中国环境科学
中國環境科學
중국배경과학
CHINA ENVIRONMENTAL SCIENCE
2010年
z1期
69-74
,共6页
彭克俭%刘益贵%沈振国%邓小鹏
彭剋儉%劉益貴%瀋振國%鄧小鵬
팽극검%류익귀%침진국%산소붕
龙须眼子菜%镉%铅%分布
龍鬚眼子菜%鎘%鉛%分佈
룡수안자채%력%연%분포
Potamogeton pectinatus%cadmium%lead%distribution
采用室内浸提、扫描电镜附加能谱分析、差数离心和凝胶层析等手段,研究了镉、铅在龙须眼子菜(Potamogeton pectinatus)叶片中的分布.结果表明,龙须眼子菜对镉、铅具有很强的吸收能力,对溶液中镉、铅的平均去除效率分别为84%、91%.当镉、铅处理液浓度分别为6.67,83.00μmol/L时,龙须眼子菜对镉、铅的生物积累量分别为496,10800mg/kg,其中可溶态镉、铅的浓度分别为55.0,14.1mg/kg,说明龙须跟子菜叶片中的镉、铅大部分都足以结合态存在的.铅在龙须眼子菜叶细胞上的分布重量百分比及原子百分比均高于镉.15%的镉和25%的铅分布在龙须眼子菜的细胞壁中;56%的镉和25%的铅分布在液泡和胞基质中.龙须眼子菜叶片中除了有小分子蛋白与镉结合外,还有其他小分子有机物也能与镉结合,而铅则主要与小分子蛋白结合.
採用室內浸提、掃描電鏡附加能譜分析、差數離心和凝膠層析等手段,研究瞭鎘、鉛在龍鬚眼子菜(Potamogeton pectinatus)葉片中的分佈.結果錶明,龍鬚眼子菜對鎘、鉛具有很彊的吸收能力,對溶液中鎘、鉛的平均去除效率分彆為84%、91%.噹鎘、鉛處理液濃度分彆為6.67,83.00μmol/L時,龍鬚眼子菜對鎘、鉛的生物積纍量分彆為496,10800mg/kg,其中可溶態鎘、鉛的濃度分彆為55.0,14.1mg/kg,說明龍鬚跟子菜葉片中的鎘、鉛大部分都足以結閤態存在的.鉛在龍鬚眼子菜葉細胞上的分佈重量百分比及原子百分比均高于鎘.15%的鎘和25%的鉛分佈在龍鬚眼子菜的細胞壁中;56%的鎘和25%的鉛分佈在液泡和胞基質中.龍鬚眼子菜葉片中除瞭有小分子蛋白與鎘結閤外,還有其他小分子有機物也能與鎘結閤,而鉛則主要與小分子蛋白結閤.
채용실내침제、소묘전경부가능보분석、차수리심화응효층석등수단,연구료력、연재룡수안자채(Potamogeton pectinatus)협편중적분포.결과표명,룡수안자채대력、연구유흔강적흡수능력,대용액중력、연적평균거제효솔분별위84%、91%.당력、연처리액농도분별위6.67,83.00μmol/L시,룡수안자채대력、연적생물적루량분별위496,10800mg/kg,기중가용태력、연적농도분별위55.0,14.1mg/kg,설명룡수근자채협편중적력、연대부분도족이결합태존재적.연재룡수안자채협세포상적분포중량백분비급원자백분비균고우력.15%적력화25%적연분포재룡수안자채적세포벽중;56%적력화25%적연분포재액포화포기질중.룡수안자채협편중제료유소분자단백여력결합외,환유기타소분자유궤물야능여력결합,이연칙주요여소분자단백결합.
Biosorption of metals by P. pectinatus in a laboratory experiment was carried out to investigate the abilities of P. pectinatus to remove Cd and Pb from contaminated water. P. pectinatus was capable of removing large amount of Cd and Pb from solution.The average removal efficiencies were 84% and 91% for Cd and Pb, respectively. Under 6.67umolCd/L and 83.00 祄olPb/L treatment, the maximum accumulation capacities were 496 mg/kg for Cd and 10800 mg/kg for Pb and the water-soluble Cd and Pb concentrations were 55.0 and 14.1 mg/kg, respectively. Most of Cd and Pb in the aquatic plant P. pectinatus could be compositions. Scanning electron microscopic and energy-dispersive X-ray microelemental analyses revealed that there was more Pb distribution in the cell wall than Cd. The subcelluar Cd distribution in leaf cells of P. pectinatus showed that there was 15%Cd and 25% Pb distribution in the cell-wall and 56%Cd and 25%Pb distribution in soluble fraction. In this study size exclusion chromatography using a Sehadex G-50 column was also performed to separate various Cd and Pb protein complexes in short term exposure to Cd and Pb. In the leaf of P. pectinatus a portion of Cd and most of Pb binds with high molecular weight complexes, and another portion of Cd could bind with low molecular weight complexes; distribution