Department of Geosciences, University of Massachusetts Amherst, Amherst, MA, USA.
Department of Plant & Soil Science, University of Vermont, Burlington, VT, 05405, USA.
Environ Pollut. 2020 Jul;262:114126. doi: 10.1016/j.envpol.2020.114126. Epub 2020 Feb 24.
Trace metals can be essential for organo-metallic structures and oxidation-reduction in metabolic processes or may cause acute or chronic toxicity at elevated concentrations. The uptake of trace metals by earthworms can cause transfer from immobilized pools in the soil to predators within terrestrial food chains. We report a synthesis and evaluation of uptake and bioaccumulation empirical data across different metals, earthworm genera, ecophysiological groups, soil properties, and experimental conditions (metal source, uptake duration, soil extraction method). Peer-reviewed datasets were extracted from manuscripts published before June 2019. The 56 studies contained 3513 soil-earthworm trace metal concentration paired data sets across 11 trace metals (As, Cd, Cr, Cu, Hg, Mn, Ni, Pb, Sb, U, Zn). Across all field and laboratory experiments studied, the median concentrations of Hg, Pb, and Cd in earthworm tissues that were above concentrations known to be hazardous for consumption by small mammals and avian predators but not for Cu, Zn, Cr, Ni, and As. Power regressions show only Hg and Cd earthworm tissue concentrations were well-correlated with soil concentrations with R > 0.25. However, generalized linear mixed-effect models reveal that earthworm concentrations were significantly correlated with soil concentrations for log-transformed Hg, Cd, Cu, Zn, As, Sb (p < 0.05). Factors that significantly contributed to these relationships included earthworm genera, ecophysiological group, soil pH, and organic matter content. Moreover, spiking soils with metal salts, shortening the duration of exposure, and measuring exchangeable soil concentrations resulted in significantly higher trace metal uptake or greater bioaccumulation factors. Our results highlight that earthworms are able to consistently bioaccumulate toxic metals (Hg and Cd only) across field and laboratory conditions. However, future experiments should incorporate greater suites of trace metals, broader genera of earthworms, and more diverse laboratory and field settings to generate data to devise universal quantitative relationships between soil and earthworm tissue concentrations.
痕量金属对于有机金属结构和代谢过程中的氧化还原至关重要,但在浓度升高时也可能导致急性或慢性毒性。蚯蚓对痕量金属的吸收会导致其从土壤中固定的库转移到陆地食物链中的捕食者。我们报告了对不同金属、蚯蚓属、生态生理群、土壤性质和实验条件(金属来源、吸收时间、土壤提取方法)的吸收和生物累积经验数据的综合评估。从 2019 年 6 月之前发表的手稿中提取了经过同行评审的数据集。这些研究共包含 56 项研究,涵盖了 11 种痕量金属(As、Cd、Cr、Cu、Hg、Mn、Ni、Pb、Sb、U、Zn)的 3513 对土壤-蚯蚓痕量金属浓度数据。在所研究的所有现场和实验室实验中,蚯蚓组织中 Hg、Pb 和 Cd 的浓度中位数均高于已知对小型哺乳动物和鸟类捕食者有危害的浓度,但 Cu、Zn、Cr、Ni 和 As 的浓度则不然。幂回归表明,仅 Hg 和 Cd 的蚯蚓组织浓度与土壤浓度呈高度相关,相关系数 R>0.25。然而,广义线性混合效应模型显示,对于对数变换后的 Hg、Cd、Cu、Zn、As 和 Sb,蚯蚓浓度与土壤浓度显著相关(p<0.05)。对这些关系有显著贡献的因素包括蚯蚓属、生态生理群、土壤 pH 值和有机质含量。此外,向土壤中添加金属盐、缩短暴露时间以及测量可交换的土壤浓度会导致痕量金属吸收或生物累积因子显著增加。我们的研究结果表明,蚯蚓在野外和实验室条件下都能够持续地生物累积有毒金属(仅 Hg 和 Cd)。然而,未来的实验应纳入更多种类的痕量金属、更广泛的蚯蚓属以及更多样化的实验室和野外环境,以生成数据,从而制定土壤与蚯蚓组织浓度之间的通用定量关系。