Mueller Kevin E, Shann Jodi R
Department of Biological Sciences, University of Cincinnati, Cincinnati, OH 45221-0006, USA.
J Environ Qual. 2007 Jan 9;36(1):120-7. doi: 10.2134/jeq2006.0130. Print 2007 Jan-Feb.
This study investigated the effects of organic and inorganic nutrients on the microbial degradation of the common soil contaminant pyrene. The material used in this investigation was collected from potted trees that had been growing for over a year in a soil artificially contaminated with polycyclic aromatic hydrocarbons. Soil was removed from the nonroot (bulk) and root (rhizosphere) zones of these pots and used in mineralization studies that tracked microbial degradation of 14C-pyrene. The factors influencing degradation in these zones were then tested by amendment with essential inorganic nutrients or with root-derived materials. As expected, pyrene mineralization was greater in soil removed from the rhizosphere than in bulk soil. The rate of mineralization in rhizosphere soil was inhibited by inorganic nutrient amendment, whereas nutrients stimulated mineralization in the bulk soil. Pyrene mineralization in bulk soil was also increased by the addition of root extracts intended to mimic exudation by living roots. However, amendment with excised fine roots that were allowed to decay over time in soil initially inhibited mineralization. With time, the rate of mineralization increased, eventually exceeding that of unamended bulk soil. Combined, the initial inhibition and subsequent stimulation produced a zero net impact of decaying fine roots on bulk soil mineralization. Our results, in conjunction with known temporal patterns of fine root dynamics in natural systems, support the idea that seasonal variations in nutrient and substrate availability may influence the long-term effect of plants on organic degradation in soil, possibly reducing or negating the beneficial effects of vegetation that are often observed in short-term studies.
本研究调查了有机和无机养分对常见土壤污染物芘微生物降解的影响。本研究使用的材料取自盆栽树木,这些树木在人工受多环芳烃污染的土壤中生长了一年多。从这些花盆的非根(土体)和根(根际)区域取出土壤,用于追踪14C-芘微生物降解的矿化研究。然后通过添加必需的无机养分或根衍生材料来测试影响这些区域降解的因素。正如预期的那样,根际土壤中芘的矿化程度高于土体土壤。无机养分添加抑制了根际土壤的矿化速率,而养分促进了土体土壤的矿化。添加旨在模拟活根分泌物的根提取物也增加了土体土壤中芘的矿化。然而,添加在土壤中随时间腐烂的细根最初抑制了矿化。随着时间的推移,矿化速率增加,最终超过未添加细根的土体土壤。综合来看,最初的抑制和随后的促进对土体土壤矿化产生了细根腐烂的零净影响。我们的结果与自然系统中细根动态的已知时间模式相结合,支持了养分和底物可用性的季节性变化可能影响植物对土壤中有机降解的长期影响的观点,这可能会减少或消除短期研究中经常观察到的植被有益影响。