长三角经济增长与碳排放异速关系及形成机制

低碳经济是长三角高质量一体化发展的内在要求。针对2000—2017年长三角地区经济增长与碳排放时空关联、异速增长关系及影响因素的研究发现：（1）长三角地区经济增长与碳排放具有正向关联,关联强度总体呈“V”型波动变化。2000—2008年高关联强度区相对集中分布于苏南、苏北及浙中等地区,2009—2017年空间关联强度明显下降,大体呈“南低北高”分布。（2）长三角地区经济增长与碳排放异速变化以经济扩张弱型为主,大部分地区经济增长与碳排放异速关系实现由正转负。（3）地理探测器诊断第二产业比例、第三产业比例、城市化和人口密度是驱动长三角地区经济增长与碳排放异速变动的主要因子。（4）多尺度地理加权回归表明人口密度显著负向影响长三角地区经济增长与碳排放异速变化,投资强度和财政支出强度起到抑制作用,城市化和消费水平表现出先促进后抵消作用,第二产业与第三产业占比及固碳水平则起到先抑制后促进作用。     

Secondary organic aerosol formation from straw burning using an oxidation flow reactor

Herein, we use an oxidation flow reactor, Gothenburg: Potential Aerosol Mass (Go: PAM) reactor, to investigate the secondary organic aerosol (SOA) formation from wheat straw burning. Biomass burning emissions are exposed to high concentrations of hydroxyl radicals (OH) to simulate processes equivalent to atmospheric oxidation of 0-2.55 days. Primary volatile organic compounds (VOCs) were investigated, and particles were measured before and after the Go: PAM reactor. The influence of water content (i.e. 5% and 11%) in wheat straw was also explored. Two burning stages, the flaming stage, and non-flaming stages, were identified. Primary particle emission factors (EFs) at a water content of 11% (∼3.89 g/kg-fuel) are significantly higher than those at a water content of 5% (∼2.26 g/kg-fuel) during the flaming stage. However, the water content showed no significant influence at the non-flaming stage. EFs of aromatics at a non-flaming stage (321.8±46.2 mg/kg-fuel) are larger than that at a flaming stage (130.9±37.1 mg/kg-fuel). The OA enhancement ratios increased with the increase in OH exposure at first and decreased with the additional increment of OH exposure. The maximum OA enhancement ratio is ∼12 during the non-flaming stages, which is much higher than ∼ 1.7 during the flaming stages. The mass spectrum of the primary wheat burning organic aerosols closely resembles that of resolved biomass burning organic aerosols (BBOA) based on measurements in ambient air. Our results show that large gap (∼60%-90%) still remains to estimate biomass burning SOA if only the oxidation of VOCs were included.     

改性颗粒活性炭对水中溴酸根的吸附特性研究

采用阳离子表面活性剂氯化十六烷基吡啶(CPC)改性颗粒活性炭以提高活性炭对溴酸根的吸附能力.通过小试研究了改性颗粒活性炭(GAC-CPC)对溴酸根的吸附特性,考察了BrO-3初始浓度、pH、共存阴离子等因素对吸附过程的影响.结果表明,CPC改性能显著提高GAC对BrO-3的吸附能力,吸附量随着初始浓度升高而增大;在碱性条件下GAC-CPC对BrO-3的吸附量减小;共存阴离子与BrO-3在GAC-CPC上存在竞争吸附,其影响顺序为:NO-3SO2-4PO3-4CO2-3.用准一级、准二级和颗粒内扩散动力学模型拟合GAC-CPC吸附BrO-3的动力学过程,结果表明,准二级动力学能更好的描述吸附过程,且孔扩散可能是改性GAC吸附BrO-3初始阶段的主要速率控制因素.用Langmuir和Freundlich等温吸附模型拟合不同温度下BrO-3的吸附平衡过程,结果表明,Langmuir等温吸附模型能很好的描述吸附平衡过程,GAC-CPC吸附BrO-3的过程是自发且放热的,温度升高不利于吸附.     

