中国水泥行业节能减排的潜力与成本分析

全球水泥的温室气体排放约占人类活动排放的5%,其中中国的水泥产量就占到世界总量的50%,连续25年居世界第一位,2010年中国水泥总产量达到18.8亿t。水泥行业是我国排放和耗能的大户,其产业特点是总体产量高,企业平均规模小、技术水平低和产品结构落后,因而,水泥行业节能减排行动是我国应对气候变化的重要措施和基本内容,也是实现我国水泥工业可持续发展的重要保证。本文通过大量的实地调研和数据收集,在识别了18种水泥行业节能减排的典型技术基础上,以日产5 000 t的生产线作为基准,通过边际减排成本的测算,定量分析了我国水泥行业节能减排技术的减排潜力和成本,并最终得到这些技术的边际减排成本曲线,按照减排成本由低到高的排序,主要的减排技术分为能源利用效率、替代能源、混合水泥和CCS技术。最后通过分析我国水泥行业节能减排的技术现状及相关的政策障碍,给出了相应的应对措施和政策建议。     

能源回弹效应的研究进展及其政策涵义

“十二五”期间节能减排的目标是单位GDP能耗下降16％,为实现这一目标,政府采取了以提高能源效率为核心的节能减排政策,但是能源效率的提高可能产生潜在的“回弹效应”,即可能增加能源的使用从而使得节能减排目标难以实现.本文在文献研究的基础上,分析了回弹效应的类型和产生机理,梳理了国内外文献中关于回弹效应测度的实证结果,指出了当前实证研究中存在的主要问题,并从公共政策制定的角度设计了经济模型和其他社会科学相结合的定性比较分析研究方案,主张从经济主体行为反应、替代品价格、能源补贴以及发展新能源政策等多重视角研究回弹效应发生的内在机理,从而对能源政策产生明确的导向.最后,提出了加强能源回弹效应研究的具体政策建议.     

2008年低温雨雪冰冻对武汉城市公共交通的影响评估

为了对2008年低温雨雪期间气象条件对城市交通运输的影响给出定量评估,运用天气分析及统计学方法,分析了低温雨雪冰冻期间武汉市主要气候特征,利用2008年初持续低温雨雪期间武汉城市公共交通线路（包括公交车、轮渡、汽渡）逐日停运数据,定义了持续低温雨雪冰冻过程城市公共交通影响度,通过统计分析,找到了关键气象因子、关键期和低温临界指标,建立了气象评估模型。结果表明：在持续低温雨雪冰冻过程中,初发时期是公共交通影响的关键时期之一,影响度与积雪深度关系最密切,在公交车、轮渡、汽渡3种交通工具中,公交车影响度与气象要素的相关最密切,对武汉城市公交车造成明显影响的临界气温是17℃。该结论在实际的气象灾害评估业务工作中进行了运用,效果良好     

高铁酸钾氧化处理苯酚废水的研究

采用高铁酸钾氧化法处理了具有难生化特性的苯酚废水,以期为该废水提供一种高效经济的处理方法.研究了高铁酸钾加入量、pH值、反应时间、苯酚初始浓度和稳定剂对苯酚废水处理效果的影响.实验结果表明,高铁酸钾投加量为1.2g/L,pH值为4,反应30 min,初始苯酚浓度为100m/L时处理效果最好.所考察的稳定剂包括HAC、N...     

TiO2载体对Mn-Ce/TiO2催化剂脱硝活性的影响

以TiO₂为载体,选取过渡金属元素Mn为活性组分,稀土金属元素Ce为活性助剂,采用分步共混法制备了Mn-Ce/TiO₂催化剂（活性组分负载量16%）,系统研究了TiO₂载体的晶型和晶粒尺寸对催化剂脱硝活性的影响。实验结果表明：分别以锐钛矿型和金红石型TiO₂为载体制备的催化剂,其低温脱硝活性相差不大,活性组分均以无定型态高度分散于载体中,以金红石型TiO₂为载体制备的催化剂中部分TiO₂转变为锐钛矿型;以不同晶粒尺寸TiO₂载体制备的催化剂的低温脱硝活性相差较大,比表面积较大、晶粒尺寸较小的TiO₂载体制备的催化剂,其脱硝活性低于晶粒尺寸较大的TiO₂载体制备的催化剂。     

