Dyson Eshariah N, Hagmann Diane F, Idrovo Cesar, Krumins Jennifer Adams, Goodey Nina M
Department of Chemistry and Biochemistry, Montclair State University, Montclair, New Jersey 07043, United States.
Department of Earth and Environmental Science, Montclair State University, Montclair, New Jersey 07043, United States.
ACS Omega. 2024 Sep 25;9(40):41544-41554. doi: 10.1021/acsomega.4c05265. eCollection 2024 Oct 8.
Soil vertical heterogeneity refers to the variation in soil properties and composition with depth. In uncontaminated soils, properties including the organic matter content and nutrient concentrations typically change gradually with depth due to natural processes such as weathering, leaching, and organic matter decomposition. In contaminated soils, heavy metals and organic contaminants can migrate vertically through leaching or root uptake and translocation by plants and macrobiota, if present, leading to vertical heterogeneity in contaminant concentrations at different depths. Contaminants can alter soil properties, and we investigated the implications of soil vertical heterogeneity for germination and microbial functioning. We collected soil from an urban brownfield and created two conditions: structured soil samples collected with the soil core intact and mixed (unstructured) samples. When planted, the germination rate was significantly lower in the structured conditions (3.1 ± 1.7%) compared to mixed soils (17 ± 4.6%), suggesting that the vertical heterogeneity of contaminated soil influenced plant germination. To map the vertical distribution of contaminants and nutrient cycling rates in the structured soil samples, we collected 10 cm-deep soil cores from the barren site and a neighboring vegetated reference site and measured heavy metal concentrations, soil enzyme activities, and organic matter content in five 2 cm vertical layers. In the barren soil cores, metals were found concentrated in the top 2 cm layer, while in the vegetated soil cores, metals were uniformly distributed. No significant differences were observed for the organic matter content or moisture along depth. Published studies on vertical distribution of enzyme activities and metal concentrations have treated the top 10-20 cm as a single layer and thus would have not revealed the thin (<2 cm thick) metal cap on the surface of the barren soil core. Despite the metal cap, enzyme activities in the top layer were similar to those in the lower layers of the barren soil core, suggesting that high metal concentrations do not limit soil enzyme activity under all circumstances. Investigating vertical heterogeneity in postindustrial soils can inform efforts to convert industrial barrens to vegetated environments.
土壤垂直异质性是指土壤性质和组成随深度的变化。在未受污染的土壤中,由于风化、淋溶和有机物分解等自然过程,包括有机质含量和养分浓度在内的性质通常会随深度逐渐变化。在受污染的土壤中,如果存在重金属和有机污染物,它们可以通过淋溶或植物及大型生物区系的根系吸收和转运而垂直迁移,导致不同深度处污染物浓度的垂直异质性。污染物会改变土壤性质,我们研究了土壤垂直异质性对发芽和微生物功能的影响。我们从一个城市棕地采集土壤,并创建了两种条件:完整采集土壤核心的结构化土壤样本和混合(非结构化)样本。种植后,结构化条件下的发芽率(3.1±1.7%)显著低于混合土壤(17±4.6%),这表明受污染土壤的垂直异质性影响了植物发芽。为了绘制结构化土壤样本中污染物的垂直分布和养分循环速率,我们从荒地和邻近的植被参考地点采集了10厘米深的土壤核心,并测量了五个2厘米垂直层中的重金属浓度、土壤酶活性和有机质含量。在荒地土壤核心中,金属集中在顶部2厘米层,而在植被土壤核心中,金属分布均匀。沿深度方向,有机质含量或湿度没有显著差异。关于酶活性和金属浓度垂直分布的已发表研究将顶部10 - 20厘米视为单层,因此不会揭示荒地土壤核心表面薄薄的(<2厘米厚)金属覆盖层。尽管有金属覆盖层,但荒地土壤核心顶层的酶活性与较低层相似,这表明在所有情况下高金属浓度并不限制土壤酶活性。研究后工业土壤中的垂直异质性可为将工业荒地转变为植被环境的努力提供信息。