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951.
采用自制壳聚糖改性聚丙烯无纺布膜为膜组件的A/O-MBR(厌氧/好氧-膜生物反应器)工艺对聚酯工艺废水的处理进行了研究,并与PVDF商品膜性能进行了比较研究。在近70 d的运行中,当进水COD在200~500 mg/L之间,总氮在30~45 mg/L之间波动时,2种平板膜出水水质稳定。出水COD40 mg/L,NH4+-N0.5 mg/L,TN5 mg/L,浊度0.2 NTU,均满足回用水水质要求和最新的辽宁省废水排放标准。实验中考察分析了污泥浓度和COD/TN对总氮去除率的影响。对比2种膜的运行结果,改性聚丙烯无纺布膜的出水水质略好于PVDF商品膜,但过膜压力稍大、膜通量稍小。 相似文献
952.
Spatial and temporal distribution of polycyclic aromatic hydrocarbons (PAHs) in sediments of the Nansi Lake, China 总被引:2,自引:0,他引:2
Hong-Li Li Hong Gao Chen Zhu Guo-Gang Li Fan Yang Zheng-Yu Gong Jun Lian 《Environmental monitoring and assessment》2009,154(1-4):469-478
Polycyclic aromatic hydrocarbons (PAHs) were measured in surface sediments and dated core sediments from the Nansi Lake of China to investigate the spatial and temporal distribution characteristics. The concentrations of 16 kinds priority PAH compounds were determined by GC-MS method. And 210Pb isotope dating method was used to determine the chronological age of the sediment as well as the deposition rate. The results indicated that the total PAHs concentration ranges in surface and core sediment samples were 160 ~32,600 and 137 ~ 693 ng/g (dry wt.), respectively. The sediment rate and the average mass sedimentation were calculated to be 0.330 cm·year???1 and 0.237 g·cm???2·yr???1 and the sediment time of the collected core sample ranged from 1899 to 2000. The peak of PAH concentrations came at recent years. The source analysis showed PAHs mainly came from the contamination of low temperature pyrogenic processes, such as coal combustion. The PAHs concentrations were lower than ERL and LEL values for most collected samples. However, in several surface sediment samples especially in estuary sites, the PAHs concentrations were not only higher than ERL and LEL values, but also higher than ERM values. 相似文献
953.
A green-house study was conducted in late 2005 to investigate the aging behavior of p,p'-DDE in two types of soil, Hydragric Anthrosols (An) and Hydragric Acrisols (Ac), according to the World Reference Base (WRB) [FAO/ISRIC/ISSS. 1998. World reference base for soil resources. World soil resources reports, Rome. p. 87]. Paddy rice and dry rice were grown in submerged paddy soils and non-submerged upland soils, respectively. The concentration of extractable p,p'-DDE in fresh DDE-spiked soils was 746.2ngg(-1). During the first few weeks of the experiment, the extractability of p,p'-DDE became increasingly low as the aging period prolonged. However, certain amount of p,p'-DDE that had been captured by soil minerals and organic matter (OM) could be released and became extractable in the later period. The extractability of p,p'-DDE in submerged soils was significantly lower than that in non-submerged soil, because flooding could increase the binding of pollutants to soil particles. The plantation of both dry rice and paddy rice slowed down the aging process of p,p'-DDE. After one month's growth of rice, p,p'-DDE bound to soil particles was released and became extractable. The OM and silt content of An are higher than that of Ac, resulting in more bound residues and relative lower extractability of p,p'-DDE in An. In addition, the extractability of p,p'-DDE could be reduced by the addition of rice straw to soils. 相似文献
954.
建设世界旅游精品是张家界制定的旅游业发展的战略目标,一流的旅游环境条件是实现这一目标的必备条件。然而,张家界目前的旅游环境与世界旅游精品存在差距,环境管理中存在基础性工作、基础性研究比较薄弱、制度不够健全等方面的问题,影响了环境管理效率。在分析研究张家界环境管理中存在问题的基础上,针对性地提出保护、改善环境的对策,是实现世界旅游精品战略目标的基础工作。 相似文献
955.
956.
957.
华北清洁地区气溶胶特征及其来源研究 总被引:25,自引:3,他引:22
本文用中子活化分析和质子激发X荧光分析法,测定了华北清洁地区气溶胶样品中几十个元素的含量,对粗粒和细粒两种颗粒物进行了平均元素浓度和富集因子的计算。基于对华北地区获得的颗粒物数据以及不同来源气溶胶化学组成的讨论,得出华北清洁地区大气颗粒物的质量浓度要比城市地区小很多,细颗粒物的平均质量浓度比粗颗粒要高,华北清洁地区人为污染元素的粗细比率与城市地区的相比很低,大气污染物主要是由远距离输送来的。 相似文献
958.
This study aims to evaluate the influence of start-up on polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans (PCDD/Fs) concentration in the stack flue gas of incinerators and its contributing PCDD/F emission. The PCDD/F emission of the first sample among three consecutive stack flue gas samples of five intermittent incinerators, which sampled at a stable combustion condition after start-up, is 2-3 times higher than the mean of the others. For verifying the PCDD/F characteristics of incinerators during start-up, one continuous MSWI was investigated for two years. The elevated PCDD/F emissions of the MSWI during start-up could reach 96.9 ng I-TEQN m(-3) and still maintained a high PCDD/F emission (40 times higher than the Taiwan emission limit) even 18 h after the injection of activated carbon, indicating the memory effect. Taking the MSWI for example, which consists of four incinerators, the estimated annual PCDD/F emission from normal operational conditions was 0.112 g I-TEQ. However, one start-up procedure can generate approximately 60% of the PCDD/F emissions for one whole year of normal operations. And the PCDD/F emission, which is the result of the start-ups of four incinerators, was at least two times larger than that of a whole year's normal operations, without consideration for the PCDD/F emission contributed by the long lasting memory effect. 相似文献
959.
960.
Fluidised bed combustor (FBC) is one of the key technologies for sewage sludge incineration. In this paper, a mathematical model is developed for the simulation of a large-scale sewage sludge incineration plant. The model assumes the bed consisting of a fast-gas phase, an emulsion phase and a fuel particle phase with specific consideration for thermally-thick fuel particles. The model further improves over previous works by taking into account throughflow inside the bubbles as well as the floating and random movement of the fuel particles inside the bed. Validation against both previous lab-scale experiments and operational data of a large-scale industrial plant was made. Calculation results indicate that combustion split between the bed and the freeboard can range from 60/40 to 90/10 depending on the fuel particle distribution across the bed height under the specific conditions. The bed performance is heavily affected by the variation in sludge moisture level. The response time to variation in feeding rate is different for different parameters, from 6min for outlet H(2)O, 10min for O(2), to 34min for bed temperature. 相似文献