三江平原新鲜沼泽土添加不同量的NH4HCO3后,在25°C下进行了6次连续培养。首次在大气浓度CH4(约1.8 μl/l)中培养时,供试沼泽土氧化大气CH4速率与NH4HCO3的加入量成反比,表明NH4+最初抑制沼泽土氧化大气浓度CH4。第1次用高浓度CH4(约8 000 μl/l)培养沼泽土时,铵态氮抑制供试沼泽土氧化高浓度CH4,但随着培养的继续,铵态氮的抑制作用逐渐减弱,最终转变为促进供试沼泽土氧化高浓度CH4。经过高浓度CH4培养后,添加NH4HCO3的供试沼泽土氧化大气CH4速率上升2.6~5倍,且与NH4HCO3的加入量呈正相关,表明铵态氮肥最初对沼泽土氧化CH4的抑制作用已经转变为促进作用。铵态氮对沼泽土氧化大气浓度CH4和高浓度CH4的抑制作用都是短暂的,其长期作用将是促进沼泽土氧化CH4。
Wetland, one of the most important ecosystems in the world, plays a significant role in global C and N cycles. Although the majority of studies to date have been centered on wetlands as CH4 sources, wetland soils can however also act as CH4 sinks. It has been recognized that Sanjiang Plain palustrine wetland (45°01'-48°28'N, 130°13'-135°05'E), one of the largest palustrine wetland areas in China, play a significant role in the estimation of CH4 budgets. To find the influence of nitrogen fertilizer on CH4 oxidation in mire soils, the fresh mire soil from Sanjiang Plain was amended with 0, 25 or 50 mg(N)/l NH4HCO3 and incubated at 25℃ over six consecutive periods: first at atmospheric CH4 concentration (about 1.8 μL/L), then at elevated CH4 concentration (about 8000 μL/L) for four times, and finally at concentration of about 1.8μL/L. The addition of NH4HCO3 resulted in reduction in the rate of CH4 oxidation approximately in inverse proportion to the amount of NH4HCO3 added. At ~8000 μL/L, the initial inhibitory effect was gradually released and disappeared during subsequent incubations. Finally, NH4HCO3 addition stimulated the CH4 oxidation. NH4HCO3 addition stimulated the rates of CH4 oxidation by the mire soil at atmospheric CH4 concentration during the final incubation. The initial inhibitory effect of NH4HCO3 addition on CH4 oxidation at both atmospheric CH4 concentration and high CH4 concentration in mire soil is temporary, and the long-term effect of NH4HCO3 addition may be stimulating.
[1] 张峰,周维芝,张坤.湿地生态系统的服务功益及可持续利用[J].地理科学,2003, 23(6): 674~679.
[2] 宋长春.湿地生态系统碳循环研究进展[J].地理科学, 2003, 23(5): 622~628.
[3] 吕宪国,黄锡畴.我国湿地研究进展[J].地理科学, 1998, 18(4): 293~300.
[4] Kravchenko I K. Methane oxidation in boreal peat soils treated with various nitrogen compounds[J]. Plant and Soil, 2002, 242: 157-162.
[5] 丁维新,蔡祖聪.沼泽甲烷排放及其主要影响因素[J].地理科学, 2002, 22(5): 619~625.
[6] 王德宣,吕宪国,丁维新,等.三江平原沼泽湿地与稻田CH4排放对比研究[J].地理科学, 2002, 22(4): 500~504.
[7] 崔保山.三江平原沼泽地CH4排放规律及估算[J].地理科学,1997, 17(1): 93~95.
[8] 王长科,吕宪国,蔡祖聪,等.东北三江平原土壤氧化CH4研究[J].环境科学学报, 2004,24(5): 939~941.
[9] 鲁如坤.土壤农业化学分析方法[M].北京:中国农业科技出版社,1999.289.
[10] Sitaula B K, Hansen S, Sitaula J I B, et al. Methane oxidation potentials and fluxes in agricultural soil: effects of fertilizationand soil compaction[J]. Biogeochemistry, 2000, 48(3): 323-339.
[11] Hutsch B W, Webster C P, Powlson D S. Long-term effects of nitrogen fertilization on methane oxidation in soil of the Broadbalk Wheat Experiment[J]. Soil Biology and Biochemistry, 1993, 25(10): 1307-1315.
[12] Cai Z C, Mosier A R. Effect of NH4Cl addition on methane oxidation by paddy soils[J]. Soil Biology and Biochemistry, 2000, 32: 1537-1545.
[13] Bodeller P L E, Roslev P, Henckel T, et al. Stimulation by ammonium-based fertilizers of methane oxidation in soil around rice roots[J]. Nature, 2000, 403(6768): 421-424.