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Trifluoroacetic Acid from Degradation of HCFCs and HFCs: A Three-dimensional Modeling Study

机译:降解HCFC和HFC的三氟乙酸:三维建模研究

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摘要

Trifluoroacetic acid (TFA; CF3 COOH) is produced by the degradation of the halocarbon replacements HFC-134a, HCFC-124, and HCFC-123. The formation of TFA occurs by HFC/HCFC reacting with OH to yield CF3COX (X = F or CI), followed by in-cloud hydrolysis of CF3COX to form TFA. The TFA formed in the clouds may be reevaporated but is finally deposited onto the surface by washout or dry deposition. Concern has been expressed about the possible long-term accumulation of TFA in certain aquatic environments, pointing to the need to obtain information on the concentrations of TFA in rainwater over scales ranging from local to continental. Based on projected concentrations for HFC-134a, HCFC-124, and HCFC-123 of 80, 10, and 1 pptv in the year 2010, mass conservation arguments imply an annually averaged global concentration of 0.16 microg/L if washout were the only removal mechanism for TFA. We present 3-D simulations of the HFC/HCFC precursors of TFA that include the rates of formation and deposition of TFA based on assumed future emissions. An established (GISS/Harvard/ UCI) but coarse-resolution (8 deg latitude by 10 deg longitude) chemical transport model was used. The anually averaged rainwater concentration of 0.12 gg/L (global) was calculated for the year 2010, when both washout and dry deposition are included as the loss mechanism for TFA from the atmosphere. For some large regions in midnorthern latitudes, values are larger, 0.15-0.20 microg/L. The highest monthly averaged rainwater concentrations of TFA for northern midlatitudes were calculated for the month of July, corresponding to 0.3-0.45 microg/L in parts of North America and Europe. Recent laboratory experiments have suggested that a substantial amount of vibrationally excited CF3CHFO is produced in the degradation of HFC-134a, decreasing the yield of TFA from this compound by 60%. This decrease would reduce the calculated amounts of TFA in rainwater in the year 2010 by 26%, for the same projected concentrations of precursors.
机译:三氟乙酸(TFA; CF3 COOH)是通过卤代烃替代品HFC-134a,HCFC-124和HCFC-123的降解而产生的。 TFA的形成是通过HFC / HCFC与OH反应生成CF3COX(X = F或CI),然后在云端将CF3COX水解形成TFA。云中形成的TFA可以重新蒸发,但最终通过冲洗或干法沉积而沉积在表面上。人们对某些水生环境中TFA可能长期积累表示关切,指出有必要获取有关从局部到大陆范围的雨水中TFA浓度的信息。根据2010年HFC-134a,HCFC-124和HCFC-123的预计浓度分别为80、10和1 pptv,质量守恒定律的论点是,如果唯一的去除方法是清除,则全球年平均浓度为0.16微克/升。 TFA机制。我们介绍了TFA的HFC / HCFC前体的3-D模拟,包括基于假定的未来排放量的TFA的形成和沉积速率。使用已建立的(GISS / Harvard / UCI)但分辨率较粗(经度8度乘以10度)的化学传输模型。计算了2010年的年平均雨水浓度为0.12 gg / L(全球),其中包括冲刷和干沉降作为大气中TFA的损失机制。对于中北纬度的一些大区域,值较大,为0.15-0.20 microg / L。计算了7月当月北半球最高TFA的月平均雨水最高浓度,相当于北美和欧洲部分地区的0.3-0.45 microg / L。最近的实验室实验表明,在HFC-134a的降解过程中会产生大量的振动激发CF3CHFO,从而使该化合物的TFA收率降低60%。对于相同的前体预计浓度,这种减少将使2010年雨水中TFA的计算量减少26%。

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