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Molecular hydrogen (H2) combustion emissions and their isotope (D/H) signatures from domestic heaters, diesel vehicle engines, waste incinerator plants, and biomass burning

机译:家用加热器,柴油发动机,废物焚化炉和生物质燃烧产生的分子氢(H2)燃烧排放物及其同位素(D / H)标记

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摘要

Molecular hydrogen (H), its stable isotope signature (δD), and thekey combustion parameters carbon monoxide (CO), carbon dioxide (CO), andmethane (CH) were measured from various combustion processes. H inthe exhaust of gas and oil-fired heaters and of waste incinerator plants wasgenerally depleted compared to ambient intake air, while CO was significantlyelevated. These findings contradict the often assumed co-occurring net Hand CO emissions in combustion processes and suggest that previous Hemissions from combustion may have been overestimated when scaled to COemissions. For the gas and oil-fired heater exhausts, H and δDgenerally decrease with increasing CO, from ambient values of~0.5 ppm and +130‰ to 0.2 ppm and −206‰,respectively. These results are interpreted as a combination of anisotopically light H source from fossil fuel combustion and a D/H kineticisotope fractionation of hydrogen in the advected ambient air during itspartial removal during combustion. Diesel exhaust measurements fromdynamometer test stand driving cycles show elevated H and CO emissionsduring cold-start and some acceleration phases. While H and CO emissionsfrom diesel vehicles are known to be significantly less than those fromgasoline vehicles (on a fuel-energy base), we find that their molar H/COratios (median 0.026, interpercentile range 0.12) are also significantly lesscompared to gasoline vehicle exhaust. Using H/CO emission ratios, alongwith CO global emission inventories, we estimate global H emissions for2000, 2005, and 2010. For road transportation (gasoline and diesel), wecalculate 8.3 ± 2.2 Tg, 6.0 ± 1.5 Tg, and 3.8 ± 0.94 Tg,respectively, whereas the contribution from diesel vehicles is low(0.9–1.4%). Other fossil fuel emissions are believed to be negligiblebut H emissions from coal combustion are unknown. For residential(domestic) emissions, which are likely dominated by biofuel combustion,emissions for the same years are estimated at 2.7 ± 0.7 Tg,2.8 ± 0.7 Tg, and 3.0 ± 0.8 Tg, respectively. For biomass burning Hemissions, we derive a mole fraction ratio ΔH/ΔCH(background mole fractions subtracted) of 3.6 using wildfire emission datafrom the literature and support these findings with our wood combustionresults. When combining this ratio with CH emission inventories, theresulting global biomass burning H emissions agree well with publishedglobal H emissions, suggesting that CH emissions may be a good proxyfor biomass burning H emissions.
机译:从各种燃烧过程中测量了分子氢(H),其稳定的同位素特征(δD)以及关键燃烧参数一氧化碳(CO),二氧化碳(CO)和甲烷(CH)。与环境进气相比,燃气和燃油加热器以及垃圾焚烧厂的废气中的H普遍减少,而CO则显着升高。这些发现与在燃烧过程中通常假定的同时发生的手部净CO排放量相矛盾,并表明当按CO排放量缩放时,以前的燃烧排放量可能被高估了。对于燃气和燃油加热器的排气,H和δD通常随着CO的增加而降低,分别从〜0.5 ppm和+ 130‰的环境值降低到0.2 ppm和-206‰的环境值。这些结果被解释为来自化石燃料燃烧的同位素轻氢源与在燃烧过程中部分除去的对流环境空气中氢的D / H动力学同位素分馏的组合。测功机试验台的柴油机排气测量表明,在冷启动和某些加速阶段,H和CO排放量升高。虽然已知柴油车辆的H和CO排放量要比汽油车辆的H和CO排放量要低得多(基于燃料能源),但我们发现它们的摩尔H / COratios(中位数为0.026,百分位数范围为0.12)也比汽油车辆的排放量要少得多。 。使用H / CO排放比,以及CO全球排放清单,我们估算2000年,2005年和2010年的全球H排放。对于公路运输(汽油和柴油),我们计算8.3±2.2 Tg,6.0±1.5 Tg和3.8±0.94 Tg ,而柴油车的贡献较低(0.9-1.4%)。据信其他化石燃料的排放量可以忽略不计,但燃煤产生的H排放量尚不清楚。对于可能由生物燃料燃烧占主导的住宅(家庭)排放,估计同一年的排放分别为2.7±0.7 Tg,2.8±0.7 Tg和3.0±0.8 Tg。对于生物质燃烧排放,我们使用文献中的野火排放数据得出了3.6的摩尔分数比ΔH/ΔCH(减去背景摩尔分数),并用我们的木材燃烧结果支持了这些发现。当将此比率与CH排放清单相结合时,得出的全球生物质燃烧H排放量与已公布的全球H排放量非常吻合,这表明CH排放量可以很好地替代生物质燃烧H排放量。

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