臭氧污染对不同品种小麦干物质与生物量碳积累与分配的影响

近地层臭氧(O3)污染对陆地生态系统及植物生长的危害备受关注.本研究利用开放式臭氧污染(Free-air O3concentration enrichment,O3FACE)研究平台,研究了大气O3浓度增加(比周围大气高50%)对长江三角洲地区5个冬小麦(Tritcium aestivum L.)品种(扬麦15、扬麦16、烟农19、扬幅麦2号和嘉兴002)的干物质与生物量碳的积累与分配以及作物残体C/N比的影响.结果表明,不同品种小麦的干物质积累和分配对O3升高的响应差异明显;O3升高具有降低扬麦15、嘉兴002和增加扬幅麦2号总生物量的趋势,但对扬麦16和烟农19几乎无影响,其中嘉兴002达到显著水平.O3升高显著增加了扬麦15、嘉兴002和显著降低了烟农19和扬幅麦2号的根/冠比,而对品种扬麦16无影响,导致干物质在地上和地下分配呈现品种差异.高O3环境下扬麦15、扬麦16和嘉兴002穗重降低,而烟农19和扬幅麦2号无明显变化;小麦籽粒占穗的比重在高O3条件下嘉兴002、烟农19和扬幅麦2号显著降低8.2%～15.5%,扬麦15呈增加趋势而扬麦16变化不大;表明O3升高将致嘉兴002、烟农19、扬幅麦2号和扬麦16不同程度减产.O3升高导致烟农19和扬幅麦2号秸秆碳量显著增加14.1%～22.9%和C/N比显著降低10.9%～29.1%,JX002秸秆碳量显著减少和C/N比显著增加,扬麦16和扬麦15的秸秆碳量与C/N比则分别呈增加和降低趋势.O3升高显著降低了扬麦16、烟农19和扬幅麦2号品种的根茬碳量和C/N比,对嘉兴002的根茬碳量无显著影响却显著降低了C/N比,但对扬麦15根茬碳数量与质量均影响不大.评价小麦干物质的形成与分配、根茬和秸秆固碳的质与量对O3污染的响应需考虑品种差异影响.     

黄冈市大气挥发性有机物污染特征、来源及对臭氧生成的影响

基于黄冈市城区大气挥发性有机物（VOCs）离线采样数据和常规空气污染物、气象在线监测数据,分析了黄冈市大气VOC组分和体积分数特征,并利用正交矩阵因子分解（PMF）模型和耦合MCM机制的光化学反应箱式模型（PBM-MCM）分别分析了臭氧（O₃）污染高发期VOCs的来源及臭氧生成敏感性.结果表明,φ（TVOCs）平均值为（21.57±3.13）×10^-9,且呈现出冬春高、夏秋低的季节性特征,其中烷烃（49.9%）和烯烃（16.4%）的占比最大.PMF解析结果显示黄冈市大气VOCs主要来源为：燃料燃烧源（27.8%）、机动车排放源（19.9%）、溶剂使用源（15.7%）、工业卤代烃排放源（12.1%）、化工企业排放源（10.5%）、自然源（7.8%）和柴油车排放源（6.2%）.在人为源中,溶剂使用、燃料燃烧和化工企业排放的VOCs对大气环境中O₃生成的贡献较大,贡献了O₃生成的60.9%,故对O₃污染防控应优先管控这3种人为源.通过相对增量反应性（RIR）和经验动力学方法（EKMA）曲线分析,观测期间黄冈市O₃生成处于VOCs控制区,且间/对-二甲苯、乙烯、1-丁烯和甲苯等VOCs对O₃生成比较敏感,应重点削减以上VOCs的排放.     

淄博市城区臭氧超标期间的VOCs污染特征与来源解析

近年来,我国城市的臭氧（O₃）污染问题日益突出.挥发性有机物（VOCs）是O₃生成的重要前体物,因此,了解VOCs主要特征以及来源对控制O₃污染具有重要意义.于2019年5～9月在淄博市开展了在线VOCs观测,共计监测56个物种.观测期间,O₃超标率为67.8%,ρ（VOCs）平均值为140.71μg·m^-3,O₃超标日的VOCs浓度为非超标日的1.04倍.从VOCs组分结构上看,浓度从高到低依次为：芳香烃>烷烃>烯烃>炔烃.其中1,3,5-三甲苯、邻-乙基甲苯、 1-丁烯和正己烷为超标日和非超标日排放较高的物种.臭氧生成潜势（OFP）中芳香烃和烯烃贡献较大.由PMF源解析结果得出,该城区VOCs来源主要包括机动车源、固定燃烧源、溶剂使用源、工艺过程源和天然植物源,其中机动车源为该城区最主要的VOCs来源.此外,O₃超标日的机动车源占比为32.3%,固定燃烧源占比为24.2%,相比于非超标日分别升高了3.3%和6.9...     

