浅析城市生活垃圾分类回收

城市生活垃圾分类回收有别于混合收集,是垃圾收集的一种新趋势.结合我国垃圾的特点,阐明了当前垃圾分类收集的现状,并指出了我国垃圾分类回收的意义;根据当前垃圾收集存在的问题,提出了一些具体化的对策.通过垃圾的分类回收,减少了垃圾的最终处置量,提高垃圾资源化率.     

北京市生活垃圾分类标准体系框架研究

为认真贯彻落实习近平总书记关于垃圾分类工作的重要指示精神,配合《北京市生活垃圾管理条例》正式实施,北京市开展垃圾分类工作。根据北京市垃圾分类实际工作需要,按照垃圾分类全流程梳理标准,构建标准体系。以标准体系为基础,整理垃圾分类标准存量情况,分析标准制修订需求,梳理垃圾分类过程,为今后制定生活垃圾分类相关标准提供理论支撑,实现对标准的科学管理,系统地指导北京市垃圾分类工作,构建垃圾分类新发展格局。     

苏州市生活垃圾分类实践及思考

介绍了苏州市生活垃圾"近期大分流、远期细分类"的分类模式,以及垃圾分类的政策法规体系、收运体系和终端处置体系,提出关于垃圾分类对垃圾减量的贡献、厨余垃圾分类的必要性和可行性、垃圾分类的主要推动力及垃圾分类模式选择的思考和建议。     

校园生活垃圾“三元二级分类”体系研究

垃圾分类是垃圾处理的基础,探索适宜的垃圾分类模式,将助力生活垃圾强制分类和处理。以山东农业大学南校区为例,采用"三元二级分类"体系,对校园生活垃圾分类进行探索;对分类后的湿垃圾资源化进行研究;对推进高校生活垃圾分类进行探讨。"三元分类"实现干、湿分离,及对特种垃圾单列;"二级分类"对三大类再进行细分。对山东农业大学南校区生活垃圾经过6次取样,统计结果为湿垃圾占比63.91%、干垃圾占比35.58%、特种垃圾占比0.51%。对其中的湿垃圾利用黄粉虫和白星花金龟过腹转化进行研究,结果表明,利用微生物+两种环境昆虫组合技术,最大可实现湿垃圾资源化减量95%,占生活垃圾总量的60.71%。在推进高校生活垃圾分类研究中,总结了成立创新团队和建立生活垃圾分类及湿垃圾资源化示范基地两条可行路径。     

广州市建筑垃圾资源化的必要性分析

摘要：随着广州市城市化进程的不断加快,城市建筑垃圾的排出量也在快速增长,如何应对和处理建筑垃圾所带来的“垃圾围城”困境,已经成为人们不得不面对的重要问题,推进建筑垃圾资源化是开展建筑垃圾综合治理的有效途径。论述了建筑垃圾资源化再生利用的必要性、紧迫性,指出了广州市建筑垃圾资源化过程中存在的问题,为推进广州市建筑垃圾综合处理实践提供了参考。     

山东省城镇居民生活垃圾分类行为研究

分析山东省城镇居民垃圾分类的现状,研究山东省城镇居民垃圾分类行为的影响因素。运用主成分分析法对居民垃圾分类行为的影响因素进行研究。居民认为处理垃圾分类时较复杂;阻力决定垃圾分类行为;居民易受到外界环境的影响。加强垃圾分类知识宣传力度、完善政策、提高技术水平等,是提高居民生活垃圾分类参与度的关键。     

基于区块链技术的垃圾回收治理平台构建探究

当今的垃圾治理问题面临着严峻的挑战,垃圾治理不善导致了严重的环境污染及资源浪费的问题。区块链技术具有去中心化、可追溯、点对点等特性。通过区块链技术构建垃圾回收治理平台,可以在垃圾回收治理的各个环节提高垃圾回收治理的效率,实现居民及企业与垃圾治理商之间的供需对接,提高垃圾回收率,进而减少资源浪费,提高产品残值,促进垃圾回收治理全产业链效率,优化及资源环境的改善。     

南充城市垃圾处理产业化研究

介绍了南充市城市垃圾概况及处理现状,提出了南充城市垃圾处理产业化的构想,并对垃圾产业化的经济效益、社会效益、环境效益进行了探讨,提出南充要实现城市垃圾产业化,必须加强宣传教育,改进垃圾收集设施,实行垃圾分类,制定政策,促进垃圾产化市场形成,实现规模化.     

