期刊文献+

冷水江锑矿区重金属污染林地土壤理化特性研究 被引量:10

Study on Physical and Chemic Characte of Forestry Soil Polluted by Heavy Metals in Antimony Mine of Len-Shuijiang City
下载PDF
导出
摘要 为了锑矿区土壤生态修复、造林树种选择和快速恢复植被提供科学依据,对冷水江锑矿区受重金属污染的林地土壤理化特性进行了分析,结果表明:矿区不同地点pH值、有机质、碱解氮、有效P、速效K有极显著差异,而同一地点不同土层厚度土壤容重、有机质、有效P、速效K有极显著差异,矿区林地土壤呈弱酸性反应,联盟点以土壤容重、速效K最高,七里铺以有机质、碱解氮、有效P最高。随着土层厚度的增加,土壤容重增大、土壤有机质含量降低、土壤有效磷含量降低、碱解氮呈多态反应。表层土壤速效钾显著高于其它土层。锑矿区土壤有机质、速效K较丰富,而有效P极度匮乏。 The physical and chemic character of forestry soil polluted by heavy metals in antimony of Len Shuijiang city is studied in order to afford scientific principle to ecological rehabilitate soil and select afforestation trees and restore vegetation rapidly. The result showed that there is significant difference in pH, soil organic matter, available nitrogen, available phosphorus, and available potassium at different antimony mineral sites. There is significant difference in soil bulk density, soil bulk density, soil organic matter, available phosphorus, and available potassium at the same antimony mineral soil depth. The forestry soil of antimony mine is feebleness acid reaction. The soil bulk density, available potassium is maximum in Lianmeng plot. The soil organic matter, available nitrogen, available phosphorus is maximum in Qilipu plot. The soil bulk density increase and the soil organic matter and available phosphorus reduce with the depth increase but available nitrogen is polymorphic. The available potassium of topsoil maximum. The soil organic matter and available potassium is enrichment but available phosphorus is poor.
出处 《中国农学通报》 CSCD 北大核心 2009年第10期246-250,共5页 Chinese Agricultural Science Bulletin
基金 国家‘十一五’科技支撑项目‘工矿废弃地植被恢复技术研究’(2006BAD03A0307)
关键词 林地土壤 重金属元素 理化特性 肥力等级 锑矿区 forestry soil, heavy metal element, physical and chemic character, rank of fertility, antimony mine
  • 相关文献

参考文献10

  • 1Fowler B A, Goering P L. Antimony[M].New York :VCH Weinheim,1991:89-112.
  • 2Crommentujin T, Polder MD, van de Plasche EJ.Maximum permissible concentrations and negligible concentrations of metals, taking background concentrations into account[M].The Netherlands: Bilthoven, 1997:32-89.
  • 3吴丰昌,郑建,潘响亮,黎文,邓秋静,莫昌琍,朱静,刘碧君,劭树勋,郭建阳.锑的环境生物地球化学循环与效应研究展望[J].地球科学进展,2008,23(4):350-356. 被引量:49
  • 4Neve S, Hofman G. Influence of soil compaction on carbon and nitrogen mineralization of soil organic matter and crop residues[J]. Biology and Fertility of Soils,2000,30(6):544-549.
  • 5张国红,张振贤,黄延楠,梁勇.土壤紧实程度对其某些相关理化性状和土壤酶活性的影响[J].土壤通报,2006,37(6):1094-1097. 被引量:37
  • 6姜必亮,王伯荪.可持续发展的生态学透视[J].生态科学,2000,19(1):65-69. 被引量:27
  • 7Wong M H. Reclamation of wastes contaminated by copper, lead end zinc. Environmental Management, 1986, 10:70%713.
  • 8Ritcey G M. Tailings Management: Problems and Solutions in the Mining Industry [M]. Amsterdam: Elsevier, 1989:321-389.
  • 9Johnson M S, Cooke JA, Stevenson JK W. Revegetation of metalliferous wastes and land after metal mining[M]. In: Hester and Harrison R M eds. Mining and Its Environmental Impact. Cambridge: Royal Society of Chemistry, 1994:31-48.
  • 10康乐.受害生态系统的恢复与重建.现代生态学透视,1990,18(2):43-49.

二级参考文献72

  • 1张国红,张振贤,梁勇,曹之富.土壤紧实度对温室番茄生长发育、产量及品质的影响[J].中国生态农业学报,2004,12(3):65-67. 被引量:43
  • 2曹磊.全球十大环境问题[J].环境科学,1995,16(4):86-88. 被引量:30
  • 3世界环境与发展委员会.我们共同的未来[M].北京:世界知识出版社,1989..
  • 4黄细喜.土壤紧实度及层次对小麦生长的影响[J].土壤学报,1988,(1):59-65.
  • 5曹利军,环境科学,1995年,4期,86页
  • 6陈敏豪,生态文化与文明前景,1995年
  • 7世界环境与发展委员会,我们共同的未来,1989年
  • 8Arvidsson J.Nutrient uptake and growth of barley as affected by soil compaction[J].Plant and Soil,1999,208 (1):9-19.
  • 9Nadian H,Smith S E,Alston A M,et al.Effects of soil compaction on plant growth,phosphorus uptake and morphological characteristics of vesicular-arbuscular mycorrhizal colonization of Trifolium subterraneum[J].New-Phytologist,1997,135(2),303-311.
  • 10Andrade A,Wolf D W,Fereres E.Leaf expansion,photosynthesis and water relations of sunflower plants growth on compacted soil[J].Plant and Soil,1993,149:175-184.

共引文献110

同被引文献97

引证文献10

二级引证文献88

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部