PDF HTML阅读 XML下载 导出引用 引用提醒 施氮对亚热带樟树林土壤呼吸的影响 DOI: 10.5846/stxb201203130334 作者: 作者单位: 中南林业科技大学,城市森林生态湖南省重点实验室;中南林业科技大学,中南林业科技大学,城市森林生态湖南省重点实验室;中南林业科技大学,城市森林生态湖南省重点实验室;中南林业科技大学,湖南会同杉木林生态系统国家野外科学观测研究站;中南林业科技大学 作者简介: 通讯作者: 中图分类号: 基金项目: "十二五"农村领域国家科技计划课题(2011BAD38B0204);教育部新世纪优秀人才支持计划(NCET-10-0151);湖南省科技厅项目(2010TP4011-3);湖南省教育厅项目(湘财教字[2010]70号);长沙市科技局项目(K1003009-61) Effect of nitrogen addition to soil respiration in Cinnamomum camphora forest in subtropical China Author: Affiliation: Central South University of Forestry and Technology,Key laboratory of Urban Forest Ecology of Hunan Province;Central South University of Forestry and Technology,Central South University of Forestry and Technology,Key laboratory of Urban Forest Ecology of Hunan Province;Central South University of Forestry and Technology,Key laboratory of Urban Forest Ecology of Hunan Province;Central South University of Forestry and Technology,Central South University of Forestry and Technology Fund Project: 摘要 | 图/表 | 访问统计 | 参考文献 | 相似文献 | 引证文献 | 资源附件 | 文章评论 摘要:人类活动引起全球范围内大气氮沉降量的升高,增加了陆地生态系统氮输入,从而影响土壤CO2排放。为揭示生态系统氮输入升高对土壤呼吸的影响,2010年6月至2012年1月,对亚热带樟树林(Cinnamomum camphora)进行模拟氮添加试验,每月上、下旬采用红外分析法测定4种氮输入水平(CK,0 g m-2a-1;低氮LN,5 g m-2 a-1;中氮MN,15 g m-2 a-1;高氮HN,30 g m-2 a-1)下的土壤呼吸速率。结果表明:(1)樟树林土壤呼吸存在明显的季节动态,最高值出现在6月,最小值出现在1月。氮添加处理显著抑制了樟树林的土壤呼吸,LN、MN、HN处理土壤呼吸年累积量分别较对照CK下降37.66%、30.62%、38.95%,各施氮处理间无显著差异,施氮对土壤呼吸的抑制作用随时间推移而减弱;(2)氮添加不影响土壤呼吸昼夜波动特征,但显著抑制土壤呼吸速率;(3)土壤呼吸与土壤温度间存在极显著的指数关系,与土壤湿度相关性不显著,CK、LN处理Q10相近,MN处理最小:(4)氮添加处理促进了土壤中氮的淋失,且随施氮水平的升高而增大。 Abstract:Increasing global atmospheric deposition of nitrogen caused by human activities has raised nitrogen input to terrestrial ecosystem, and thus influenced carbon dioxide emissions from soil. To explore how soil respiration response to increased nitrogen input, a simulated nitrogen deposition experiment has been conducted in Cinnamomum camphora forest in subtropical China between June 2010 and January 2012. Soil respiration rate was measured twice a month under four-levels of N treatments (CK, 0 g m-2a-1; LN, 5 g m-2a-1; MN, 15 g m-2a-1; HN, 30 g m-2a-1, experimental inputs)by infrared gas analyzer techniques, and the results showed that soil respiration exhibited a strong seasonal pattern, with the highest rates found in the June (819.31 mgCO2 m-2 h-1) and the lowest rates in January (169.70 mgCO2 m-2 h-1). Nitrogen addition inhibited soil respiration significantly. Soil respiration in CK group was higher than that in any other treatment group. Annual accumulative soil respiration in LN(2.55×104 kg/hm2), MN(2.84×104 kg/hm2) and HN(2.50×104 kg/hm2) was 37.66%、30.62%、38.95%, respectively, lower than in CK(4.09× 104 kg/hm2) group, however, there was no significant difference between nitrogen treatment groups. The inhibitory effect weakened over time. From June to September in year 2010, the mean soil respiration rate of LN, MN and HN were (386.31±44.81) mgCO2 m-2 h-1、(358.25±31.55) mgCO2 m-2 h-1and (367.35±41.72) mgCO2 m-2 h-1, respectively, which were 49.63%、53.28% and 52.10% lower than that in CK group(766.87±101.60 mgCO2 m-2 h-1). During same time in year 2011, the mean soil respiration of LN, MN and HN group increased to (512.7±73.12) mgCO2 m-2 h-1,(533.02±41.80) mgCO2 m-2 h-1,(486.20±50.12) mgCO2 m-2 h-1,respectively, which were19.70%、16.51%、23.85% lower than that in CK(638.45±74.91 mgCO2 m-2 h-1). Nitrogen addition couldn't change the diurnal soil respiration pattern, but depressed magnitude of soil respiration significantly. Soil respiration during daytime was lower than that in night, the minimums appeared in 10:00-14:00 and the maximums were in 22:00-2:00. The diurnal mean soil respiration rare in CK, LN, MN and HN treatment group was (805.86±74.95) mg CO2 m-2 h-1, (689.29±66.25) mg CO2 m-2 h-1, (778.85±73.73) mg CO2 m-2 h-1 and (609.85±65.33) mg CO2 m-2 h-1, respectively, and the mean soil respiration rate in CK group was significantly higher than that in LN and HN group(P<0.01). The differences between each nitrogen addition group were significantly. Soil respiration has the similar seasonal and diurnal pattern with soil temperature at 5cm depth. No matter in seasonal scale or diurnal scale, soil respiration rates showed a positive exponential relationship with soil temperature at 5cm depth, Exponential relationships between temperature and soil respiration were highly significant in all plots. However, almost in treatment, there was no obvious effect of soil moisture on soil respiration. LN group had the largest Q10 values (2.01), which similar to CK group (1.99) and higher than MN (1.79) and HN group (1.95). These results indicated that there is a significant decline of soil respiration to N addition in subtropical Cinnamomum camphora forest. 参考文献 相似文献 引证文献
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