杭州灰霾天气超细颗粒浓度分布特征

利用快速迁移率粒径谱仪(FMPS)对杭州2013年12月6～11日连续灰霾天气和灰霾消退过程超细颗粒进行监测,分析颗粒物浓度变化和粒径谱分布特征及其与气象的相关性.结果表明,颗粒物日变化特征为夜晚数浓度较高,凌晨数浓度开始降低,08:00和18:00上下班高峰期出现一个小峰值,体现出明显的交通源峰值,表明交通排放对大气污染影响较大.灰霾天气下颗粒物最高数浓度达到8.0×104cm-3.粒径谱呈双峰分布,峰值粒径分别为15 nm和100 nm,粒径在100 nm附近的粒子占大多数,粒子以爱根核模态和积聚模态为主,平均数量中位径CMD(count medium diameter)为85.89 nm.而在灰霾消退过程,颗粒物数浓度降低,峰值粒径向小粒径演变,粒径在100 nm附近的粒子逐渐减少,核模态粒子增多,大于积聚模态,平均CMD为58.64 nm.气象因素中能见度和风力与数浓度主要呈负相关,相关系数R分别为-0.225和-0.229,相对湿度与数浓度正相关,相关系数R为0.271,冬季大气比较稳定,水平温度与数浓度的相关性较小.研究灰霾天气数浓度分布和气象因素的综合影响对其形成机制及控制有重要意义.     

2011年10月珠江三角洲一次区域性空气污染过程特征分析

2011年10月18—25日珠江三角洲地区出现了一次区域性空气污染过程,重污染区域集中在西部,后期向中部转移,PM₁₀为首要污染物.针对本次空气污染过程的研究发现,此次珠江三角洲地区空气污染过程主要受大尺度冷高压活动的影响,一直为下沉气流所控制,500 m以下近地层风速很小,边界层高度较低,存在贴地逆温层,非常不利于污染物的输送和扩散.PM₁₀浓度与风速、能见度呈显著的负相关关系,与温度相关性不显著;且与风速和温度的相关性存在滞后性.稳定天气形势、大范围下沉气流、近地层静小风和贴地逆温是导致这次区域性空气污染过程的气象原因,PM₁₀浓度增加导致珠江三角洲能见度下降.     

阳澄湖浮游植物群落结构与环境因子的典范对应研究

2013年4月（春季）和10月（秋季）对阳澄湖6个点位的浮游植物群落结构进行了调查,共发现浮游植物8门91属184种,其中硅藻门为阳澄湖的主要优势门类,硅藻门中的小环藻属占主要优势种.对六个点位的浮游植物结构组成与9个环境因子的关系进行典范对应分析,结果表明东湖南与中湖北的浮游植物群落结构与其他4个点位差异性较大,pH、高锰酸盐指数、总磷、氨氮、水温是影响浮游植物分布的主要环境因子.     

壳聚糖絮凝机理及絮凝性能的影响因素分析

壳聚糖是一种天然高分子聚合物,被广泛地作为絮凝剂用于水处理过程。探讨了壳聚糖的三种絮凝机理。在水处理中,其絮凝性能的发挥受到pH值、壳聚糖的投加量、壳聚糖的分子量以及壳聚糖的脱乙酰度等因素的影响。     

东莞石马河流域水化学特征时空差异及来源辨析

石马河流域对东江饮用水源地城镇供水具有重要战略意义.为研究石马河水化学特征,分别于2012年2月、6月和11月采集石马河河水水样共39个,分析测定了水体主离子(K+、Na+、Ca2+、Mg2+、Cl-、SO2-4和HCO-3)及营养盐(PO3-4、NO-3和NH+4)浓度,探讨了水化学组成的时空差异、控制因素并对其来源进行了初步辨析.结果表明,水化学组成的时空差异显著,不同时期的河水TDS及营养盐平均浓度排序为11月2月6月;河水阴离子以HCO-3为主,2月和11月时,河水阳离子以Na++K+为主,为HCO-3-Na+水,6月时则以Ca2+为主,为HCO-3-Ca2+水;营养盐浓度在空间上的差异主要受人类活动导致N、P废水排放影响,3个时期的石马河出水口处(R7)N∶P为18.4,有利于浮游植物的生长,河道出现了富营养化的现象;Gibbs图显示,2月和11月的河水主离子受蒸发岩溶解的影响较为显著,而蒸发岩和碳酸盐岩风化共同控制6月的水化学组分;海盐沉降对石马河河水物质的贡献率较小;部分Na+、Mg2+、Cl-和SO2-4来自化肥的施用和工业废水的排放;NH+4-N、PO3-4-P和NO-3-N主要分别来源于家禽养殖废水和生活废水.     