浅谈防止海上油田地质性溢油的几个因素

油田在注水开发过程中由于注水工艺不完善、注水水质不达标、注采比不合理、井控措施无效等因素会导致地质性溢油事故的发生。文章主要针对注水性油田在开发过程中可能会导致地质性溢油的几个关键因素进行探讨,为注水性油田开发风险防范和环境保护提供参考。     

Trihalomethane formation potential of organic fractions in secondary effluent

Organic matter is known to be the precursor of numerous chlorination by-products. Organic matter in the secondary e uent from the Wenchang Wastewater Treatment Plant (Harbin, China) was physically separated into the following fractions: particulate organic carbon (1.2–0.45 m), colloidal organic carbon (0.45–0.1 m), fine colloidal organic carbon (0.1–0.025 m), and dissolved organic carbon (DOC) (< 0.025 m). Moreover, < 0.45 m fraction was chemically separated into hydrophobic acid (HPO-A), hydrophobic neutral (HPO-N), transphilic acid (TPI-A), transphilic neutral (TPI-N), and hydrophilic fraction (HPI). The chlorine reactivity of these organic fractions obtained from both size and XAD fractionations were evaluated. The structural and chemical compositions of the HPO-A, HPO-N, TPI-A, and TPI-N isolates were characterized using elemental analysis (C, H, O, and N), Fourier transform infrared spectroscopy (FT-IR), and proton nuclear magnetic resonance spectroscopy (1H-NMR). Results showed that DOC was dominant in terms of total concentration and trihalomethane formation potential (THMFP), and there was no statistical di erence in both specific THMFP (STHMFP) and specific ultraviolet light absorbance among the 0.45, 0.1, and 0.025 m filtrates. HPO-A had the highest STHMFP compared to other chemical fractions. HPO-A, HPO-N, TPI-A, and TPI-N contained 3.02%–3.52% of nitrogen. The molar ratio of H/C increased in the order of HPO-A < HPO-N < TPI-A < TPI-N. The O/C ratio was relatively high for TPI-N as compared to those for the other fractions. 1H-NMR analysis of the four fractions indicated that the relative content of aromatic protons in HPO-A was significantly higher than those in the others. The ratio of aliphatic to aromatic protons increased in the order of HPO-A < HPO-N < TPI-A < TPI-N. FT-IR analysis of the four fractions showed that HPO-A had greater aromatic C==C content whereas HPO-N, TPI-A, and TPI-N had greater aliphatic C–H content. TPI-N contained more oxygen-containing functional groups than the other fractions.     

“自由落体”游乐设备直流电机故障分析

创新是大型游乐设施占领市场的核心竞争力,但创新也容易引发各类问题及不确定性,特别是涉及游乐设备可维护性方面,更容易在创新过程中忽视。本文以国外设备供应商生产的“自由落体”游乐设备的故障入手,从研究直流电机故障机理、维修方案以及设计维保建议等几个方面,提出提升直流电机可维护性的举措,主张行业的设计人员不但要聚焦大型游乐设施的趣味性,也要更多关注如何提高大型游乐设施的可靠性、可维护性。     

Characteristics of typical dissolved black carbons and their influence on the formation of disinfection by-products in chlor(am)ination

● The physicochemical and structural properties of DBC were characterized. ● The effects of DBC on DBPs and DBPFP generation during disinfection were evaluated. ● The DBPs and DBPFP generation during chlor(am)ination were compared. Dissolved black carbon (DBC) released from biochar can be one of the potential disinfection by-products (DBPs) precursors in the dissolved organic matter pool. However, the physiochemical and structural properties of DBC and the effects on the development of DBPs and DBP formation potential (DBPFP) during the disinfection process remain unclear. In this study, the characteristics of two kinds of DBC, namely, animal-derived DBC (poultry litter DBC, PL-DBC) and plant-derived DBC (wheat straw DBC, WS-DBC), were investigated. The effects of different kinds of DBC on the evolution of DBPs and DBPFP in chlorine and chloramine disinfection processes were compared with natural organic matter (NOM). The results showed that the total DBPs concentrations derived from PL-DBC, WS-DBC and NOM were similar during chlorination (i.e., 61.23 μg/L, 64.59 μg/L and 64.66 μg/L, respectively) and chloramination (i.e., 44.63 μg/L, 44.42 μg/L and 45.58 μg/L, respectively). The lower total DBPs and DBPFP concentrations in chloramination could be attributed to the fact that the introduction of ammonia in chloramine inhibited the breaking of the bond between the disinfectant and the active group of the precursor. Additionally, DBC presented much lower total DBPFP concentrations than NOM in both chlorination and chloramination. However, both kinds of DBC tended to form more monochloroacetic acids and haloacetamides than NOM, which could result from the higher organic strength, higher protein matter, and nitrogen-rich soluble microbial products of DBC.