Qin Chongyang, Xu Xiaoyu, Peck Erin
Savannah River Ecology Laboratory, University of Georgia. PO Drawer E, Aiken, SC, 29802, USA.
Environ Manage. 2022 May;69(5):994-1004. doi: 10.1007/s00267-021-01567-7. Epub 2021 Nov 22.
The H-02 constructed wetland is a free water surface wetland to remove copper (Cu) and zinc (Zn) from the industrial wastewater. In this study, we evaluated the performance of the wetland from 2018 to 2019 and coupled the diffusive gradients in thin films (DGTs) and biotic ligand model (BLM) to explore metal speciation and bioavailability in wetland waters. Surface water samples were collected and piston DGTs were deployed in different sites of the wetland. The H-02 wetland functioned well during the sampling period with high removal efficiencies (Cu: 73.8 ± 1.2% and Zn: 75.2 ± 16.0%). In our study, with the assumption that the combination of BLM predicted inorganic metals species, BLM Cu(II) and BLM Zn(II), were the bioavailable and toxic species, DGT-Cu did not correlate to BLM Cu(II) (P = 0.47), but DGT-Zn positively correlated to BLM Zn(II) (R = 0.35, P < 0.001). Compared to the modeling results of BLM, DGT-indicated labile and/or bioavailable Cu included not only free Cu ions and inorganic Cu complexes but also a high percentage of Cu-labile organic matter complexes. DGT-indicated Zn included free Zn ion, inorganic Zn, and only a low percentage of Zn-labile organic matter complexes. Our findings illustrated the appropriate use of passive sampling techniques and geological modeling when biomonitoring could be substituted. The close monitoring of metal concentrations, speciation, and bioavailability helps us understand metal biogeochemistry and metal removal processes and ensure the long-term sustainability of the constructed wetland.
H-02人工湿地是一种自由水面湿地,用于去除工业废水中的铜(Cu)和锌(Zn)。在本研究中,我们评估了该湿地在2018年至2019年期间的性能,并结合薄膜扩散梯度技术(DGT)和生物配体模型(BLM)来探究湿地水体中金属的形态和生物有效性。采集了地表水样本,并在湿地的不同位置部署了活塞式DGT。在采样期间,H-02湿地运行良好,去除效率较高(铜:73.8±1.2%,锌:75.2±16.0%)。在我们的研究中,假设BLM预测的无机金属形态,即BLM Cu(II)和BLM Zn(II),是具有生物有效性和毒性的形态,DGT-Cu与BLM Cu(II)不相关(P = 0.47),但DGT-Zn与BLM Zn(II)呈正相关(R = 0.35,P < 0.001)。与BLM的模拟结果相比,DGT指示的不稳定和/或具有生物有效性的铜不仅包括游离铜离子和无机铜络合物,还包括高比例的铜-不稳定有机物质络合物。DGT指示的锌包括游离锌离子、无机锌,以及低比例锌-不稳定有机物质络合物。我们的研究结果说明了在可以替代生物监测时被动采样技术和地质建模的恰当应用。对金属浓度、形态和生物有效性的密切监测有助于我们理解金属生物地球化学和金属去除过程,并确保人工湿地的长期可持续性。