互花米草厌氧消化产沼气的实验研究

为探索入侵物种互花米草厌氧生物处理的可行性,研究了互花米草中温批式厌氧发酵的产气特性和物质转化过程.结果表明,互花米草的产气率随VS负荷的增加呈现先增加后降低的趋势,当VS浓度为6.0%时,产气效果最好,产气量为294.84mL/g VS.发酵过程中,有机酸先增加后降低,pH值与有机酸呈极显著的负相关(R=-0.97508),该发酵过程为丁酸型发酵.互花米草中的维管束、薄壁细胞以及纹孔,有利于其进行厌氧生物处理, 发酵后的互花米草外观变得毛糙,出现了很多丝状物,维管束结构破坏严重,皮层和薄壁细胞不易被厌氧微生物破坏.FTIR和XRD结果显示,厌氧微生物不但利用互花米草中的易分解有机物,对纤维素的结晶区也有一定的破坏,发酵后的互花米草木质素相对含量增加.     

Regional-specific emission inventory for NH3, N2O, and CH4 via animal farming in South, Southeast, and East Asia

Ammonia, nitrous oxide, and methane emission from animal farming of South, Southeast, and East Asia, in 2000, was estimated at about 4.7 Tg NH₃–N, 0.51 Tg N₂O–N, and 29.9 Tg CH₄, respectively, using the FAO database and countries’ statistic databases as activity data, and emission factors taking account of regional characteristics. Most of these atmospheric components, up to 60–80%, were produced in China and India. Pakistan, Bangladesh, and Indonesia, which were large source countries next to China and India, contributed more than a few percent of total emission of each atmospheric component. The largest emission livestock were cattle whose contribution was considerably high in South, Southeast, and East Asia; more than one-fourth of ammonia and nitrous oxide emissions: more than half of methane emission. The other major livestock for nitrous oxide and ammonia emissions were pigs. For methane emission, buffaloes were second source livestock. To provide spatial distributions of these gases, the emissions of county and district level were allocated into each 0.5° grid by means of the weighting by high-resolution land cover datasets. The regions with considerable high emissions of all components were able to be found at the Ganges delta and the Yellow River basin. The spatial distributions for ammonia and nitrous oxide emissions were similar but had a substantial difference from methane distribution.     

A modified steady-state model for evaluation of ammonia concentrations behind a water curtain

Water curtain system has been proved an effective mitigation measurement for ammonia spill dispersion. Calculating of ammonia cloud concentration with water curtain was less studied. This paper presents a steady-state calculation model to calculate open and forced ammonia spill dispersion. The formula of ammonia absorption was built and integrated into the calculation model. The calculated downwind ammonia concentrations for open and forced spill dispersion were reproduced and compared with literature using a statistical method. In addition, the relationship between ammonia concentration in water droplet and the droplet diameter was studied. The results display that the formula of ammonia absorption is suitable for calculating mass transfer process between the ammonia cloud and the water curtain. The calculation model presents good performances for open and forced ammonia spill dispersion. This study indicates that the calculation model can be satisfactory in determining the impact of open and forced ammonia spill dispersion and the design of water curtain mitigation system.     

光导纤维氨气敏荧光传感器的研制和应用

以大环冠醚为铵离子中性载体，吖啶橙为荧光ＰＨ指示剂，二者结合于增塑的ＰＶＣ膜中，样品氨浓度变化直接引起膜的荧光强度变化。基于该原理研制成不需内电解质溶液的光导纤维氨气敏荧光传感器。用以测定生活污水的氨氮，精密度实验的平均变异系数为０．９－１．３％；回收率为９５．４％－１０５．６％。     

Conversion of organic carbon in the decomposable organic wastes in anaerobic lysimeters under different temperatures

The quantitative fractions of conversion of organic carbon in the decomposable organic wastes with initial moisture of 70% sorted from municipal solid wastes(MSW)in lysimeters into biogas,leachate and solid residue were characterized,under temperatures of 25,30 and 41℃,respectively,and circulation of leachate generated within the lysimeters.It is found that 27% of organic carbon in the wastes are conversed into gases,0.8% into leachate,and the other 72% remained in the decomposable solid residues,after 180 days‘ degradation at 41℃. Higher temperature will lead to monr rapid degradation and result to higher conversion of the organic carbon to biogas and lower to boty solid residues and leachate,while the pollutant concentrations in leachate will be lower at a higher temperature and values of COD are quite consistent with TOC.     

