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Functional resilience of microbial communities from perturbed upland grassland soils to further persistent or transient stresses.

机译:微生物群落的功能复原力,从受到干扰的高地草原土壤到进一步的持续性或短暂性胁迫。

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The microbial functioning of soils following perturbation was assessed at a temperate upland grassland site, maintained by the Soil Biodiversity and Ecosystem Function Programme at Sourhope Research Station, Scotland. Published results indicated that the soil microbial communities were resilient to these initial perturbations; in this paper we tested whether they were equally resilient to a subsequent perturbation. Soil samples were taken from field plots receiving treatments that represented different forms of perturbation, viz. reseeding, application of sewage-sludge, biocide or nitrogen plus lime, and a non-perturbed control. Functional resilience following further perturbation comprising a transient heat or persistent copper perturbation was assessed over 28 days, by monitoring the short-term decomposition of added plant residues. Bacterial community structure was assessed by DGGE separation of eubacterial 16S rDNA PCR products. PCR-DGGE did not distinguish any significant difference (P&0.05) between the bacterial communities of soils under different treatments, showing differences only between treated soils and the untreated, control soils. Two days after the application of stresses, functional capability differed in soils under different treatments. Soil samples from all the treated plots were less resilient to heat stress than soil from control plots. The initial reduction in decomposition following the addition of copper differed between treatments, but function had not recovered in any of the Cu-amended soils within 28 days. Soil resilience varied according to the type and duration of stress applied, microbial activity, soil characteristics and treatment regimes. The initial resistance of function to stress was not predictive of recovery of unction over time..
机译:在温带的高地草原地区,对土壤在扰动后的微生物功能进行了评估,该土壤位置由苏格兰Sourhope研究站的土壤生物多样性和生态系统功能计划维护。已发表的结果表明,土壤微生物群落对这些最初的干扰具有抵抗力。在本文中,我们测试了它们对于以后的扰动是否同样具有弹性。土壤样品取自田间地块,田间地块接受了代表不同形式摄动的处理,即。重新播种,施用污泥,杀生物剂或氮加石灰,并进行无扰动的控制。通过监测添加的植物残渣的短期分解,评估了进一步扰动后的功能弹性,包括暂时的热量或持续的铜扰动,持续了28天。通过DGGE分离真细菌16S rDNA PCR产物评估细菌群落结构。 PCR-DGGE没有区别在不同处理下的土壤细菌群落之间的任何显着差异(P> 0.05),仅显示了在处理过的土壤和未处理的对照土壤之间的差异。施加应力后两天,在不同处理条件下土壤的功能能力有所不同。与对照样地相比,所有处理样地的土壤样品对热应力的抵抗力均较弱。不同处理之间添加铜后分解的初始减少有所不同,但是在任何经过​​Cu修饰的土壤中,其功能在28天内均未恢复。土壤的适应力根据施加的应力的类型和持续时间,微生物活性,土壤特性和处理方式而变化。功能最初对压力的抵抗力不能预测功能随时间的恢复。

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