基于二次铝灰的地聚反应稳固化垃圾飞灰

基于工业生产铝过程中回收的二次铝灰（SAD）的地质聚合反应,提出了一种稳固化城市生活垃圾焚烧飞灰（MSWIFA）的新方法,分析硅铝物质的量之比对飞灰中重金属浸出浓度及地聚物固化体力学性能的影响规律.结果表明,当硅铝物质的量之比小于2.5时,二次铝灰-SiO₂基固化体与偏高岭土-SiO₂基固化体中的重金属浸出浓度均随着硅铝物质的量之比的增加而逐渐降低,2种固化体的抗压强度随着硅铝物质的量之比的增加而增加;硅铝物质的量之比达到2.5时,重金属的浸出浓度与固化体的抗压强度均趋于稳定.XRD分析结果显示,偏高岭土-SiO₂基固化体中聚合物的种类与数量均略高于二次铝灰-SiO₂基固化体.但从重金属的浸出浓度与固化体的抗压强度来看,2类固化体对飞灰中重金属的稳固化效果的差别很小,二次铝灰加上部分硅基材料可以作为偏高岭土的替代品,用于稳固化飞灰重金属的地质聚合反应中.二次铝灰-SiO₂基固化体的抗压强度达到13.65MPa,具备一定的力学性能,可用于部分特定的建筑材料.     

食物转化视角下我国家庭食物浪费程度与影响因素——基于CHNS数据的实证分析

长期以来,我国食物供应充足稳定,但是人口、环境等因素不断对此提出挑战,并且我国每年的食物损失和浪费数量十分惊人。从食物转化视角将食物浪费率定义为家庭食物消费中未能正常转化为家庭成员身体质量指数的比例,采用随机前沿模型并基于CHNS数据估算我国家庭食物浪费率,并探讨家庭异质性特征的影响。结果显示：家庭平均浪费率为11.28%;家庭规模越小、孩子或老年人的数量越多、收入水平越高、南方地区、户主的受教育程度越低、主要女性成员的受教育程度越高或者有工作、对膳食知识掌握程度越低的家庭浪费率越高。因此,要鼓励生产小包装食物和小型厨具,指导家庭根据实际需求购买食物,加强推广食育运动,开展节粮活动并教授减损措施。     

氯化剂对超细颗粒物与重金属共生成特性的影响

以循环流化床反应器为实验平台,研究了焚烧温度为850℃下添加剂（NH₄Cl和KCl）对超细颗粒物与重金属共生成特性的影响.结果表明：NH₄Cl和KCl的存在均会降低超细颗粒物的数量浓度,但KCl的效果更佳,发挥的是阶梯式或者协同式作用.此外,添加比例为3%时对超细颗粒物数量浓度的降低最为明显.重金属Cr,Mn,Ni主要通过夹带方式形成超细颗粒物;而重金属Pb,Cu,Zn则主要通过蒸发、冷凝和吸附方式累积在超细颗粒物中.无机氯在焚烧过程中可以作为颗粒之间良好的粘合剂,促进超细颗粒物之间的成长和团聚,同时促进其表面形态的生长.此外,K的存在会促进细模态颗粒物之间的凝聚成长,使得细模态颗粒物的峰值增大,而NH₄⁺的存在会降低粗模态颗粒物的峰值.本研究可为污泥等废物热处理过程中重金属与超细颗粒物的协同控制提供借鉴.     

不同预处理方法促进剩余污泥发酵制氢研究进展

综述了剩余污泥发酵制氢的底物预处理方法,主要包括物理法（热水解法、微波法、超声波法、冻融法）;化学法（酸碱预处理、臭氧氧化法）;生物法（生物强化技术、生物酶法）,分析比较了不同预处理方法的剩余污泥发酵制氢体系的氢气含量及产率,污泥处理后溶解性化学需氧量、挥发性脂肪酸含量的变化和工程应用的优缺点,并指出目前研究存在的一些不足和对未来应用前景的展望,以期为剩余污泥发酵制氢预处理方法的研究与应用提供依据.     

