Centre d'Ecologie des Ressources Renouvelables (L.P. CNRS no. 8211), 29, rue Jeanne Marvig, 31055 Toulouse Cédex, and Centre de Physiologie Végétale (U.A. CNRS no. 241), Université Paul Sabatier, 31062 Toulouse Cédex, France.
Appl Environ Microbiol. 1989 Apr;55(4):922-6. doi: 10.1128/aem.55.4.922-926.1989.
The contribution of lignin to the formation of humic compounds was examined in different environments of the terrestrial-aquatic interface in the Garonne River valley in southwestern France. Alluvial soils and submerged or nonsubmerged river and pond sediments containing alder, poplar, or willow [C-lignin]ligno-celluloses were incubated. After a 49-day incubation period, 10 to 15% of labeled lignins in alluvial soils was recovered as evolved CO(2). In nonsubmerged sediments, 10% of the applied activity was released as CO(2), and in submerged sediments, only 5% was released after 60 days of incubation. In the different alluvial soils and sediments, the bulk of residual activity (70 to 85%) remained in the two coarsest-grain fractions (2,000 to 100 and 100 to 50 mum). Only 2 to 6% of the residual activity of these two coarse fractions was recovered as humic and fulvic acids, except in the case of alder [C-lignin]lignocellulose, which had decomposed in a soil collected beneath alders. In this one 55% of the residual activity was extracted as humic substances from the 2,000- to 100-mum fraction. Humic and fulvic acids represented from 6 to 50% of the residual activity in the finest-grain fractions (50 to 20 and 20 to 0 mum). The highest percentages were obtained in soil collected beneath alders and in submerged pond sediment. The contribution of different groups of microorganisms, as well as nutrients and clay content, may influence humic-substance formation in such environments. Physical stability also may be an important factor for complex microbial activity involved in this process.
本研究考察了法国西南部加龙河流域陆地-水域界面不同环境中木质素对腐殖质形成的贡献。含有桤木、白杨或柳树[C-木质素]木质纤维素的冲积土壤和淹没或未淹没的河流和池塘沉积物被用来进行培养。经过 49 天的培养期后,在冲积土壤中,10%到 15%的标记木质素以释放的 CO2形式被回收。在未淹没的沉积物中,10%的应用活性被释放为 CO2,而在淹没的沉积物中,经过 60 天的培养后,只有 5%被释放。在不同的冲积土壤和沉积物中,大部分残留活性(70%至 85%)仍存在于两个最粗粒级(2000 至 100 和 100 至 50 微米)中。除了在柳树[C-木质素]木质纤维素分解的土壤中,这两个粗粒级的残留活性中只有 2%至 6%被回收为腐殖酸和富里酸。在这种情况下,从 2000 至 100 微米级的粗粒级中提取了 55%的残留活性作为腐殖质物质。在最细粒级(50 至 20 和 20 至 0 微米)中,腐殖酸和富里酸分别占残留活性的 6%至 50%。在柳树下采集的土壤和淹没的池塘沉积物中获得的比例最高。不同微生物群、养分和粘土含量的贡献可能会影响此类环境中腐殖质物质的形成。物理稳定性也可能是参与这一过程的复杂微生物活性的一个重要因素。