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Dissolved carbon leaching from soil is a crucial component of the net ecosystem carbon balance.

机译:从土壤中溶出的碳淋溶是生态系统净碳平衡的重要组成部分。

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摘要

Estimates of carbon leaching losses from different land use systems are few and their contribution to the net ecosystem carbon balance is uncertain. We investigated leaching of dissolved organic carbon (DOC), dissolved inorganic carbon (DIC), and dissolved methane (CH4), at forests, grasslands, and croplands across Europe. Biogenic contributions to DIC were estimated by means of its Delta 13C signature. Leaching of biogenic DIC was 8.3+or-4.9 g m-2 yr-1 for forests, 24.1+or-7.2 g m-2 yr-1 for grasslands, and 14.6+or-4.8 g m-2 yr-1 for croplands. DOC leaching equalled 3.5+or-1.3 g m-2 yr-1 for forests, 5.3+or-2.0 g m-2 yr-1 for grasslands, and 4.1+or-1.3 g m-2 yr-1 for croplands. The average flux of total biogenic carbon across land use systems was 19.4+or-4.0 g C m-2 yr-1. Production of DOC in topsoils was positively related to their C/N ratio and DOC retention in subsoils was inversely related to the ratio of organic carbon to iron plus aluminium (hydr)oxides. Partial pressures of CO2 in soil air and soil pH determined DIC concentrations and fluxes, but soil solutions were often supersaturated with DIC relative to soil air CO2. Leaching losses of biogenic carbon (DOC plus biogenic DIC) from grasslands equalled 5-98% (median: 22%) of net ecosystem exchange (NEE) plus carbon inputs with fertilization minus carbon removal with harvest. Carbon leaching increased the net losses from cropland soils by 24-105% (median: 25%). For the majority of forest sites, leaching hardly affected actual net ecosystem carbon balances because of the small solubility of CO2 in acidic forest soil solutions and large NEE. Leaching of CH4 proved to be insignificant compared with other fluxes of carbon. Overall, our results show that leaching losses are particularly important for the carbon balance of agricultural systems.
机译:来自不同土地利用系统的碳淋失损失的估算很少,并且它们对生态系统净碳平衡的贡献尚不确定。我们研究了欧洲各地森林,草地和农田中溶解有机碳(DOC),溶解无机碳(DIC)和溶解甲烷(CH 4 )的浸出。通过其Delta 13 C签名估算了DIC的生物成因。森林生物DIC的溶出度为8.3+或-4.9 gm -2 yr -1 ,24.1+或-7.2 gm -2 yr < sup> -1 用于草地,而14.6 + or-4.8 gm -2 yr -1 用于农田。森林的DOC浸出等于3.5+或-1.3 gm -2 yr -1 ,5.3+或-2.0 gm -2 yr 草原为-1 ,农田为4.1+或-1.3 gm -2 yr -1 。整个土地利用系统的总生物碳平均通量为19.4+或-4.0 g C m -2 yr -1 。表土中DOC的产生与它们的C / N比成正相关,而在土壤中的DOC保留与有机碳与铁和铝(氢)氧化物的比成反比。土壤空气中CO 2 的分压和土壤pH决定了DIC的浓度和通量,但相对于土壤空气CO 2 ,土壤溶液中的DIC常常过饱和。草原中生物碳的淋溶损失(DOC加生物DIC)等于净生态系统交换(NEE)的5-98%(中位数:22%)加上施肥的碳输入量减去收获后的碳去除量。碳淋洗使农田土壤的净损失增加了24-105%(中位数:25%)。对于大多数森林地来说,由于CO 2 在酸性森林土壤溶液中的溶解度较小和NEE较大,淋溶几乎不会影响实际的生态系统净碳平衡。与其他碳通量相比,CH 4 的浸出被证明是微不足道的。总体而言,我们的结果表明,浸出损失对于农业系统的碳平衡尤为重要。

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