Rahman Farhana Alamgir, Allan Deborah L, Rosen Carl J, Sadowsky Michael J
Department of Soil, Water, and Climate, University of Minnesota, 1991 Upper Buford Circle, 439 Borlaug Hall, St. Paul, MN 55108, USA.
J Environ Qual. 2004 Jan-Feb;33(1):173-80. doi: 10.2134/jeq2004.1730.
Lumber used to construct raised garden beds is often treated with chromated copper arsenate (CCA). This project aimed to determine (i) how far As, Cu, and Cr had diffused away from CCA-treated wood surfaces in raised garden beds under realistic conditions, (ii) the uptake of these elements by crops, and (iii) the effect of CCA solution on soil bacteria. This study showed that As, Cu, and Cr diffuse into soil from CCA-treated wood used to construct raised garden beds. To determine crop uptake of these elements, contaminated soil 0 to 2 cm from the treated wood was obtained from two different beds (40-50 mg kg(-1) As); control soil was collected 1.5 m away from the treated wood (<3-10 mg kg(-1) As). Four replicates of carrot (Daucus carota var. sativus Hoffm. cv. Thumbelina), spinach (Spinacia oleracea L. cv. Indian Summer), bush bean (Phaseolus vulgaris L. cv. Provider), and buckwheat (Fagopyrum esculentum Moench cv. Common) were grown in pots containing these soils in a greenhouse. After harvest, plant materials were dried, ground, digested, and analyzed for As by inductively coupled plasma-hydride generation (ICP-HG). Concentrations of As in all crops grown in contaminated soils were higher than those from control soils. The levels of As in the crops remained well below the recommended limit for As set by the United States Public Health Service (2.6 mg kg(-1) fresh wt.). To determine if bacteria in soils 0 to 2 cm from the treated wood had higher resistance to Type C chromated copper arsenate (CCA-C) solution than those from reference soils, dilution plates were set up using quarter-strength tryptic soy agar (TSA) media and 0 to 22.94 g L(-1) (0-1.25% v/v) CCA-C working solution. The microorganisms from soils adjacent to treated wood had greater growth on the CCA-amended media than those from reference soils outside the bed.
用于建造高台式花园苗床的木材通常用铬酸铜砷酸盐(CCA)处理。本项目旨在确定:(i)在实际条件下,砷、铜和铬从经CCA处理的木材表面在高台式花园苗床中扩散了多远;(ii)这些元素被作物吸收的情况;(iii)CCA溶液对土壤细菌的影响。本研究表明,砷、铜和铬从用于建造高台式花园苗床的经CCA处理的木材扩散到土壤中。为了确定作物对这些元素的吸收情况,从两个不同的苗床中获取了距处理过的木材0至2厘米处的受污染土壤(砷含量为40 - 50毫克/千克);对照土壤是在距处理过的木材1.5米处采集的(砷含量<3 - 10毫克/千克)。在温室中,将胡萝卜(胡萝卜变种霍夫迈斯特拇指胡萝卜品种)、菠菜(菠菜印度夏日品种)、菜豆(菜豆供应者品种)和荞麦(荞麦普通品种)各四个重复种植在装有这些土壤的花盆中。收获后,将植物材料干燥、研磨、消化,并通过电感耦合等离子体 - 氢化物发生法(ICP - HG)分析砷含量。在受污染土壤中种植的所有作物中的砷浓度均高于对照土壤中的作物。作物中的砷含量仍远低于美国公共卫生服务局设定的砷推荐限量(2.6毫克/千克鲜重)。为了确定距处理过的木材0至2厘米处土壤中的细菌对C型铬酸铜砷酸盐(CCA - C)溶液的抗性是否高于参考土壤中的细菌,使用四分之一强度的胰蛋白胨大豆琼脂(TSA)培养基和0至22.94克/升(0 - 1.25% v/v)的CCA - C工作溶液设置稀释平板。与处理过的木材相邻土壤中的微生物在添加了CCA的培养基上比苗床外参考土壤中的微生物生长得更好。