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在湿地土壤中用作木材防腐剂的微米化 Cu 的转化和释放。

Transformation and release of micronized Cu used as a wood preservative in treated wood in wetland soil.

机构信息

EPA, ORD, Center for Public Health and Environmental Assessment, Corvallis, OR, USA.

EPA, ORD, Center for Environmental Solutions and Emergency Response, Cincinnati, OH, USA.

出版信息

Environ Pollut. 2021 Oct 15;287:117189. doi: 10.1016/j.envpol.2021.117189. Epub 2021 Apr 19.

Abstract

Micronized Cu (μ-Cu) is used as a wood preservative, replacing toxic chromated copper arsenate (CCA). Micronized Cu is malachite [CuCO(OH)] that has been milled to micron/submicron particles, with many particle diameters less than 100 nm, mixed with biocides and then used to treat wood. In addition to concerns about the fate of the Cu from μ-Cu, there is interest in the fate of the nano-Cu (n-Cu) constituents. We examined movement of Cu from μ-Cu-treated wood after placing treated-wood stakes into model wetland ecosystems. Release of Cu into surface and subsurface water was monitored. Surface water Cu reached maximum levels 3 days after stake installation and remained elevated if the systems remained inundated. Subsurface water Cu levels were 10% of surface water levels at day 3 and increased gradually thereafter. Sequential filtering indicated that a large portion of the Cu in solution was associating with soluble organics, but there was no evidence for n-Cu in solution. After 4 months, Cu in thin-sections of treated wood and adjacent soil were characterized with micro X-ray absorption fine structure spectroscopy (μ-XAFS). Localization and speciation of Cu in the wood and adjacent soil using μ-XAFS clearly indicated that Cu concentrations decreased over time in the treated wood and increased in the adjacent soil. However, n-Cu from the treated wood was not found in the adjacent soil or plant roots. The results of this study indicate that Cu in the μ-Cu-treated wood dissolves and migrates into adjacent soil and waters primarily in ionic form (i.e., Cu) and not as nano-sized Cu particles. A reduced form of Cu (CuS) was identified in deep soil proximal to the treated wood, indicating strong reducing conditions. The formation of the insoluble CuS effectively removes some portion of dissolved Cu from solution, reducing movement of Cu to the water column and diminishing exposure.

摘要

微米化铜(μ-Cu)被用作木材防腐剂,取代有毒的铬酸铜砷酸盐(CCA)。微米化铜是孔雀石[CuCO(OH)],经过研磨成微米/亚微米颗粒,许多粒径小于 100nm,与杀生剂混合,然后用于处理木材。除了对来自μ-Cu 的铜的命运的担忧外,人们还对纳米铜(n-Cu)成分的命运感兴趣。我们研究了将处理过的木桩放入模型湿地生态系统后,来自μ-Cu 处理过的木材中的铜的迁移情况。监测了 Cu 向地表水和地下水的释放情况。在木桩安装后 3 天,地表水 Cu 达到最高水平,如果系统保持淹没状态,则会保持升高。地下水 Cu 的水平在第 3 天为地表水水平的 10%,此后逐渐增加。连续过滤表明,溶液中大部分 Cu 与可溶性有机物结合,但溶液中没有 n-Cu 的证据。4 个月后,采用微 X 射线吸收精细结构光谱(μ-XAFS)对处理过的木材和相邻土壤中的 Cu 进行了特征描述。使用μ-XAFS 对木材和相邻土壤中 Cu 的定位和形态分析清楚地表明,随着时间的推移,处理过的木材中的 Cu 浓度降低,而相邻土壤中的 Cu 浓度增加。然而,相邻土壤或植物根系中没有发现来自处理过的木材的 n-Cu。本研究结果表明,μ-Cu 处理过的木材中的 Cu 溶解并迁移到相邻的土壤和水中,主要以离子形式(即 Cu)存在,而不是纳米级 Cu 颗粒。在靠近处理过的木材的深部土壤中鉴定出了一种还原形式的 Cu(CuS),表明存在强烈的还原条件。不溶性 CuS 的形成有效地将部分溶解的 Cu 从溶液中去除,减少了 Cu 向水柱的迁移,降低了暴露量。

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