Institute of Biological and Environmental Sciences, University of Aberdeen, Cruickshank Building, St. Machar Drive, Aberdeen AB24 3UU, UK.
Appl Environ Microbiol. 2010 Nov;76(22):7626-34. doi: 10.1128/AEM.00595-10. Epub 2010 Oct 1.
Both bacteria and thaumarchaea contribute to ammonia oxidation, the first step in nitrification. The abundance of putative ammonia oxidizers is estimated by quantification of the functional gene amoA, which encodes ammonia monooxygenase subunit A. In soil, thaumarchaeal amoA genes often outnumber the equivalent bacterial genes. Ecophysiological studies indicate that thaumarchaeal ammonia oxidizers may have a selective advantage at low ammonia concentrations, with potential adaptation to soils in which mineralization is the major source of ammonia. To test this hypothesis, thaumarchaeal and bacterial ammonia oxidizers were investigated during nitrification in microcosms containing an organic, acidic forest peat soil (pH 4.1) with a low ammonium concentration but high potential for ammonia release during mineralization. Net nitrification rates were high but were not influenced by addition of ammonium. Bacterial amoA genes could not be detected, presumably because of low abundance of bacterial ammonia oxidizers. Phylogenetic analysis of thaumarchaeal 16S rRNA gene sequences indicated that dominant populations belonged to group 1.1c, 1.3, and "deep peat" lineages, while known amo-containing lineages (groups 1.1a and 1.1b) comprised only a small proportion of the total community. Growth of thaumarchaeal ammonia oxidizers was indicated by increased abundance of amoA genes during nitrification but was unaffected by addition of ammonium. Similarly, denaturing gradient gel electrophoresis analysis of amoA gene transcripts demonstrated small temporal changes in thaumarchaeal ammonia oxidizer communities but no effect of ammonium amendment. Thaumarchaea therefore appeared to dominate ammonia oxidation in this soil and oxidized ammonia arising from mineralization of organic matter rather than added inorganic nitrogen.
细菌和氨氧化古菌都参与氨氧化作用,这是硝化作用的第一步。功能基因 amoA 用于估计潜在氨氧化菌的丰度,amoA 基因编码氨单加氧酶亚单位 A。在土壤中,氨氧化古菌 amoA 基因的数量通常多于等效的细菌基因。生态生理学研究表明,氨氧化古菌可能在低氨浓度下具有选择性优势,并且可能适应于矿化作用是氨主要来源的土壤。为了验证这一假设,在含有有机、酸性森林泥炭土(pH 值为 4.1)的微宇宙中进行硝化作用时,研究了氨氧化菌的氨氧化菌和细菌氨氧化菌,该土壤中氨浓度低,但在矿化作用期间具有高氨释放潜力。净硝化速率很高,但添加铵不会影响。可能由于细菌氨氧化菌的丰度低,无法检测到细菌 amoA 基因。系统发育分析表明,优势种群属于 1.1c、1.3 和“深泥炭”谱系,而已知的 amo 包含谱系(1.1a 和 1.1b 组)仅占总群落的一小部分。硝化过程中 amoA 基因的丰度增加表明氨氧化古菌的生长,但添加铵对其没有影响。同样,amoA 基因转录物的变性梯度凝胶电泳分析表明,氨氧化古菌群落的时间变化很小,但铵添加没有影响。因此,氨氧化古菌似乎在该土壤中主导氨氧化作用,并氧化有机物质矿化产生的氨,而不是添加的无机氮。