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Soil COsub2/sub efflux of a larch forest in northern Japan

机译:日本北部落叶松林的土壤CO 2 外排

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We had continuously measured soil CO2 efflux (Rs) in a larch forestin northern Japan at hourly intervals for the snow-free period in 2003 withan automated chamber system and partitioned Rs into heterotrophicrespiration (Rh) and autotrophic respiration (Rr) by using thetrench method. In addition, we applied the soil CO2 concentrationgradients method to continuously measure soil CO2 profiles undersnowpack in the snowy period and to partition Rs into topsoil (Oaand A horizons) CO2 efflux (Ft) with a depth of 0.13 m and sub-soil(C horizon) CO2 efflux (Fc). We found that soil CO2 effluxeswere strongly affected by the seasonal variation of soil temperature butweakly correlated with soil moisture, probably because the volumetric soilmoisture (30–40% at 95% confidence interval) was within a plateauregion for root and microbial activities. The soil CO2 effluxes changedseasonally in parallel with soil temperature in topsoil with the peak inlate summer. On the other hand, the contribution of Rr to Rs was thelargest at about 50% in early summer, when canopy photosynthesis andplant growth were more active. The temperature sensitivity (Q10) ofRr peaked in June. Under snowpack, Rs was stable until mid-March andthen gradually increased with snow melting. Rs summed up to79 gC m?2 during the snowy season for 4 months. The annual Rs wasdetermined at 934 gC m?2 y?1 in 2003, which accounted for 63%of ecosystem respiration. The annual contributions of Rh and Rs toRs were 57% and 43%, respectively. Based on the gradient approach,Rs was partitioned vertically into litter (Oi and Oe horizons)with a depth of 0.01–0.02 m, topsoil and sub-soil respirations withproportions of 6, 72 and 22%, respectively, on an annual basis. Thevertical distribution of CO2 efflux was consistent with those of soilcarbon and root biomass.
机译:我们在2003年无雪期以小时间隔连续测量了日本北部落叶松林中的土壤CO 2 外排量( R s )用自动室系统将 R s 分为异养性呼吸( R h )和自养呼吸( R r )。此外,我们应用土壤CO 2 浓度梯度方法,连续测量雪期下雪期土壤CO 2 剖面,并划分 R s 进入表土(O a 和A层)CO 2 外排( F t )深度为0.13 m且地下土壤(C层)CO 2 外流( F c )。我们发现土壤CO 2 的流出量受到土壤温度的季节性变化的强烈影响,但与土壤水分的相关性微弱,这可能是因为土壤水分的体积(95%置信区间为30–40%)处于高原地区。根和微生物活动。土壤CO 2 的通量随土壤温度随季节呈季节变化,夏末最高。另一方面,夏季初 R r 对 R s 的贡献最大,约为50% ,当冠层光合作用和植物生长更加活跃时。 R r 的温度敏感性( Q 10 )在6月达到峰值。在积雪下, R s 一直稳定到3月中旬,然后随着融雪而逐渐增加。 R s 在雪季持续4个月的总和为79 gC m ?2 。 2003年确定的年度 R s 为934 gC m ?2 y ?1 ,占63%生态系统呼吸。 R h 和 R s 对 R s的年度贡献分别为57%和43%。基于梯度方法,将 R s 垂直划分为凋落物(O i 和O e 层)深度为0.01-0.02 m,表土和下层土壤呼吸的比例分别为每年6%,72%和22%。 CO 2 外排的垂直分布与土壤碳和根系生物量的垂直分布基本一致。

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