Instituto de Ingeniería, Universidad Nacional Autónoma de México, Av. Universidad 3000, 04510 México D.F., México.
Molina Center for Energy and the Environment, 3252 Holiday Ct, Suite 223, La Jolla 92037, USA.
Sci Total Environ. 2019 Mar 15;656:468-474. doi: 10.1016/j.scitotenv.2018.11.373. Epub 2018 Nov 26.
Wastewater treatment is an important source of methane (CH) emissions. In most large-size aerobic treatment plants, the excess sludge is digested in anaerobic reactors (AD), with the concomitant CH emissions. The guidelines of the Intergovernmental Panel on Climate Change (IPCC) have been adopted worldwide for quantifying the national emission inventories, which include wastewater treatment plants (WWTP) as a key category. The IPCC recommends using default emission factors (Tier 1) for countries with limited available data (such as Mexico and most developing countries). However, these estimates have a high degree of uncertainty, owing to the lack of reliable information about the operation process and local environmental conditions. In order to reduce uncertainty in the estimation of CH emission from WWTP in Mexico, a country-specific emission factor was determined for AD associated with activated sludge process. This was accomplished with on-site data obtained from the AD of six activated sludge WWTP. In addition, the measured CH emissions were compared to those resulting from the application of the IPCC Tier 1 method, using the recommended default methane correction factor (MCF: 0.8) as well as alternate values (0.32 and 0.26) recently proposed by the authors. Results show that the IPCC Tier 1 method, using the recommended MCF, highly overestimate CH emissions compared with the values obtained on-site. In contrast, the alternate MCF achieved better estimations than the IPCC-recommended MCF, much closer to the observed emission values. The CH emission factor proposed as country (Mexico) specific value is 0.49 kg CH/kg BOD, which would allow the application of IPCC Tier 2 method. By doing so, the uncertainty associated with CH emission from aerobic treatment plants with AD would be reduced. This, in turn, would provide important information for implementing appropriate CH mitigation strategies for the water sector.
污水处理是甲烷 (CH) 排放的重要来源。在大多数大型好氧处理厂中,剩余污泥在厌氧反应器 (AD) 中消化,同时伴随着 CH 排放。政府间气候变化专门委员会 (IPCC) 的指南已在全球范围内采用,用于量化国家排放清单,其中包括污水处理厂 (WWTP) 作为一个关键类别。对于数据有限的国家(如墨西哥和大多数发展中国家),IPCC 建议使用默认排放因子(第 1 层)。然而,由于缺乏有关运营过程和当地环境条件的可靠信息,这些估计存在高度不确定性。为了降低墨西哥 WWTP 中 CH 排放估算的不确定性,确定了与活性污泥工艺相关的 AD 的特定于国家的排放因子。这是通过从六个活性污泥 WWTP 的 AD 获得的现场数据来实现的。此外,还将测量的 CH 排放量与应用 IPCC 第 1 层方法的结果进行了比较,使用推荐的默认甲烷校正因子 (MCF:0.8) 以及作者最近提出的替代值 (0.32 和 0.26)。结果表明,与现场获得的值相比,使用推荐 MCF 的 IPCC 第 1 层方法高度高估了 CH 排放量。相比之下,替代 MCF 比 IPCC 推荐的 MCF 实现了更好的估算,更接近观察到的排放值。作为国家(墨西哥)特定值提出的 CH 排放因子为 0.49 kg CH/kg BOD,这将允许应用 IPCC 第 2 层方法。这样,AD 好氧处理厂 CH 排放的不确定性将降低。这反过来又将为水部门实施适当的 CH 缓解策略提供重要信息。