南京市加油站VOCs排放清单

在分析国内外加油站VOCs排放因子的基础上,结合油气回收进程和排放控制现状,初步建立南京市加油站VOCs排放清单。结果表明：全市加油站VOCs排放因子为168 mg/L,年排放VOCs为300 t。S1+S2、S1+S2+OMS和S1+S2+OMS+VRD 3类加油站的VOCs排放因子分别为335 mg/L、198 mg/L和147 mg/L,OMS和VRD对VOCs排放控制效果显著。     

汽车涂装VOCs减排途径探究

汽车涂装VOCs的大量排放严重污染环境且危害人体健康,需对其排放水平加以控制。根据汽车涂装VOCs的产生环节,从原料替代、工艺改善和VOCs治理方式等方面探究其减排途径,提高治理水平。采用环保型涂料从源头减少VOCs排放,优化涂装工艺、采用高涂着率喷枪,优化喷枪与涂装面角度、雾化压力、涂装面距离等可以提高喷涂效率,减少过量喷涂。就治理方式而言,吸附技术适用于中低浓度需回收的VOCs气体,燃烧技术几乎不产生二次污染物,吸附浓缩+燃烧技术因治理效果好而被广泛应用。     

水泥行业NOx污染防治及减排措施研究

环境污染问题是现代社会面临的一项重要问题。NOx作为大气污染物的重要组成部分之一,我国现行规定水泥行业的NOx排放限值为400mg/Nm^3,这与国际标准之间尚存在较大的差距。近年来,随着社会经济的快速发展,人们对环保的要求也越来越高,因此水泥行业必须要更加开展好NOx污染防治及减排工作。本文主要针对水泥行业NOx污染防治及减排措施进行了研究,希望有助于提升相关工作质量,促进环境保护。     

燃用蔗髓锅炉的硫平衡及二氧化硫排放分析

通过现场监测和调研数据,分析燃用蔗髓锅炉的硫平衡及SO 2排放情况。结果显示,烟气排放的SO 2主要来源于鲜蔗和回用洗布水中含有的硫。8个锅炉硫排放在线监测均值与手工监测均值相对偏差为3.76%~14.9%,表明结果一致性较好。蔗髓硫质量分数为0.01%~0.04%,蔗髓含硫折算后的SO 2值和在线监测SO 2值分别为22.1 mg/m 3~49.9 mg/m 3和43.9 mg/m 3~114.5 mg/m 3,说明鲜蔗和制糖工艺流程的共同影响使得燃用蔗髓锅炉排放烟气SO 2值偏高。     

《涂料、油墨及胶粘剂工业大气污染物排放标准》(GB 37824—2019)解读

简述了我国涂料、油墨及胶粘剂工业的污染排放现状与特征,对《涂料、油墨及胶粘剂工业大气污染物排放标准》(GB 37824—2019)进行了解读。该标准在我国打赢蓝天保卫战三年行动计划的背景下发布实施,从全过程控制的角度构建了大气污染物排放指标体系,明确了以非甲烷总烃(NMHC)和总挥发性有机物(TVOC)为综合表征,与有毒有害特征污染物协调控制的挥发性有机物(VOCs)排放指标体系;提出了涂料、油墨、胶粘剂工业无组织排放控制要求和监测监控要求。指出,涂料、油墨及胶粘剂工业的VOCs控制以无组织排放为主,因此必须从源头减排入手,强化全过程控制和全生命周期控制,环境与安全协同,逐步实现行业可持续发展。     

Agricultural ammonia emissions inventory and spatial distribution in the North China Plain

An agricultural ammonia (NH₃) emission inventory in the North China Plain (NCP) on a prefecture level for the year 2004, and a 5 × 5 km² resolution spatial distribution map, has been calculated for the first time. The census database from China's statistics datasets, and emission factors re-calculated by the RAINS model supported total emissions of 3071 kt NH₃-N yr⁻¹ for the NCP, accounting for 27% of the total emissions in China. NH₃ emission from mineral fertilizer application contributed 1620 kt NH₃-N yr⁻¹, 54% of the total emission, while livestock emissions accounted for the remaining 46% of the total emissions, including 7%, 27%, 7% and 5% from cattle, pigs, sheep and goats, and poultry, respectively. A high-resolution spatial NH₃ emissions map was developed based on 1 × 1 km land use database and aggregated to a 5 × 5 km grid resolution. The highest emission density value was 198 kg N ha⁻¹ yr⁻¹.     