兼氧条件下厨余垃圾发酵液作碳源的反硝化性能

在兼氧条件下,利用厨余垃圾厌氧发酵液调节反硝化系统的碳氮比（COD/TN,C/N）,并考察了其脱氮性能.结果表明,不同C/N条件下,反应系统均未出现有机物的积累,但高C/N条件下的亚硝酸盐最大积累浓度和积累速率高于低C/N;随着进水C/N的增大,反应整体脱氮率和反硝化速率不断增大,当C/N为13时,反硝化速率达到了最大值,为9.79mg/（gVSS·h）,其脱氮率超过95%;相同C/N条件下,反硝化速率和最大亚硝酸盐积累浓度均与进水硝酸盐浓度成正比.此外,实验结果表明,兼氧条件下的反硝化过程虽不易出现COD残留,但去除单位氮所需的有机物更多,且整体反硝化速率以及亚硝酸盐还原速率均低于厌氧条件.     

3D打印技术在固体废弃物资源循环中的应用

打印材料是限制3D打印技术发展和推广应用的瓶颈问题,目前已经发现部分固体废弃物与3D打印的契合度很高,可以用于制备3D打印材料.本文综述了4类可以用于3D打印的固体废弃物,包括硅铝基废弃物、农林废弃物、废旧塑料和废旧金属,着重讨论了这4类废弃物制备3D打印材料的方法以及废弃物的添加对原打印材料造成的影响,同时分析了当前废弃物制备3D打印材料需要解决的问题,并对废弃物基3D打印材料的发展趋势进行了展望.     

Flow analysis of major and trace elements in residues from large-scale sewage sludge incineration

Increase of sewage sludge (SS) has led to the construction of more incineration plants, exacerbating to the production of SS incineration residues. However, few studies have considered the mass balance of elements in large-scale SS incineration plants, affecting the residues treatment and utilization. In this study, flow analysis was conducted for major and trace elements in the SS, the fly ash (sewage sludge ash, SSA) and bottom ash from two large-scale SS incineration plants. The elemental characteristics were compared with those of coal fly ash (CFA), and air pollution control residues from municipal solid waste incineration (MSWIA), as well as related criteria. The results showed that the most abundant major element in SSA was Si, ranging from 120 to 240 g/kg, followed by Al (76–348 g/kg), Ca (26–113 g/kg), Fe (35–80 g/kg), and P (26–104 g/kg), and the trace elements were mainly Zn, Ba, Cu, and Mn. Not all the major elements were derived from SS. Most trace elements in the SS incineration residues accounted for 82.4%–127% of those from SS, indicating that SS was the main source of trace elements. The partitioning of heavy metals in the SS incineration residues showed that electrostatic precipitator ash or cyclone ash with high production rates were the major pollutant sinks. The differences in some major and trace elements could be indicators to differentiate SSA from CFA and MSWIA. Compared with related land criteria, the pollutants in SSA should not be ignored during disposal and utilization.     

Primary and secondary organic aerosol in an urban/industrial site: Sources, health implications and the role of plastic enriched waste burning

