated in E. fetida, however, were higher in the earthworms exposed to the higher mercury soils and lower in the less mercury-contaminated soils.
机译:inorganic中无机汞的生物累积因子(BAF)通常<1;然而,据报导高达〜10的因素。关于来自实际污染土壤的the中生物汞的生物累积的信息很少,因此在对汞污染场所进行生态风险评估的风险表征阶段尚不确定。这项研究的开始是为了确定从污染了大约30年的土壤中,埃塞俄比亚fetida中的总汞(T-Hg)和一甲基汞(MMHg)的吸收速率和生物蓄积率。这项研究包括在三种被汞污染的土壤和一种具有汞背景浓度的土壤中进行28天的吸收期,然后仅对本底土壤进行14天的净化阶段。研究土壤中的总汞浓度为85至11,542μgkg〜(-1)干重土壤。 MMHg浓度范围为1.12至7.35μgkg〜(-1)干重土壤。 T-Hg达到90%稳态的时间为36至42天。在为期42天的研究中,MMHg暴露均未达到稳定状态。估计达到90%稳态所需的时间从97天到192天不等。 T-Hg的BAF在0.6到3.3之间。 MMHg的BAF在175至249之间。T-Hg和MMHg的BAF在暴露于低污染土壤的soil中较大,而在高汞污染土壤中则较小。但是,在暴露于高汞土壤的worm中,生物积累的T-Hg和MMHg的绝对浓度较高,而在汞污染较少的土壤中,则较低。

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