Laboratory for Air Pollution/Environmental Technology, Empa, Swiss Federal Laboratories for Materials Science and Technology, Überlandstrasse 129, 8600 Dübendorf, Switzerland.
Environ Sci Technol. 2012 Feb 7;46(3):1650-8. doi: 10.1021/es2034608. Epub 2012 Jan 24.
HFC-1234yf (2,3,3,3-tetrafluoropropene) is under discussion for replacing HFC-134a (1,1,1,2-tetrafluoroethane) as a cooling agent in mobile air conditioners (MACs) in the European vehicle fleet. Some HFC-1234yf will be released into the atmosphere, where it is almost completely transformed to the persistent trifluoroacetic acid (TFA). Future emissions of HFC-1234yf after a complete conversion of the European vehicle fleet were assessed. Taking current day leakage rates and predicted vehicle numbers for the year 2020 into account, European total HFC-1234yf emissions from MACs were predicted to range between 11.0 and 19.2 Gg yr(-1). Resulting TFA deposition rates and rainwater concentrations over Europe were assessed with two Lagrangian chemistry transport models. Mean European summer-time TFA mixing ratios of about 0.15 ppt (high emission scenario) will surpass previously measured levels in background air in Germany and Switzerland by more than a factor of 10. Mean deposition rates (wet + dry) of TFA were estimated to be 0.65-0.76 kg km(-2) yr(-1), with a maxium of ∼2.0 kg km(-2) yr(-1) occurring in Northern Italy. About 30-40% of the European HFC-1234yf emissions were deposited as TFA within Europe, while the remaining fraction was exported toward the Atlantic Ocean, Central Asia, Northern, and Tropical Africa. Largest annual mean TFA concentrations in rainwater were simulated over the Mediterranean and Northern Africa, reaching up to 2500 ng L(-1), while maxima over the continent of about 2000 ng L(-1) occurred in the Czech Republic and Southern Germany. These highest annual mean concentrations are at least 60 times lower than previously determined to be a safe level for the most sensitive aquatic life-forms. Rainwater concentrations during individual rain events would still be 1 order of magnitude lower than the no effect level. To verify these results future occasional sampling of TFA in the atmospheric environment should be considered. If future HFC-1234yf emissions surpass amounts used here studies of TFA accumulation in endorheic basins and other sensitive areas should be aspired.
1,1,1,2-四氟乙烷(HFC-134a)作为汽车空调制冷剂在欧洲汽车市场的使用正在被 2,3,3,3-四氟丙烯(HFC-1234yf)取代。HFC-1234yf 有部分会排放到大气中,在大气中几乎完全转化为持久性的三氟乙酸(TFA)。本文对 HFC-1234yf 在欧洲汽车市场完全取代 HFC-134a 后未来的排放量进行了评估。考虑到目前的泄漏率和 2020 年的车辆预测数量,预计欧洲从汽车空调中排放的 HFC-1234yf 总量将在 11.0-19.2Gg yr(-1) 之间。利用两种拉格朗日化学传输模型对欧洲的 TFA 沉降速率和雨水浓度进行了评估。模拟得到的欧洲夏季 TFA 混合比约为 0.15ppt(高排放情景),比德国和瑞士背景空气中此前测量到的水平高出 10 多倍。TFA 的平均湿沉降和干沉降速率估计为 0.65-0.76kg km(-2) yr(-1),最大值出现在意大利北部,约为 2.0kg km(-2) yr(-1)。约 30-40%的欧洲 HFC-1234yf 排放量以 TFA 的形式在欧洲沉积,其余部分则被输送到大西洋、中亚、北欧和热带非洲。在模拟的地中海和北非地区,TFA 是雨水中浓度最高的地区,达到 2500ng L(-1),而在捷克共和国和德国南部的大陆地区,TFA 的浓度最高,达到 2000ng L(-1)。这些最高的年平均浓度至少比之前确定的对最敏感水生生物的安全水平低 60 倍。在个别降雨事件中,雨水的 TFA 浓度仍将低一个数量级,远低于无影响水平。为了验证这些结果,今后应考虑对大气环境中的 TFA 进行偶发采样。如果未来 HFC-1234yf 的排放量超过了这里的使用量,就应该研究 TFA 在内陆流域和其他敏感地区的积累。