A／O生物转盘工艺处理氨氮废水

研究了A/O系统后接生物转盘工艺，对低CODcr和高氨氮的石化厂废水的处理效果。结果表明，当碳氮比为3.8时，对CODcr和氨氮均有良好的去除效果，在进水CODcr浓度为1048.70/mg/L、氨氮浓度为275.16mg/L时，CODcr去除率达93.26%，氨氮去除率达94.7%.     

Conversion of organic carbon in the decomposable organic wastes in anaerobic lysimeters under different temperatures

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壳聚糖三元接枝高分子絮凝剂对垃圾渗滤液生化处理出水的絮凝研究

采用壳聚糖三元接枝高分子絮凝剂(CAS)与聚合氯化铝(PAC)、磷酸镁铵沉淀法(MAP法)复配处理中山市老虎坑垃圾渗滤液生化处理出水.絮体粒径分布测试、絮体形态结构分析和Zata电位测定结果表明,CAS与PAC复配,可充分发挥CAS架桥和PAC电荷中和的协同作用,强化混凝过程,使细小的凝聚体形成体积庞大的絮状沉淀物,并在沉降过程中,网捕水体中的胶体颗粒,显著提高混凝效果.CAS和PAC的投加对NH4 -N脱氮的贡献甚微.采用MAP法与CAS、PAC复配,当投加量分别为50mg/LCAS、500 mg/LPAC、856 mg/LMgCl2·6H2O、1509 mg/LNa2HPO4·12H2O时,出水COD、色度分别小于300 mg/L、30倍,NH4 -N降至2 mg/L左右.     

Estimating the Effect of Protected Lands on the Development and Conservation of Their Surroundings

Abstract:  The fate of private lands is widely seen as key to the fate of biodiversity in much of the world. Organizations that work to protect biodiversity on private lands often hope that conservation actions on one piece of land will leverage the actions of surrounding landowners. Few researchers have, however, examined whether protected lands do in fact encourage land conservation nearby or how protected lands affect development in the surrounding landscape. Using spatiotemporal data sets on land cover and land protection for three sites (western North Carolina, central Massachusetts, and central Arizona), we examined whether the existence of a protected area correlates with an increased rate of nearby land conservation or a decreased rate of nearby land development. At all sites, newly protected conservation areas tended to cluster close to preexisting protected areas. This may imply that the geography of contemporary conservation actions is influenced by past decisions on land protection, often made for reasons far removed from concerns about biodiversity. On the other hand, we found no evidence that proximity to protected areas correlates with a reduced rate of nearby land development. Indeed, on two of our three sites the development rate was significantly greater in regions with more protected land. This suggests that each conservation action should be justified and valued largely for what is protected on the targeted land, without much hope of broader conservation leverage effects.     

Transformation and removal of ammonium sulfate aerosols and ammonia slip from selective catalytic reduction in wet flue gas desulfurization system

Selective catalytic reduction (SCR) denitration may increase the emission of NH₄⁺ and NH₃. The removal and transformation characteristics of ammonium sulfate aerosols and ammonia slip during the wet flue gas desulfurization (WFGD) process, as well as the effect of desulfurization parameters, were investigated in an experimental system equipped with a simulated SCR flue gas generation system and a limestone-based WFGD system. The results indicate that the ammonium sulfate aerosols and ammonia slip in the flue gas from SCR can be partly removed by slurry scrubbing, while the entrainment and evaporation of desulfurization slurry with accumulated NH₄⁺ will generate new ammonium-containing particles and gaseous ammonia. The ammonium-containing particles formed by desulfurization are not only derived from the entrainment of slurry droplets, but also from the re-condensation of gaseous ammonia generated by slurry evaporation. Therefore, even if the concentration of NH₄⁺ in the desulfurization slurry is quite low, a high level of NH₄⁺ was still contained in the fine particles at the outlet of the scrubber. When the accumulated NH₄⁺ in the desulfurization slurry was high enough, the WFGD system promoted the conversion of NH₃ to NH₄⁺ and increased the additional emission of primary NH₄⁺ aerosols. With the decline of the liquid/gas ratio and flue gas temperature, the removal efficiency of ammonia sulfate aerosols increased, and the NH₄⁺ emitted from entrainment and evaporation of the desulfurization slurry decreased. In addition, the volatile ammonia concentration after the WFGD system was reduced with the decrease of the NH₄⁺ concentration and pH values of the slurry.