Distribution and Migration Characteristics of Heavy Metals in the Sediment-Plant System
Constructed wetlands are extensively applied in waste water treatment and water ecosystem restoration. However, the accumulation and migration characteristics and potential ecology risks of heavy metals, particularly in a long-running large-scale constructed wetland for wastewater treatment, are still unclear. In this study, the variation of heavy metals in the sediment-plant system of a wetland that had been in operation for 14 years was quantified. Results show that the sediments of the constructed wetland were the sink for heavy metals but with apparent difference between them. Cu, Zn, Pb, Cd and Cr contents were significantly increased (P 0.05) in sediments within 0-40 cm depth and Zn and Cr have even accumulated at 40-60 cm depth. Along with the surface flow direction, heavy metal concentrations mostly showed a decline trend. In comparison, Cu and Cr transported longer distance. Bioconcentration factors show that the two common wetland plants, P australis and Typha, exhibited obvious differences in enrichment performance of heavy metals, with the orders of Zn Cr > Cd > Cu > Pb > As and Cd > Zn > Cr > Cu > As > Pb, respectively. Harvested plants above ground removed a small part of heavy metals from the wetland system, with the translocation factors less than 1, indicating a suitable condition for phytostabilization. Root zone of the wetland system effectively restricted the leaching of heavy metals. Sediment organic matter was the primary environmental factor affecting the distribution and migration of heavy metals in the wetland system. The discrepancy in the migration characteristics of pollutants, especially heavy metals, should be seriously considered in the design and management of wetland systems, including highly-enrichment plants, appropriate hydraulic residence time, and effective surficial filling medium.