长江经济带碳排放现状及未来碳减排

长江经济带是我国"三大支撑带"之一,其碳减排目标实现对我国生态文明建设具有重要意义。采用2005~2013年长江经济带(含9省2市)的能源消耗与经济社会数据,通过数理统计,得出各地历年碳排放量、人均碳排放、能源强度、产业结构多元水平的具体数值及变化率,结合运用弹性计算和矩阵分类法,发现长江经济带碳排放存在空间与结构差异。研究结果显示:(1)长江经济带碳排放及增长率、人均碳排放及增长率、能源强度都高于全国平均水平,能源强度下降率低于全国平均水平;把长江经济带分为东中西三段区域,碳排放总量、人均碳排放及能源强度下降率梯度下降,碳排放增长率、人均碳排放增长率、能源强度梯度上升。(2)工业化开始越早、重工业化主导向生产性服务业主导转变越快、越充分地区,经济低碳化水平越高;通过提升产业结构多元化速度有利于碳减排。(3)长江经济带各地实现碳减排措施应有不同,东段地区应着重降低人均碳排放,中西段地区应着重于降低能源强度。(4)未来碳减排应兼顾公平与效率,各地区碳减排目标分配应结合各地支付能力、碳汇能力、生产效率、能源结构等因素来安排。     

Characteristics of chlorofluorocarbons (CFCs) emitted from a municipal waste treatment facility

The emission concentrations of several chlorofluorocarbons (CFCs) were measured from a municipal waste treatment facility (located in Seoul, Republic of Korea) to investigate the emission characteristics of CFCs in the urban environment. To this end, a total of five CFCs (CFC-10, CFC-11, CFC-20, CFC-30, and CFC-113) were analyzed by the thermal desorption-gas chromatography-mass spectrometry (TD-GC-MS) method. The results of this study indicate that the formation of CFC-11 (8.21 ± 1.68 ppb in spring) and CFC-20 (3.92 ± 3.93 ppb in spring) proceeded very actively within the facility. Moreover, CFC-113 was also found in relatively high concentrations (3.34 ± 1.31 ppb in spring) in the treatment facility. Unlike other CFCs, CFC-10 was observed mainly at ambient (and reference) locations and one point inside the treatment facility. In conclusion, emissions of some important CFCs are a prominent process, as they were measured either frequently or abundantly both in winter and spring. It is further indicated that certain CFCs (like CFC-11 and CFC-30) are subject to highly significant seasonal variations.     

Vertical emission profiles for Europe based on plume rise calculations

The vertical allocation of emissions has a major impact on results of Chemistry Transport Models. However, in Europe it is still common to use fixed vertical profiles based on rough estimates to determine the emission height of point sources. This publication introduces a set of new vertical profiles for the use in chemistry transport modeling that were created from hourly gridded emissions calculated by the SMOKE for Europe emission model. SMOKE uses plume rise calculations to determine effective emission heights. Out of more than 40 000 different vertical emission profiles 73 have been chosen by means of hierarchical cluster analysis. These profiles show large differences to those currently used in many emission models. Emissions from combustion processes are released in much lower altitudes while those from production processes are allocated to higher altitudes. The profiles have a high temporal and spatial variability which is not represented by currently used profiles.     

Contamination and emission factors of PCDD/Fs, unintentional PCBs, HxCBz, PeCBz and polychlorophenols in chloranil in China

The production of chloranil is regarded as a potentially significant source of unintentional POPs. This research aimed to identify the contamination levels of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), polychlorinated biphenyls (PCBs), hexachlorobenzene (HxCBz), pentachlorobenzene (PeCBz) and polychlorophenols in chloranil samples and identify the formation pathways. The toxicity equivalent (TEQ) values for PCDD/Fs in the chloranil samples ranged from 163 to 1 540 200 pg I-TEQ g⁻¹, while the PCB TEQ values ranged from 1.9 to 3.3 pg WHO-TEQ g⁻¹. High levels of HxCBz, PeCBz and polychlorophenols were also detected in the chloranil samples. The average emission factors were 522.2 mg I-TEQ t⁻¹ (PCDD/Fs), 0.0026 mg WHO-TEQ t⁻¹ (PCBs), 32.6 mg t⁻¹ (HxCBz), and 136.6 mg t⁻¹ (PeCBz). The PCDD/Fs and PCBs are thought to be formed from the polychlorophenols and polychlorobenzenes generated during the chloranil production process. Purification of the chloranil products can reduce the unintentional POPs releases and protect the environment.