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首页> 外文期刊>Oecologia >Soil carbon dioxide partial pressure and dissolved inorganic carbonate chemistry under elevated carbon dioxide and ozone
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Soil carbon dioxide partial pressure and dissolved inorganic carbonate chemistry under elevated carbon dioxide and ozone

机译:二氧化碳和臭氧升高下的土壤二氧化碳分压和溶解的无机碳酸盐化学

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Global emissions of atmospheric CO(2) and tropospheric O(3) are rising and expected to impact large areas of the Earth's forests. While CO(2) stimulates net primary production, O(3) reduces photosynthesis, altering plant C allocation and reducing ecosystem C storage. The effects of multiple air pollutants can alter belowground C allocation, leading to changes in the partial pressure of CO(2) (pCO(2)) in the soil , chemistry of dissolved inorganic carbonate (DIC) and the rate of mineral weathering. As this system represents a linkage between the long- and short-term C cycles and sequestration of atmospheric CO(2), changes in atmospheric chemistry that affect net primary production may alter the fate of C in these ecosystems. To date, little is known about the combined effects of elevated CO(2) and O(3) on the inorganic C cycle in forest systems. Free air CO(2) and O(3) enrichment (FACE) technology was used at the Aspen FACE project in Rhinelander, Wisconsin to understand how elevated atmospheric CO(2) and O(3) interact to alter pCO(2) and DIC concentrations in the soil. Ambient and elevated CO(2) levels were 360+/-16 and 542+/-81 microl l(-1), respectively; ambient and elevated O(3) levels were 33+/-14 and 49+/-24 nl l(-1), respectively. Measured concentrations of soil CO(2) and calculated concentrations of DIC increased over the growing season by 14 and 22%, respectively, under elevated atmospheric CO(2) and were unaffected by elevated tropospheric O(3). The increased concentration of DIC altered inorganic carbonate chemistry by increasing system total alkalinity by 210%, likely due to enhanced chemical weathering. The study also demonstrated the close coupling between the seasonal delta(13)C of soil pCO(2) and DIC, as a mixing model showed that new atmospheric CO(2) accounted for approximately 90% of the C leaving the system as DIC. This study illustrates the potential of using stable isotopic techniques and FACE technology to examine long- and short-term ecosystem C sequestration.
机译:大气中CO(2)和对流层O(3)的全球排放量正在上升,预计会影响地球森林的大部分地区。虽然CO(2)刺激了净初级生产力,但O(3)减少了光合作用,改变了植物C的分配并减少了生态系统C的存储。多种空气污染物的影响可以改变地下C的分配,从而导致土壤中CO(2)(pCO(2))的分压,溶解性无机碳酸盐(DIC)的化学性质和矿物风化率的变化。由于该系统代表了长期和短期C循环与封存大气CO(2)之间的联系,因此影响净初级生产的大气化学变化可能会改变这些生态系统中C的命运。迄今为止,对于森林系统中无机碳循环对CO(2)和O(3)升高的综合影响知之甚少。自由空气CO(2)和O(3)富集(FACE)技术在威斯康星州莱茵兰德市的Aspen FACE项目中使用,以了解大气中CO(2)和O(3)的相互作用如何改变pCO(2)和DIC在土壤中的浓度。环境和升高的CO(2)水平分别为360 +/- 16和542 +/- 81 microl l(-1);环境和升高的O(3)水平分别为33 +/- 14和49 +/- 24 nl(-1)。在大气CO(2)升高的情况下,土壤CO(2)的测量浓度和DIC的计算浓度在整个生长季节分别增加了14%和22%,并且不受对流层O(3)的影响。 DIC浓度的增加通过将系统的总碱度提高210%,改变了无机碳酸盐的化学性质,这可能是由于化学风化的增强。该研究还证明了土壤pCO(2)的季节性delta(13)C与DIC之间的紧密耦合,因为混合模型显示,新的大气CO(2)约占90%的C,而将系统作为DIC。这项研究说明了使用稳定同位素技术和FACE技术检查长期和短期生态系统碳固存的潜力。

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