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福建沿海公路旁土壤重金属分布格局及防护林的作用 被引量:7
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作者 尤龙辉 叶功富 +3 位作者 陈增鸿 白永会 朱美琴 高伟 《福建林学院学报》 CSCD 北大核心 2012年第3期199-207,共9页
采用污染指数分析7种重金属元素(Pb、Cr、Cu、Zn、Cd、Ni、As)的扩散格局及其对防护林带的影响,比较有林带和无林带路旁土壤重金属污染的差异。结果表明,有林带和无林带路旁土壤重金属含量峰值均不在路肩处,其中无林带路段大部分出现在... 采用污染指数分析7种重金属元素(Pb、Cr、Cu、Zn、Cd、Ni、As)的扩散格局及其对防护林带的影响,比较有林带和无林带路旁土壤重金属污染的差异。结果表明,有林带和无林带路旁土壤重金属含量峰值均不在路肩处,其中无林带路段大部分出现在距路肩100-200 m的范围,然后逐渐下降到对照值,而有林带路段大部分出现在距路肩10-50 m的范围,且在越过峰值以后各样点的含量值基本上比无林带对应样点的低,并达到显著水平;单项污染综合指数显示,在无林带路段,除了Cr和Ni,其他重金属元素对路旁200 m范围内的土壤均产生了不同程度的污染,其中以Zn和Cu的污染最严重,有林带路段重金属污染范围大部分缩小为100 m;多项污染综合指数显示,无林带路段路旁土壤重金属污染的范围达到300 m,而有林带路段缩小为200 m;相关性分析显示,土壤重金属污染主要来源于公路交通,根据当前沿海防护林的经营管理方式,在公路两侧建设50 m宽的防护林带,能有效抑制由交通引起的重金属污染的扩散。 展开更多
关键词 林带 无林带 重金属污染 污染指数 水平格局 防护作用
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Mobilization of Inorganic Phosphorus from Soils by Ectomycorrhizal Fungi 被引量:5
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作者 ZHANG Liang WANG Ming-Xia +3 位作者 LI Hua YUAN Ling HUANG Jian-Guo C.PENFOLD 《Pedosphere》 SCIE CAS CSCD 2014年第5期683-689,共7页
Ectomycorrhizal(EM) fungi could form symbiosis with plant roots and participate in nutrient absorption; however, many EM species commonly found in forest soils, where phosphorus(P) concentration and availability are u... Ectomycorrhizal(EM) fungi could form symbiosis with plant roots and participate in nutrient absorption; however, many EM species commonly found in forest soils, where phosphorus(P) concentration and availability are usually very low, particularly in tropical and subtropical areas, have not yet been investigated for their efficiencies to mobilize soil P. In this study, fungal growth, P absorption,efflux of protons and organic acids, and soil P depletion by four isolates of EM fungi isolated either from acidic or calcareous soils were compared in pure liquid culture using soil as a sole P source. Boletus sp. 7(Bo 7), Lactarius deliciosus 3(Ld 3), and Pisolithus tinctorius 715(Pt 715) from acidic and P-deficient soils of southwestern China showed higher biomass and P concentration and accumulation than Cenococcum geophilum 4(Cg 4) from a calcareous soil of Inner Mongolia, northern China, after 4 weeks of liquid culture. Oxalate, malate, succinate, acetate, and citrate concentrations in the culture solutions varied significantly with fungal species,and oxalate accounted for 51.5%–91.4% of the total organic acids. Organic acids, particularly oxalate, in the culture solutions may lead to the solubilization of iron-bound P(Fe-P), aluminum-bound P(Al-P), and occluded P(O-P) from soil phosphates. Fungal species also varied greatly in proton efflux, which decreased the culture solution pH and may dissolve calcium-bound P(Ca-P) in soil.This could be the reason for the increment of both inorganic P in the culture solutions and Olsen P in the soil when EM fungi were present. Total inorganic P, the sum of Al-P, Fe-P, O-P, and Ca-P, in the culture solutions was positively correlated with the total concentration of organic acids in the culture solutions(r = 0.918*, n = 5), but negatively with both the total inorganic P in soil(r =-0.970**, n = 5) and the culture solution pH(r =-0.830*, n = 5). These suggested variable efficiencies of EM fungal species to mobilize inorganic P fractions from soil, which could make EM trees to utilize inorganic P in the same way like EM fungi and adapt to the soils with various P concentrations and availabilities. 展开更多
关键词 EM fungal species inorganic P organic acid P availability PROTON soil phosphate
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