农业环境科学学报
農業環境科學學報
농업배경과학학보
Journal of Agro-Environment Science
2009年
11期
2236-2240
,共5页
赵雄%李福燕%张冬明%漆智平
趙雄%李福燕%張鼕明%漆智平
조웅%리복연%장동명%칠지평
水稻土%Cd%水稻%分布%含量%相关性
水稻土%Cd%水稻%分佈%含量%相關性
수도토%Cd%수도%분포%함량%상관성
paddy soil%cadmium%rice%distribution%content%relevance
采用盆栽试验的方法,考察了水稻土中重金属镉(Cd)的浓度对水稻生长及Cd富集的影响以及Cd在水稻植株的分布情况,并进一步研究了糙米(可食部位)对Cd的富集量与土壤中Cd总量的关系.结果表明,在各个浓度Cd胁迫下,根、茎叶、稻壳、糙米相比,2个品种水稻都是根累积的Cd含量要高于茎叶和稻壳、糙米,即根>茎叶>稻壳>糙米;在水稻的茎叶细胞中,Cd主要分布在细胞壁,细胞可溶性成分,细胞器Cd的分布量较少,即细胞壁>可溶性部分>细胞器及膜部分;随Cd浓度增加,茎叶中的Cd积累量极显著增加,各细胞组分中的Cd含量均显著增加;根据国标GB 2762-2005对大米中Cd的限最标准(≤0.2 mg·kg~(-1)),水稻土土壤总Cd临界值分别为2.0mg·kg~(-1)(博优225)、3.1 mg·kg~(-1)(矮糯).因此,在污染土壤上宜选种食用部位重金属积累低的水稻品种,以减少人类吸收重金属的风险.
採用盆栽試驗的方法,攷察瞭水稻土中重金屬鎘(Cd)的濃度對水稻生長及Cd富集的影響以及Cd在水稻植株的分佈情況,併進一步研究瞭糙米(可食部位)對Cd的富集量與土壤中Cd總量的關繫.結果錶明,在各箇濃度Cd脅迫下,根、莖葉、稻殼、糙米相比,2箇品種水稻都是根纍積的Cd含量要高于莖葉和稻殼、糙米,即根>莖葉>稻殼>糙米;在水稻的莖葉細胞中,Cd主要分佈在細胞壁,細胞可溶性成分,細胞器Cd的分佈量較少,即細胞壁>可溶性部分>細胞器及膜部分;隨Cd濃度增加,莖葉中的Cd積纍量極顯著增加,各細胞組分中的Cd含量均顯著增加;根據國標GB 2762-2005對大米中Cd的限最標準(≤0.2 mg·kg~(-1)),水稻土土壤總Cd臨界值分彆為2.0mg·kg~(-1)(博優225)、3.1 mg·kg~(-1)(矮糯).因此,在汙染土壤上宜選種食用部位重金屬積纍低的水稻品種,以減少人類吸收重金屬的風險.
채용분재시험적방법,고찰료수도토중중금속력(Cd)적농도대수도생장급Cd부집적영향이급Cd재수도식주적분포정황,병진일보연구료조미(가식부위)대Cd적부집량여토양중Cd총량적관계.결과표명,재각개농도Cd협박하,근、경협、도각、조미상비,2개품충수도도시근루적적Cd함량요고우경협화도각、조미,즉근>경협>도각>조미;재수도적경협세포중,Cd주요분포재세포벽,세포가용성성분,세포기Cd적분포량교소,즉세포벽>가용성부분>세포기급막부분;수Cd농도증가,경협중적Cd적루량겁현저증가,각세포조분중적Cd함량균현저증가;근거국표GB 2762-2005대대미중Cd적한최표준(≤0.2 mg·kg~(-1)),수도토토양총Cd림계치분별위2.0mg·kg~(-1)(박우225)、3.1 mg·kg~(-1)(왜나).인차,재오염토양상의선충식용부위중금속적루저적수도품충,이감소인류흡수중금속적풍험.
Cadmium(Cd) is important contaminants in agricultural soil and threatening agriculture and human health. With the development of industry and agriculture, the soil heavy metal cadmium pollution becomes more and more serious. In this study, two high-yielding rice cul-tivars currently used in the local production, Boyou 225, Short glutinous treated with five levels of cadmium in a pot experiment was conducted to study the correlation between Cd accumulation of brown rice and that of paddy soils. Results showed that cadmium was not distributed uniformly in each part of rice plants. Most of the absorbed Cd assembled in the root, the upper, the less. The law of distribution of Cd in different organs of rice was:root > stem > rice husk > kernels. In rice roots and stems and leaves, cadmium was mainly distributed in the cell wall. Soluble components of cells, cell distribution of low cadmium. That is, F1(Cell wall)> F3(soluble part)> F2(cell organelles and membrane part). The rice varieties exhibited the genetic character on the Cadmium accumulation. The Cadmium contents of the grains increased with the increasing Cd concentration in soil. According to the state limit of cadmium in rice, the standard(GB 2762-2005), Contents 0.2 mg·kg~-1. In this study, tropical paddy soil total Cd threshold were Boyou225(Cd total)= 2.0 mg·kg~(-1); Short glutinous (Cd total)= 3.1 mg·kg~(-1). Therefore, for reducing the risk of the humanity to heavy metal, the rice varieties with the low capability of accumulating heavy metal in grains could be planted in a polluted soil.