Choi Jung Hyun, Park Seok Soon, Jaffé Peter R
Department of Civil and Environmental Engineering, Princeton University, Princeton, NJ 08544, USA.
Environ Pollut. 2006 Mar;140(2):286-93. doi: 10.1016/j.envpol.2005.07.009. Epub 2005 Sep 15.
This study focuses on the effect of plants on the biogeochemistry of sulfur species and the mobility of heavy metals in wetland sediments. Results showed that, in the presence of plants, sediments had elevated sulfate concentrations in the rhizosphere during the growing season, ranging from 0.2 to 6.20 mmol L(-1), whereas only a small difference in the sulfate profiles between vegetated and non-vegetated sediments was observed during senescence. Based on the sulfate concentration increase, the oxygen release rate from the roots to achieve the corresponding oxidation of sulfide was estimated as 0.85 g m(-2) day(-1). Evapotranspiration-induced advection is a major contributor to the transport of sulfate from the water column into the sediments, and also allows dissolved trace metals (i.e. Cd, Pb, and Zn) to be transported into the sediments and react with the acid volatile sulfide pool, resulting in the immobilization of trace metals in these sediments.
本研究聚焦于植物对湿地沉积物中硫物种生物地球化学及重金属迁移性的影响。结果表明,在植物存在的情况下,生长季期间根际沉积物中的硫酸盐浓度升高,范围为0.2至6.20 mmol L(-1),而在衰老期,植被覆盖和无植被覆盖的沉积物之间的硫酸盐剖面仅有微小差异。基于硫酸盐浓度的增加,根系释放氧气以实现相应硫化物氧化的速率估计为0.85 g m(-2) 天(-1)。蒸散引起的平流是硫酸盐从水柱输送到沉积物中的主要贡献因素,并且还使溶解的痕量金属(即镉、铅和锌)输送到沉积物中并与酸挥发性硫化物库发生反应,从而导致这些沉积物中痕量金属的固定化。