工业烟气氨法-络合法同时脱硫脱硝

在脱硫脱硝喷淋装置上采用氨法-络合法处理工业烟气。考察了吸收液pH、Fe(Ⅱ)EDTA浓度、初始烟气浓度、液气比对烟气同时脱硫脱硝效果的影响。实验结果表明:吸收液的酸碱度通过影响Fe(Ⅱ)与EDTA的络合形式进而影响NO去除率;SO_2去除率主要受吸收液pH和初始SO_2质量浓度的影响;当吸收液pH大于8、吸收液Fe(Ⅱ)EDTA浓度大于0.100 mol/L、初始SO_2质量浓度小于1 500 mg/m3、初始NO质量浓度为1 200 mg/m3时,SO_2去除率均在95%以上,NO去除率为54%;当液气比由1 L/m3增大至4 L/m3时,有效脱硫时间和有效脱硝时间分别增长了7 min和4 min。     

Climate change impacts on a large-scale erosion coast of Hai Hau district,Vietnam and the adaptation

Among the effects of global warming, sea level rise (SLR) and severe typhoons pose the greatest threat to the stability of human settlements along coastlines. Therefore, countermeasures must be developed to mitigate the influences of strong typhoons and persistent SLR for coastal protection. This study assesses climate change impacts on coastal erosion, especially in two projected SLR scenarios of RCP2.6 and RCP8.5. The results show that SLR and severe typhoons lead to the increase of coastal erosion, beach lowering and scour. Moreover, as in projected SLR scenarios, average waves in high tide can cause severe soil erosion at inner slopes and lead to dyke failure by 2060. The paper highlights the need for additional countermeasures to protect the coast of Hai Hau district against SLR and severe typhoons. Among the alternatives available for countering these threats, applying soil stabilization and soil improvement combined with geosynthetics are promising strategies for coastal structures. Hybrid structures can be used with earth reinforcement and soil improvement. Additionally, the paper emphasizes the importance of multiple protective adaptations, including geosynthetics and ecological engineering measures against climate change-induced severe erosion on the coast of Hai Hau district.     

Investigation of the accumulation of ash,heavy metals,and polycyclic aromatic hydrocarbons to assess the stability of lysis–cryptic growth sludge reduction in sequencing batch reactor

The accumulation of ash, heavy metals, and polycyclic aromatic hydrocarbons (collectively called potential accumulating substances, PAS) was evaluated to ascertain the stability of lysis–cryptic growth sludge reduction process (LSRP) for municipal sludge treatment. One sequencing batch reactor (SBR) incorporated with homogenization was run to test the LSRP and another SBR as a control. The continuous monitoring results for 2 months showed that the ash and heavy metals slightly increased, and the polycyclic aromatic hydrocarbons decreased by 18.0%, indicating that there may be negligible accumulations during the LSRP. Their accumulations met pattern I, as demonstrated by statistical analysis, proving no PAS accumulation for LSRP. This was further confirmed by sludge activity and system performance. Moreover, the mechanism for no PAS accumulation was discussed. It was concluded that the LSRP was stable with no worries about PAS accumulation under the operational conditions.     

用于污水再生利用的生物活性炭床的有机物降解特性

以微生物增殖动力学的基本方程-莫诺方程为出发点,通过氮同位素分析比较了具有同源性微生物的生物陶粒滤床和生物活性炭床的有机物生物降解规律,建立了生物活性炭床的有机物生物降解动力学方程,提出在污水再生利用过程中生物活性炭床符合高基质有机物降解动力学模型,即有机物降解呈一级反应动力学方程。以此方程为基础,分析计算了生物活性炭床沿炭床深度的吸附性能,结果表明,在生物活性炭床中,随生物功能的减弱,生物活性炭床对有机物的吸附能力逐渐加强。     

Heterogeneous photocatalytic degradation of methyl orange in schwertmannite/oxalate suspension under UV irradiation

Introduction

Schwertmannite was synthesized through an oxidation of FeSO₄ by Acidithiobacillus ferrooxidans LX5 cell suspension at an initial pH?2.5 and 28°C for 3?days and characterized using X-ray diffraction spectroscopy and scanning electron microscope. The schwertmannite photocatalytic degradation of methyl orange (MO) by oxalate was investigated at different initial pH values, concentrations of schwertmannite, oxalate, and MO.

Results

The results demonstrated that photodegradation of MO in the presence of schwertmannite or oxalate alone was very weak. However, the removal of MO was significantly enhanced when schwertmannite and oxalate coexisted in the reaction system. Low pH (4 or less) was beneficial to the degradation of MO. The optimal doses of schwertmannite and oxalate were 0.2?g?L^?1 and 2?mM, respectively. Hydroxyl radicals (·OH) and Fe(II), the intermediate products, were also examined during the reaction to explore their correlation with the degradation of MO.

Conclusion

A possible mechanism for the photocatalytic decomposition of MO in the study was proposed. The formation of Fe(III)-oxalate complexes on the surface of schwertmannite was a precursor of H₂O₂ and Fe(II) production, further leading to the yield of ·OH responsible for the decomposition of MO.