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蜂窝煤燃烧氟污染的控制 总被引:1,自引:0,他引:1
以碳酸钙为固氟添加剂,以炉渣及粉煤灰等低氟材料取代全部或部分粘土作为粘结剂来制作蜂窝煤,进行了燃煤降氟的试验研究.结果表明,添加碳酸钙能有效降低蜂窝煤燃烧时候的氟排放,当煤:粘土:CaCO3的质量比为70:17:13时,碳酸钙的固氟效果最佳,氟的排放率可降低64.1%.以炉渣为粘结剂制作蜂窝煤能够显著降低燃烧时向外界排放的氟化物量,当煤:炉渣:CaCO3为80:8:12时,蜂窝煤燃烧排氟量较小且趋于稳定.已拌有一定剂量粉煤灰粘结剂的煤中添加15%的粘土后碳酸钙的固氟效果明显改善,当煤:粘土:粉煤灰:CaCO3为70:15:9:6时固氟效果最佳,此时蜂窝煤氟逸出率仅为18.2%,氟的减排率达到77.9%,显著优于未添加粘土时碳酸钙的固氟效果,蜂窝煤添加碳酸钙固氟剂进行高效固氟时,需同时适当增加粉煤灰加入量,以稳定固氟剂的高温固氟效果. 相似文献
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Under the project of evaluating the health status of the employees of CHEMKO factory (East Slovakia) which produced PCBs between 1955 and 1985, the level of β2-microglobulin (β2-m) was measured in the serum of 242 subjects from CHEMKO (Group A) and two control groups from much less polluted areas: 1. 277 females from a small mountainous village (Group B), 2. 179 adults from the area of a large city of Ko
ice (Group C). The level of thymidine kinase (TK) was measured in the groups A and B only. In addition, age-matched groups of 155 women each from all areas were evaluated. In both the whole group and the age-matched group from CHEMKO the level of β2-m was significantly lower (P<0.001) than that in the respective control groups, while no difference was found in the level of TK. In conclusion, it is suggested that the decrease of β2-m in CHEMKO employees might be related to the immunotoxic effects of organochlorines. 相似文献
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新型复合球填料为沸石与悬浮球填料的有机组合体,密度约为0.92~0.97g/cm3,比表面积为711~1185m2/m3,表面粗糙,物化性能稳定.在曝气量为20∶1,停留时间为6 h时,装有新型复合球填料的反应柱挂膜容易,成膜时间短,膜不易脱落,且生物相丰富.膜成熟时对生活污水中的氨氮和COD都有很好的去除效果,出水氨氮浓度≤2 mg/L,去除率≥93%;出水COD浓度≤22 mg/L,去除率≥80%.新型复合球反应柱在稳定状态处理低浓度的二级出水时,出水氨氮浓度≤2 mg/L,去除率≥89%,出水COD浓度为10~36 mg/L,去除率为48%~81%.出水水质符合GB50335-2002标准. 相似文献
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The degradation of a common textile dye, Reactive-brilliant red X-3B, by several advanced oxidation technologies was studied in an air-saturated aqueous solution. The dye was resistant to the UV illumination (wavelength λ 320 nm), but was decolorized when one of Fe3+, H2O2 and TiO2 components was present. The decolorization rate was observed to be quite different for each system, and the relative order evaluated under comparable conditions followed the order of Fe2+–H2O2–UV Fe2+–H2O2 > Fe3+–H2O2–UV > Fe3+–H2O2 > Fe3+–TiO2–UV > TiO2–UV > Fe3+–UV > TiO2–visible light (λ 450 nm) > H2O2–UV > Fe2+–UV. The mechanism for each process is discussed, and linked together for understanding the observed differences in reactivity. 相似文献
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采用混凝-两级厌氧/缺氧/好氧-膜生物反应器(A3-MBR)处理实际餐厨垃圾发酵废液,通过对运行参数进行优化确定最优工况,并考察其在该条件下长期运行的处理效果。结果表明,混凝预处理的最适pH为8,最佳混凝剂投加量为1 000 mg·L-1。A3-MBR系统在最优运行条件:总HRT为110 h,回流比为200%,进水COD负荷控制在2.3~3.6 g·(L·d)-1下可稳定运行。当系统进水COD、TN、NH3-N和TP浓度分别为(10 984±383)、(335.9±16.2)、(209.1±6.7)和(37.2±2.3)mg·L-1时,系统进水有机负荷为2.3~3.5 g·(L·d)-1,在最优条件下处理系统出水的COD、TN、NH3-N和TP分别为(202±23)、(62.1±7.1)、(0.33±0.13)和(8.3±0.9)mg·L-1,其去除率分别为98.2%、81.5%、99.8%和77.8%。A3-MBR系统对有机物具有良好的去除效果,厌氧段未积累挥发性脂肪酸。最终出水中溶解性有机物主要为II区芳香族蛋白质类似物,残留的挥发性有机物以酯类物质为主。 相似文献
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The present study performed a roadside data analysis to provide baseline data for exploring associations between environmental exposure to four gaseous pollutants and health effects on residents living near roadways. The yearly roadside concentrations of CO and SO2 showed a well-defined decreasing trend, whereas those of NO2 and O3 exhibited the reverse trend. In most cases, the diurnal trends of the roadside concentrations were well-defined for all seasons, plus the daytime concentrations were higher than the nighttime concentrations. In contrast to the other target pollutants, the daytime O3 concentrations observed at the roadside sites were lower than those observed at the residential site, likely due to high-levels of fresh NO from traffic emissions that rapidly react with O3, thereby reducing the O3 roadside level. The Sunday roadside concentrations of CO, NO2, and SO2 were similar to or somewhat lower than the weekday concentrations. Conversely, for O3, the Sunday roadside concentrations were similar to or somewhat higher than the weekday concentrations. The higher O3 concentrations on Sunday may be due to the reduced titration from a decrease in NOx emissions under VOC-limited conditions (low VOC/NOx conditions). The monthly averages of O3 concentrations exhibited the reverse seasonal variation to the other target compounds, with peak O3 concentrations between April and June, and the second peak between August and October. It is also suggested that for O3, the 8-h standard is more stringent than the 1-h standard, while for NO2 and SO2, the 1-h standard is more stringent than the 24-h standard. The multiple regression equations obtained from the relationship between the concentrations and five meteorological parameters indicated that the number and type of meteorological variables in the equations varied according to the pollutant, monitoring station, or season. 相似文献