超临界CO2和液态CO2及气态N2注入采空区防灭火性能实验

为对比研究超临界态CO_2、液态CO_2和气态N_2注入采空区的防灭火性能,自主研制了模拟采空区残煤自燃过程实验系统,开展了超临界态CO_2、液态CO_2和气态N_2注入采空区防灭火实验。实验结果表明:12 MPa、39℃超临界态CO_2对采空区自燃残煤的降氧降温能力优于6 MPa、30℃液态CO_2优于6 MPa、39℃气态N_2;12 MPa、39℃超临界态CO_2对残煤的降温能力是6 MPa、30℃液态CO_2的1.7倍,是6 MPa、39℃气态N_2的10倍,对采空区的降温能力是液态CO_2的2倍,为气态N_2的8倍;12 MPa、39℃超临界CO_2对采空区的降氧速率比6 MPa、30℃液态CO_2和6 MPa、39℃气态N_2高12.5%;12 MPa、39℃超临界CO_2的降温能力是8 MPa、39℃超临界CO_2的1.7倍,因此适当提高超临界态CO_2的注入压力,防灭火性能更佳。     

华南地区春季酸沉降区域源解析

应用IDNN区域源解析模式,处理了1986年2—8月间华南地区观测的酸雨样品,识别了春季广东、广西地区酸雨区域漂,结果得到,80％以上H⁺、50％SO₄^2-和60％NO₃^-来源于南岭以北地区。     

Distribution of organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs) in surface water and sediments from Baiyangdian Lake in North China

Persistent organochlorine compounds, including hexachlorocyclohexanes (HCHs), dichlorodiphenyltrichloroethanes (DDTs) and polychlorinated biphenyls (PCBs) were analyzed in surface water and sediments from Baiyangdian Lake, North China. Total concentrations of HCHs, DDTs and PCBs in surface water were in the range of 3.13-10.60, 4.05-20.59 and 19.46-131.62 ng/L, respectively, and total concentrations of HCHs, DDTs and PCBs in sediments were 1.75-5.70, 0.91-6.48 and 5.96-29.61 ng/g dry weight, respectively. Among the groups of HCHs (sum of α-HCH, β-HCH, γ-HCH and δ-HCH) and DDTs (sum of DDT, DDD and DDE), the predominance of β-HCH, DDE and DDD in water and sediment samples was clearly observed. This observation suggested that β-HCH was resistant to biodegradation and the DDTs had been transformed to its metabolites, DDE and DDD. For PCBs, penta-, hexa- and hepta-chlorinated congeners were the most abundant compounds in the both phases. Furthermore, the partitioning of chlorinated compounds between sediment and water was investigated to understand their transport and fates in aquatic ecosystems. The results indicated that average logs of organic carbon-normalized sediment-water partition coefficients (logK_oc') for OCPs varied between 3.20 and 5.53, and for PCBs, logK_oc' values ranged from 3.19 to 5.57. The observed logK_oc' was lower than their equilibrium logK_oc predicted from linear model, which may be attributed to the solubility enhancement effect of colloidal matter in water phase and the disequilibrium between sediment and water.     

2021年沙尘天气影响下江苏省空气质量特征分析

对2021年影响江苏省的沙尘天气过程开展研究,分析受影响的时间、区域特征及环境空气质量特征。结果表明,影响江苏省的沙尘天气过程共计13次,全省累计受影响229 d。从时间分布看,沙尘天气过程多发生在1月、3—5月,2月、11月较少,6—10月和12月无沙尘天气过程。从区域分布看,苏北地区受沙尘天气过程影响较显著,受影响天数>20 d的城市均分布于此。受沙尘天气过程影响,且东北偏北风或东北风输送时,可吸入颗粒物(PM₁₀)和细颗粒物(PM_2.5)较易出现小时高值。沙尘过程造成PM₁₀日均质量浓度超标的天数占比为38.0%,造成PM_2.5日均质量浓度超标的天数占比仅为12.7%;扣除沙尘天气过程影响后,PM_2.5和PM₁₀年均质量浓度分别较扣除前下降1和6μg/m³,沙尘天气过程对PM₁₀质量浓度的影响大于对PM_2.5质量浓度的影响。受沙尘天气过程影响时,环境空气质量为轻度污染及以上级别占...     

电增强载铝活性炭纤维吸附除氟的效果与影响因素

以含氟地下水为研究对象,采用自制电促吸附除氟反应器,开展电增强载铝活性炭纤维吸附除氟的动态实验,研究了不同电压、极板间距、地下水碱度和流速对吸附除氟效果的影响。实验结果表明,在负载炭纤维毡的电极一端加正电,可以提高除氟效果。当电压为1.6 V时除氟效果较好,单位面积炭毡处理达标水量为56.7 L/m2;极板间距设置为4mm时电吸附反应器除氟效果最佳;通过调节pH改变地下水碱度,当地下水pH调节为5.5时,电吸附反应器除氟效果较未调节前提高50%;当采用3对电极板,流速为1.88 m/h时,达到最高表面处理负荷2 073.6 L/(m2.d);探究了反应器的反洗再生方式,并连续进行了吸附再生的动态实验;穿透的反应器以Al2(SO4)3溶液为再生液并采用反向加电1.6 V的方式,可以达到较好的再生效果,实现连续动态运行。     

