中国地质
中國地質
중국지질
CHINESE GEOLOGY
2014年
5期
1693-1704
,共12页
廖启林%刘聪%朱伯万%华明%金洋%翁志华%常青%蔡玉曼
廖啟林%劉聰%硃伯萬%華明%金洋%翁誌華%常青%蔡玉曼
료계림%류총%주백만%화명%금양%옹지화%상청%채옥만
镉污染土壤%凹凸棒石%调控试验%效果
鎘汙染土壤%凹凸棒石%調控試驗%效果
력오염토양%요철봉석%조공시험%효과
Cd-contaminated soil%attapulgite%controlling test%effect
提凹凸棒石是一种富Mg的硅酸盐粘土矿物,具有抑制土壤的Cd活性的作用。江苏拥有丰富的凹凸棒石矿产资源,在利用凹凸棒石调控土壤Cd污染方面具有资源优势。文章报道了苏南地区典型Cd污染蔬菜地和稻田添加凹凸棒石粉的现场调控试验研究成果。结果显示:(1)当土壤Cd含量为0.3~0.45 mg/kg时,每年添加750 g/m2以上的凹凸棒石粉,可以使蔬菜Cd含量平均下降30%左右,凹凸棒石的最大有效添加量为1500 g/m2;(2)当土壤Cd含量约为3 mg/kg、pH<6.5时,每年添加2000 g/m2的凹凸棒石粉,连续施用2年可使稻米Cd含量从0.5 mg/kg以上降低至0.2 mg/kg以下,稻米Cd含量与土壤pH呈显著负相关;(3)添加凹凸棒石可适度提高土壤的pH和CEC,同时还能降低农产品Cu、Zn含量,在防治耕地Cd污染上具有广阔应用前景。
提凹凸棒石是一種富Mg的硅痠鹽粘土礦物,具有抑製土壤的Cd活性的作用。江囌擁有豐富的凹凸棒石礦產資源,在利用凹凸棒石調控土壤Cd汙染方麵具有資源優勢。文章報道瞭囌南地區典型Cd汙染蔬菜地和稻田添加凹凸棒石粉的現場調控試驗研究成果。結果顯示:(1)噹土壤Cd含量為0.3~0.45 mg/kg時,每年添加750 g/m2以上的凹凸棒石粉,可以使蔬菜Cd含量平均下降30%左右,凹凸棒石的最大有效添加量為1500 g/m2;(2)噹土壤Cd含量約為3 mg/kg、pH<6.5時,每年添加2000 g/m2的凹凸棒石粉,連續施用2年可使稻米Cd含量從0.5 mg/kg以上降低至0.2 mg/kg以下,稻米Cd含量與土壤pH呈顯著負相關;(3)添加凹凸棒石可適度提高土壤的pH和CEC,同時還能降低農產品Cu、Zn含量,在防治耕地Cd汙染上具有廣闊應用前景。
제요철봉석시일충부Mg적규산염점토광물,구유억제토양적Cd활성적작용。강소옹유봉부적요철봉석광산자원,재이용요철봉석조공토양Cd오염방면구유자원우세。문장보도료소남지구전형Cd오염소채지화도전첨가요철봉석분적현장조공시험연구성과。결과현시:(1)당토양Cd함량위0.3~0.45 mg/kg시,매년첨가750 g/m2이상적요철봉석분,가이사소채Cd함량평균하강30%좌우,요철봉석적최대유효첨가량위1500 g/m2;(2)당토양Cd함량약위3 mg/kg、pH<6.5시,매년첨가2000 g/m2적요철봉석분,련속시용2년가사도미Cd함량종0.5 mg/kg이상강저지0.2 mg/kg이하,도미Cd함량여토양pH정현저부상관;(3)첨가요철봉석가괄도제고토양적pH화CEC,동시환능강저농산품Cu、Zn함량,재방치경지Cd오염상구유엄활응용전경。
Attapulgite is a kind of clay mineral of Mg-rich silicate, and it also constitutes a kind of abundant non-metallic mineral resources in Jiangsu Province. As a kind of chemical remediation or immobilization material to tackle Cd-contaminated soil, its advantage in controlling heavy metal mobility is quite obvious. On the basis of choosing typical Cd-contaminated sites from vegetable garden and paddy land, a preliminary control test was systematically conducted to treat soil pollution of heavy metals so as to apply some doses of attapulgite powder in the southern area of Jiangsu Province. The related test data and controlling effect are reported in this paper to decrease Cd content of vegetable and rice from Cd-contaminated sites. Some conclusions have been reached:(1) when Cd concentration is 0.3-0.45 mg/kg in soil of the site, Cd content of vegetable can be decreased by 30%or so by applying attapulgite powder in excess of 750 g/m2 , and maximum effective applying dose is 1500 g/m2 to contaminated soil annually; (2) when Cd concentration is about 3 mg/kg and pH is lower than 6.5 in soils of the site, Cd content of rice can be dramatically decreased from more than 0.5 mg/kg to less than 0.2 mg/kg after 2 years’application of attapulgite powder in excess of 2000 g/m2 to polluted soil annually, and there are distinct negative correlated relationship between Cd content of rice and pH in polluted soil, with the correlation coefficient being-0.95; (3) the significance of applying attapulgite to the above-mentioned polluted soil is obvious in elevating pH values and cation exchange capacity (CEC), and at the same time the element concentrations of Cu and Zn can be decreased in the vegetable or rice samples. It is thus held that the prospect of applying attapulgite to soil should be relatively huge or wide in curing Cd-contaminated lands.