基于多年遥感数据分析长江河口海岸带湿地变化及其驱动因子

研究河口海岸带湿地长时间演变对湿地保护管理和海岸带资源评估具有重要意义.本文获取长江口1979—2015年10景Landsat-MSS/TM/OLI影像和2015年13景GF1-PMS高空间分辨率数据,对比两个典型实验区分类算法,选用最优的决策树算法应用到长江口Landsat影像中,得到沿岸湿地要素近40年的面积变化情况.研究表明,2015年长江河口海岸带湿地总面积为4725 km2,自然湿地占63.5%,人工湿地占21.2%,湿地总面积相比1979年增加了662 km2,自然湿地面积减少了163 km2,而人工湿地面积增加了766 km2.长江口自然湿地面积在1979—2000年减少幅度较大,2000年后由于保护管理加强而减少幅度变小;人工湿地和建筑面积增加较为明显,主要是由于大型水库的修建和人工鱼塘开发及港口建设.湿地总的变化趋势为河口区不断淤积,自然湿地转变为人工湿地,人工湿地转变为建筑用地等非湿地;其中,滩涂面积减少283 km2,水库、养殖鱼塘和水稻田面积分别增加了92、355和319 km2,主要发生在崇明东滩和启东沿岸;非湿地中建筑用地面积增加154 km2,灌木草场面积减少147 km2,主要发生在上海和启东沿岸.同时比较分析长江口3个区域湿地驱动因子发现,北岸启东沿岸和南岸南汇东滩湿地因经济快速发展和港口水利工程修建,以及过度开垦滩涂等自然湿地使人工湿地增加明显;而长江上游径流量、区域降水和海平面上涨等自然因素控制着中支河道区(如崇明东滩)自然湿地的变化.     

建筑安全风险因素分级排序的风险矩阵法

为减少风险分级排序时产生的风险结,在引入施工安全事故频率的基础上,采用单元格细化和Borda序值法改进原有的风险矩阵法。改进后的方法使得风险等级数量增加,风险结数量减少。将该方法应用于脚手架工程的风险因素的分级与排序,风险等级分为6级,且实现了12个因素的明确排序。     

Fatal pedestrian crashes on interstates and other freeways in the United States

Introduction: More than 800 pedestrians die annually in crashes on interstates and other freeways in the United States, but few studies have examined their characteristics. Method: Data from the Fatality Analysis Reporting System on pedestrians fatally injured during 2015–2017 were analyzed. Chi-square tests compared characteristics of pedestrians killed on interstates and other freeways with those that died on other roads, and across crash types among freeway deaths. Land use characteristics of locations where pedestrians were killed while crossing freeways in a large state (California) were identified using Google Earth. Results: A larger proportion of pedestrians killed on freeways died on dark and unlit roads (48% vs. 32%), were male (78% vs. 68%), or were ages 20–44 (55% vs. 32%) compared with pedestrians killed on other roads. Crossing (42%) was the most common crash type among pedestrian deaths on freeways, followed by disabled-vehicle-related crashes (18%). Pedestrians who died while crossing more often had blood alcohol concentrations ≥ 0.08 g/dL (40%) than those in disabled-vehicle-related (22%) or other crashes (34%). Deaths in crossing crashes were more likely than other freeway deaths to occur on urban roads (81%), at speed limits ≤50 mph (13%), or between 18:00 and 23:59 (49%), and 58% of crossing crashes analyzed for land use were located between residential and other (e.g., commercial, recreational) uses. Over a third (37%) of deaths in disabled-vehicle-related crashes occurred at speed limits ≥70 mph. Conclusions: A surprising proportion of pedestrian deaths occur on controlled-access roads not designed for walking. Countermeasures for these crashes need to be implemented to see meaningful reductions in pedestrian fatalities overall. Practical applications: Improving roadway and vehicle lighting, requiring reflective warning devices for marking disabled vehicles, constructing pedestrian overpasses and underpasses in areas frequently crossed, and promoting alternative means of traveling between residential and commercial areas could help.     

基于改进的SPAR-H化工实验室人因可靠性分析

近年来化工实验室事故屡禁不止,其中人的不安全行为是导致事故发生的主要原因.为评估实验人员可靠性,进一步管控化工实验室人的不安全行为,基于标准化工厂人因可靠性分析(SPAR-H)方法,结合化工实验室人因失误的特点,确定了更加适用于化工实验室的人因可靠性分析方法.首先依据"S-O-P"认知模型对人因失误类型进行划分;然后基...     

Monitoring of a Coastal Mediterranean Area: Culturable Bacteria, Phytoplankton, Environmental Factors and their Relationships in the Southern Adriatic Sea

Culturable heterotrophic bacterial and phytoplanktonic densities were investigated at four sites in the Southern Adriatic Sea (Brindisi, S. Cataldo, Otranto and S. M. di Leuca) over an annual cycle. The main phytoplankton groups, the bacterial biodiversity, as well as the faecal contamination indicators were determined. Culturable bacterial numbers averaged 4.8 ± 0.2 log CFU ml⁻¹ whereas phytoplankton numbers averaged 2.1 ± 0.4 log cells ml⁻¹. Relationships between culturable bacteria, phytoplankton and the environmental factors were established. Bacterial and phytoplankton densities usually depended significantly on temperature, dissolved oxygen, phosphate and nitrite only in the S. Cataldo transect. In all the examined transects phytoplankton showed a bloom during the January–February period followed by a bacterial peak during the February–March period. Thus we can suppose that the phytoplankton winter bloom is responsible for the availabily of organic matter for bacterial populations in the following months in this oligotrophic ecosystem.