PM10 samples were collected from an urban/industrial site nearby Athens, where uncontrolled burning activities occur. PAHs, monocarboxylic, dicarboxylic, hydroxycarboxylic and aromatic acids, tracers from BVOC oxidation, biomass burning tracers and bisphenol A were determined. PAH, monocarboxylic acids, biomass burning tracers and bisphenol A were increased during autumn/winter, while BSOA tracers, dicarboxylic- and hydroxycarboxylic acids during summer. Regarding aromatic acids, different sources and formation mechanisms were indicated as benzoic, phthalic and trimellitic acids were peaked during summer whereas p-toluic, isophthalic and terephthalic were more abundant during autumn/winter. The Benzo[a]pyrene-equivalent carcinogenic power, carcinogenic and mutagenic activities were calculated showing significant (p < 0.05) increases during the colder months. Palmitic, succinic and malic acids were the most abundant monocarboxylic, dicarboxylic and hydrocarboxylic acids during the entire sampling period. Isoprene oxidation was the most significant contributor to BSOA as the isoprene-SOA compounds were two times more abundant than the pinene-SOA (13.4 ± 12.3 and 6.1 ± 2.9 ng/m³, respectively). Ozone has significant impact on the formation of many studied compounds showing significant correlations with: isoprene-SOA (r = 0.77), hydrocarboxylic acids (r = 0.69), pinene-SOA (r = 0.63),dicarboxylic acids (r = 0.58), and the sum of phthalic, benzoic and trimellitic acids (r = 0.44). PCA demonstrated five factors that could explain sources including plastic enriched waste burning (30.8%), oxidation of unsaturated fatty acids (23.0%), vehicle missions and cooking (9.2%), biomass burning (7.7%) and oxidation of VOCs (5.8%). The results highlight the significant contribution of plastic waste uncontrolled burning to the overall air quality degradation.     

Effect of environmental parameters on the degradability of polymer films in laboratory-scale composting reactors

Previous research in our laboratory reported a convenient laboratory-scale composting test method to study the weight loss of polymer films in aerobic thermophilic (53°C) reactors maintained at a 60% moisture content. The laboratory-scale compost reactors contained the following synthetic compost mixture (percentage on dry-weight basis): tree leaves (45.0), shredded paper (16.5), food (6.7), meat (5.8), cow manure (17.5), sawdust (1.9), aluminum and steel shavings (2.4), glass beads (1.3), urea (1.9), and a compost seed (1.0) which is designated Mix-1 in this work. To simplify the laboratory-scale compost weight loss test method and better understand how compost mixture compositions and environmental parameters affect the rate of plastic degradation, a systematic variation of the synthetic mixture composition as well as the moisture content was carried out. Cellulose acetate (CA) with a degree of substitution (DS) value of 1.7 and cellophane films were chosen as test polymer substrates for this work. The extent of CA DS-1.7 and cellophane weight loss as a function of the exposure time remained unchanged when the metal and glass components of the mixture were excluded in Mix-2. Further study showed that large variations in the mixture composition such as the replacement of tree leaves, food, meat, and sawdust with steam-exploded wood and alfalfa (forming Mix-C) could be made with little or no change in the time dependence of CA DS-1.7 film weight loss. In contrast, substituting tree leaves, food, meat, cow manure, and sawdust with steam-exploded wood in combination with either Rabbit Choice (Mix-D) or starch and urea (Mix-E) resulted in a significant time increase (from 7 to 12 days) for the complete disappearance of CA DS-1.7 films. Interestingly, in this work no direct correlation was observed between the C/N ratio (which ranged from 13.9 to 61.4) and the CA DS-1.7 film weight loss. Decreasing moisture contents of the compost Mix-2 from 60 and 50 and 40% resulted in dramatic changes in polymer degradation such that CA DS-1.7 showed an increase in the time period for a complete disappearance of polymer films from 6 to 16 and 30 days, respectively.Guest Editor: Dr. Graham Swift, Rohm & Haas.Paper presented at the Bio/Environmentally Degradable Polymer Society—Second National Meeting, August 19–21, 1993, Chicago, Illinois.     

粉煤灰和活性污泥对好氧填埋渗滤液组分的影响

通过在好氧反应器中添加粉煤灰和活性污泥来加速固体废物的降解。实验结果表明,添加粉煤灰不但改善了氧气扩散,而且增强了反应器对各种污染物的去除能力,对渗滤液中COD、NH4+、NO3-的去除率分别达到75%、68%和65%以上;添加活性污泥引入了一定量的微生物,也有利于固体废物的降解,渗滤液中COD、NH4+、NO3-的去除率分别达到了90%、65%和77%。因此,通过添加粉煤灰和活性污泥来加速固体废物降解是可行的。