生态环境学报
生態環境學報
생태배경학보
ECOLOGY AND ENVIRONMENT
2009年
5期
1764-1766
,共3页
王圆方%朱宁%颜丽%娄翼来%关连珠
王圓方%硃寧%顏麗%婁翼來%關連珠
왕원방%주저%안려%루익래%관련주
外源Cd~(2+)%土壤微团聚体%含量%形态转化
外源Cd~(2+)%土壤微糰聚體%含量%形態轉化
외원Cd~(2+)%토양미단취체%함량%형태전화
added water-soluble Cd~(2+)%soil microaggregate%content%chemical speciation
采用室内培养和室内分析相结合的方法,研究了外源Cd~(2+)进入土壤30 d后,在土壤各级微团聚体中的含量富集和形态赋存情况.研究结果表明:外源水溶性镉进入土壤30 d后,100%转化成了颗粒态,其中58.5%转化为了可交换态,0.98%转化成了碳酸盐结合态,1.26%转化成了铁锰氧化物结合态,7.68%转化成了有机结合态,31.5%转化成了残渣态,这基本与其中各粒级微团聚体中的赋存形态的情况一致.在土壤中赋存的镉主要分布在各级微团聚体中,在各粒级微团聚体中的含量分布顺序为<10μm微团聚体>10~50μm微团聚体>50~250 μm微团聚体;外源镉向小粒级微团聚体的富集倾向明显高于向大粒级微团聚体的富集倾向,其中在<10μm微团聚体中富集系数为1.43,在50~250μm微团聚体中的富集系数只有0.60.
採用室內培養和室內分析相結閤的方法,研究瞭外源Cd~(2+)進入土壤30 d後,在土壤各級微糰聚體中的含量富集和形態賦存情況.研究結果錶明:外源水溶性鎘進入土壤30 d後,100%轉化成瞭顆粒態,其中58.5%轉化為瞭可交換態,0.98%轉化成瞭碳痠鹽結閤態,1.26%轉化成瞭鐵錳氧化物結閤態,7.68%轉化成瞭有機結閤態,31.5%轉化成瞭殘渣態,這基本與其中各粒級微糰聚體中的賦存形態的情況一緻.在土壤中賦存的鎘主要分佈在各級微糰聚體中,在各粒級微糰聚體中的含量分佈順序為<10μm微糰聚體>10~50μm微糰聚體>50~250 μm微糰聚體;外源鎘嚮小粒級微糰聚體的富集傾嚮明顯高于嚮大粒級微糰聚體的富集傾嚮,其中在<10μm微糰聚體中富集繫數為1.43,在50~250μm微糰聚體中的富集繫數隻有0.60.
채용실내배양화실내분석상결합적방법,연구료외원Cd~(2+)진입토양30 d후,재토양각급미단취체중적함량부집화형태부존정황.연구결과표명:외원수용성력진입토양30 d후,100%전화성료과립태,기중58.5%전화위료가교환태,0.98%전화성료탄산염결합태,1.26%전화성료철맹양화물결합태,7.68%전화성료유궤결합태,31.5%전화성료잔사태,저기본여기중각립급미단취체중적부존형태적정황일치.재토양중부존적력주요분포재각급미단취체중,재각립급미단취체중적함량분포순서위<10μm미단취체>10~50μm미단취체>50~250 μm미단취체;외원력향소립급미단취체적부집경향명현고우향대립급미단취체적부집경향,기중재<10μm미단취체중부집계수위1.43,재50~250μm미단취체중적부집계수지유0.60.
Contents and chemical speciation of water-soluble Cd~(2+) in several different particle size microaggregate fractions 30 days after added into the bulk soil were investigated by using laboratory incubation method. Obtained results showed that, the added wa-ter-soluble Cd~(2+) were completely transformed into other forms including exchangeable fraction, carbonate bound fraction, Fe/Mn oxide bound fraction, organic bound fraction and residual fraction, with percentages of 58.5%, 0.98%, 1.26%, 7.68% and 31.5%, respectively. Such distribution pattern of Cd chemical speciation was consistent with those in different particle size microaggregates. The Cd added into the soil was mostly concentrated in the micruaggregate, and the Cd contents in the different particle size microag-gregates declined in the order of particle size <10 μm, 10~50 μm and 50~250 μm. The added Cd was more prone to be enriched in small microaggregate than big one. The enrichment coefficient of Cd was 1.43 in <10 μm particle size microaggregate, but only 0.60 in 50~250 μm.