综合分选处理村镇垃圾的技术方案研究

通过回收垃圾中的资源,提高垃圾的处理率,利用先进的分选技术,将垃圾减量化、资源化和无害化处理,使垃圾中的资源得到有效的利用。特别是城乡结合部垃圾的治理,提出了处理工艺和方案。     

城市生活垃圾三元二级分类体系的构建及应用前景

城市生活垃圾的精细分类是高效高值化垃圾处理的基础和前提,城市生活垃圾处理的关键在于阻遏垃圾混合和如何充分利用湿垃圾。城市生活垃圾三元二级分类体系,即首先将垃圾分为3种类型:干垃圾、湿垃圾和特种垃圾;然后再分别进行二次单一化精细分类。源头分类阻遏了垃圾进入混合状态;对有机垃圾则通过物理破碎、微生物混合发酵预处理、环境昆虫过腹转化的"三位一体处理技术系统"实现资源化利用。城市生活垃圾三元二级分类体系是一个简化垃圾分类体系,改变了"可回收"与"不可回收"垃圾难以快捷界定的难题。     

Determination of the Thermal Efficiency of Pre-boilover Burning of a Slick of Oil on Water

The burning rate of a slick of oil on a water bed is calculated by a simple expression derived from a one-dimensional heat conduction equation. Heat feedback from the flame to the surface is assumed to be a constant fraction of the total energy released by the combustion reaction. The constant fraction (χ) is named the burning efficiency and represents an important tool in assessing the potential of in situ burning as a counter-measure to an oil-spill. The total heat release, as a function of the pool diameter, is obtained from an existing correlation. It is assumed that radiative heat is absorbed close to the fuel surface, that conduction is the dominant mode of heat transfer in the liquid phase and that the fuel boiling temperature remains constant. By matching the characteristic thermal penetration length scale for the fuel/water system and an equivalent single layer system, a combined thermal diffusivity can be calculated and used to obtain an analytical solution for the burning rate. Theoretical expressions were correlated with crude oil and heating oil, for a number of pool diameters and initial fuel layer thickness. Experiments were also conducted with emulsified and weathered crude oil. The simple analytical expression describes well the effects of pool diameter and initial fuel layer thickness permitting a better observation of the effects of weathering, emulsification and net heat feedback to the fuel surface. Experiments showed that only a small fraction of the heat released by the flame is retained by the fuel layer and water bed (of the order of 1%). The effect of weathering on the burning rate decreases with the weathering period and that emulsification results in a linear decrease of the burning rate with water content.     

Calculation of carbon balances for evaluation of the biodegradability of polymers

Establishing carbon balances has been proven to be an applicable and powerful tool in testing biodegradability of polymers. In controlled degradation tests at a 4-L scale with the model polymer poly(-hydroxybutyrate) (PHB), it was shown that the degree of degradation could not be determined with satisfactory accuracy from CO₂ release alone. Instead, the course of degradation was characterized by means of establishing carbon balances for the degradation of PHB withAcidovorax facilis and a mixed culture derived from compost. Different analytical methods for determining the different carbon fractions were adapted to the particular test conditions and compared. Quantitative determination of biomass and residual polymer were the main problems in establishing carbon balances. Amounts of biomass derived from protein measurements depend strongly on assumptions of the protein content of the biomass. Selective oxidation of biomass with hypochlorite was used as alternative, but here problems arose from insoluble metabolic products. Determination of soluble components with the method of chemical oxygen demand (COD) also includes empirical assumptions but seems acceptable if the dissolved carbon fraction is in the range of some 10% total carbon. Results confirm both analytical assays and theoretical approaches, in ending up at values very close to 100%, within an acceptable standard deviation range under test conditions comparable to standard test practice.Paper presented at the Bio/Environmentally Degradable Polymer Society—Third National Meeting, June 6–8, 1994, Boston, Massachusetts.     

