Johns Hopkins University, Department of Chemistry, Baltimore, MD 21218, United States of America.
Colorado School of Mines, Department of Chemistry and Geochemistry, Golden, CO 80401, United States of America.
Sci Total Environ. 2019 Jun 10;668:234-244. doi: 10.1016/j.scitotenv.2019.01.433. Epub 2019 Feb 27.
Commercially available lumber, pressure-treated with micronized copper azole (MCA), has largely replaced other inorganic biocides for residential wood treatment in the USA, yet little is known about how different outdoor environmental conditions impact the release of ionic, nano-scale, or larger (micron-scale) copper from this product. Therefore, we weathered pressure treated lumber for 18 months in five different climates across the continental United States. Copper release was quantified every month and local weather conditions were recorded continuously to determine the extent to which local climate regulated the release of copper from this nano-enabled product during its use phase. Two distinct release trends were observed: In cooler, wetter climates release occurred primarily during the first few months of weathering, as the result of copper leaching from surface/near-surface areas. In warmer, drier climates, less copper was initially released due to limited precipitation. However, as the wood dried and cracked, the exposed copper-bearing surface area increased, leading to increased copper release later in the product lifetime. Single-particle-ICP-MS results from laboratory prepared MCA-wood leachate solutions indicated that a) the predominant form of released copper passed through a filter smaller than 0.45 micrometers and b) released particles were largely resistant to dissolution over the course of 6 wks. Toxicity Characteristic Leaching Procedure (TCLP) testing was conducted on nonweathered and weathered MCA-wood samples to simulate landfill conditions during their end-of-life (EoL) phase and revealed that MCA wood released <10% of initially embedded copper. Findings from this study provide data necessary to complete a more comprehensive evaluation of the environmental and human health impacts introduced through release of copper from pressure treated lumber utilizing life cycle assessment (LCA).
市售的经微米级铜唑(MCA)加压处理的木材已在很大程度上取代了其他无机杀生物剂,用于美国住宅木材处理,但人们对不同的户外环境条件如何影响这种产品释放离子、纳米级或更大(微米级)铜知之甚少。因此,我们在美国大陆的五个不同气候区将加压处理的木材风化了 18 个月。每月定量测定铜的释放量,并连续记录当地的天气条件,以确定当地气候在该纳米增强产品使用阶段对铜释放的调节程度。观察到两种明显的释放趋势:在较冷、较湿的气候中,由于铜从表面/近表面区域浸出,释放主要发生在风化的前几个月。在较温暖、较干燥的气候中,由于降水有限,最初释放的铜较少。然而,随着木材变干和开裂,暴露的含铜表面积增加,导致产品寿命后期铜的释放增加。从实验室制备的 MCA-木材浸出液中获得的单颗粒 ICP-MS 结果表明:a)通过小于 0.45 微米的过滤器的释放铜的主要形式;b)释放的颗粒在 6 周的过程中基本上不易溶解。对未风化和风化的 MCA 木材样品进行了毒性特征浸出程序(TCLP)测试,以模拟其生命周期结束(EoL)阶段的垃圾填埋条件,结果表明 MCA 木材释放的初始嵌入铜不到 10%。本研究的结果提供了必要的数据,以完成更全面的评估,即通过压力处理木材释放铜对环境和人类健康的影响,利用生命周期评估(LCA)。