长三角地区2017～2020年臭氧浓度时空分布与人群健康效益评估

近年来,我国臭氧(O₃)浓度呈升高趋势,成为仅次于PM_2.5影响空气质量的重要因素.为掌握长三角地区蓝天保卫战实施期间O₃时空变化特征和人群健康影响,采用莫兰指数和冷热点空间统计方法分析了长三角地区2017～2020年210个监测站点O₃浓度时空特征,并利用健康风险和环境价值评价法评估了长三角区域人群O₃暴露水平变化的健康收益.结果表明,2017～2020年,长三角地区O₃年均值和暖季均值的四分位数范围(IQR)呈现从高浓度向低浓度位移的趋势.暖季和冷季O₃浓度均值均呈现北高南低的空间分布态势.暖季O₃浓度均值在长三角北部和中部腹地城市出现高浓度O₃集聚的特征.区域O₃年均暴露浓度超过160μg·m^-3及以上的人口比例由2017年的72.3%降低至2020年的34.8%.三省一市人口加权年均O₃暴露浓度总体呈现下降趋势,但长三...     

石化炼制企业噪声治理探讨

文章通过对石油化工炼制企业噪声的分析,相对不同场所噪声源进行不同治理方案的探讨,就某石化公司典型装置蒸馏装置为例进行噪声源及相应的治理方案分析,选择在临厂界处建设隔声屏障,对声源进行有效的阻隔,监测结果表明:隔声屏障起到了有效的隔声降噪作用,厂界噪声达GB 12348-2008《工业企业厂界环境噪声排放标准》。     

Characterization of aircraft emissions and air quality impacts of an international airport

Beijing Capital International Airport(ZBAA) is the world's second busiest airport. In this study, the emissions of air pollutants from aircraft and other sources at ZBAA in 2015 were estimated using an improved method, which considered the mixing layer height calculated based on aircraft meteorological data relay(AMDAR), instead of using the height(915 m)recommended by ICAO. The yearly emissions of NO_x, CO, VOCs, SO_2, and PM_(2.5) at the airport were 8.76 × 10~3, 4.43 × 10~3, 5.43 × 10~2, 4.80 × 10~2, and 1.49 × 10~2 ton/year, respectively. The spatial–temporal distribution of aircraft emissions was systematically analyzed to understand the emission characteristics of aircraft. The results indicated that NOxwas mainly emitted during the take-off and climb phases, accounting for 20.5% and 55.5% of the total emissions. CO and HC were mainly emitted during the taxi phase, accounting for 91.6%and 92.2% of the total emissions. Because the mixing layer height was high in summer, the emissions of aircraft were at the highest level throughout the year. Based on the detailed emissions inventory, four seasons simulation using WRF-CMAQ model was performed over the domain surrounding the airport. The results indicated that the contribution to PM_(2.5) was relatively high in winter; the average impact was about 1.15 μg/m~3 within a radius of1 km around the airport. Meanwhile, the near surroundings and southwest areas of the airport are the most sensitive to PM_(2.5).     

Bio-remediation of acephate–Pb(II) compound contaminants by Bacillus subtilis FZUL-33

Removal of Pb~(2+)and biodegradation of organophosphorus have been both widely investigated respectively. However, bio-remediation of both Pb~(2+)and organophosphorus still remains largely unexplored. Bacillus subtilis FZUL-33, which was isolated from the sediment of a lake, possesses the capability for both biomineralization of Pb~(2+)and biodegradation of acephate. In the present study, both Pb~(2+)and acephate were simultaneously removed via biodegradation and biomineralization in aqueous solutions.Batch experiments were conducted to study the influence of p H, interaction time and Pb~(2+)concentration on the process of removal of Pb2+. At the temperature of 25°C, the maximum removal of Pb~(2+)by B. subtilis FZUL-33 was 381.31 ± 11.46 mg/g under the conditions of p H 5.5, initial Pb~(2+)concentration of 1300 mg/L, and contact time of 10 min. Batch experiments were conducted to study the influence of acephate on removal of Pb~(2+)and the influence of Pb2+on biodegradation of acephate by B. subtilis FZUL-33. In the mixed system of acephate–Pb2+, the results show that biodegradation of acephate by B. subtilis FZUL-33 released PO43+, which promotes mineralization of Pb2+. The process of biodegradation of acephate was affected slightly when the concentration of Pb2+was below 100 mg/L. Based on the results, it can be inferred that the B. subtilis FZUL-33 plays a significant role in bio-remediation of organophosphorus-heavy metal compound contamination.     

A simulation study of mercury release fluxes from soils in wet-dry rotation environment

A simulative mesocosm study was conducted to evaluate the influence of wet-dry rotation on mercury（Hg） flux from soil/water to air and the distribution of Hg species in water as well as Hg chemical fractions in soil. Three types of soil were employed including two kinds of paddy soil, Typic Purpli-Udic Cambosols（TPUC） and Xanthi-Udic Ferralosols（XUF）, as well as the Alluvial Soil（AS） from Three Gorge reservoir area in Chongqing, China. The results showed that Hg fluxes in wetting periods were significantly higher than that in drying periods. It might be due to the formation of a layer of stable air over the water surface in which some redox reactions promote evasion processes over the water surface. This result indicated that more Hg would be evaporated from the Three Gorge reservoir and paddy soil field during the flooding season. Hg fluxes were positively correlated with air temperature and solar irradiation, while negatively correlated with air humidity and the electronic conductivity of water. Hg fluxes from AS and TPUC were significantly higher than that from XUF, which might be due to the higher organic matter（OM） contents in XUF than TPUC and AS. The reduction processes of oxidized Hg were restrained due to the strong binding of Hg to OM, resulting in the decrease in Hg flux from the soil.