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Copper release and transformation following natural weathering of nano-enabled pressure-treated lumber

机译:纳米级压力处理木材自然风化后的铜释放和转化

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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 surfaceear-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). (C) 2019 Elsevier B.V. All rights reserved.
机译:在美国,用微细化的铜唑(MCA)加压处理的市售木材已在很大程度上取代了其他无机杀生物剂,用于住宅木材处理,但对于不同的室外环境条件如何影响离子,纳米级或纳米级离子的释放,人们知之甚少。此产品中的更大(微米级)的铜。因此,我们在美国大陆的五种不同气候中对经过压力处理的木材进行了18个月的风化。每月对铜的释放进行量化,并连续记录当地的天气状况,以确定在使用阶段该本地纳米产品对铜释放的调节程度。观察到两个明显的释放趋势:在凉爽,潮湿的气候中释放主要发生在风化的前几个月,这是由于铜从表面/近表面区域浸出的结果。在温暖干燥的气候中。由于降水有限,最初释放的铜较少。但是,随着木材干燥和开裂,裸露的含铜表面积增加,导致铜的释放在产品寿命的后期增加。实验室制备的MCA-木材浸出液的单颗粒ICP-MS结果表明,a)释放的铜的主要形式通过小于0.45微米的过滤器,b)释放的颗粒在6周内对溶解具有很大的抵抗力。在未风化和风化的MCA木材样品上进行了毒性特征浸出程序(TCLP)测试,以模拟其寿命终止(EoL)阶段的垃圾填埋条件,并揭示了MCA木材释放了最初嵌入铜的<10%。这项研究的发现提供了必要的数据,以完成对通过使用生命周期评估(LCA)从压力处理过的木材中释放铜所带来的环境和人类健康影响的更全面评估。 (C)2019 Elsevier B.V.保留所有权利。

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