富拉尔基发电总厂200MW机组除尘器改造

对富拉尔基发电总厂5号炉的设计条件进行了分析，针对燃用低硫煤，飞灰比电阻高，场地较小，除尘效率要求高的情况，在电除尘器的设计上采取有效措施，达到了排放要求。     

Review of the kinetics of alkaline degradation of cellulose in view of its relevance for safety assessment of radioactive waste repositories

The degradation of cellulose (a substantial component of low- and intermediate-level radioactive waste) under alkaline conditions occurs via two main processes: a peeling-off reaction and a basecatalyzed cleavage of glycosidic bonds (hydrolysis). Both processes show pseudo-first-order kinetics. At ambient temperature, the peeling-off process is the dominant degradation mechanism, resulting in the formation of mainly isosaccharinic acid. The degradation depends strongly on the degree of polymerization (DP) and on the number of reducing end groups present in cellulose. Beyond pH 12.5, the OH^- concentration has only a minor effect on the degradation rate. It was estimated that under repository conditions (alkaline environment, pH 13.3-12.5) about 10% of the cellulosic materials (average DP = 1000-2000) will degrade in the first stage (up to 10⁵ years) by the peeling-off reaction and will cause an ingrowth of isosaccharinic acid in the interstitial cement pore water. In the second stage (10⁵-10⁶ years), alkaline hydrolysis will control the further degradation of the cellulose. The potential role of microorganisms in the degradation of cellulose under alkaline conditions could not be evaluated. Proper assessment of the effect of cellulose degradation on the mobilization of radionuclides basically requires knowing the concentration of isosaccharinic acid in the pore water. This concentration, however, depends on several factors such as the stability of ISA under alkaline conditions, sorption of ISA on cement, formation of sparingly soluble ISA-salts, etc. A discussion of all the relevant processes involved, however, is far beyond the scope of the presented overview.     

Study of Aging Characteristics of Ternary Blends of Polyethylenes—II

Six film samples of low-density polypropylene (LDPE)/linear LDPE (LLDPE)/high-density polypropylene (HDPE) with varying ratios of LDPE (20–45 ... wt%) and LLDPE (25–50 wt%) having a fixed amount of HDPE at 30 wt% were prepared by blown film extrusion technique. The samples were aged at four different temperatures, 55°, 70°, 85°, and 100°C, for four different time periods in the interval of between 150 hours and up to 600 hours. The change in the structure of various constituents and the formation of various oxygenated (peroxy and hydroperoxy) and unsaturated groups during thermo-oxidative degradation was discussed by infrared spectroscopy. The visiosity-average molecular weight was found to have decreased slowly in the initial aging hours and temperatures, whereas it decreased by 10% with its previous value tensile strength that is, 100°C when aged for 600 hours. The tensile strength of the sample first increased by 67% at 55°C and 89% at 70°C up to 450 hours, whereas the values increased by 52.5% at 85°C and 33.9% at 100°C when aged for 150 hours and then decreased. The percentage elongation at break increased by 2.7% at 55°C and 10.7% at 70°C for 150 and 300 hours of aging, respectively, whereas the percentage decreased when aged at 85°C and 100°C for up to 600 hours of aging. The values of gel content (percent) increased and initial degradation temperature decreased with aging time and temperature.     

Selection of adsorbents for treatment of leachate: batch studies of simultaneous adsorption of heavy metals

The simultaneous adsorption of copper (Cu), cadmium (Cd), nickel (Ni), and lead (Pb) ions from spiked deionized water and spiked leachate onto natural materials (peat A and B), by-product or waste materials (carbon-containing ash, paper pellets, pine bark, and semi-coke), and synthetic materials (based on urea-formaldehyde resins, called blue and red adsorbents) or mixtures thereof was investigated. The adsorbents that gave the highest metal removal efficiencies were peat A, a mixture of peat B and carbon-containing ash, and a mixture of peat A and blue. At an initial concentration of 5 mg/l for each metal, the removal of each species of metal ion from spiked water and spiked leachate solutions was very good (>90%) and good (>75%), respectively. When the initial concentration of each metal in the solutions was twenty times higher (100 mg/l), there was a noticeable decrease in the removal efficiency of Cu²⁺, Cd²⁺, and Ni²⁺, but not of Pb²⁺. Langmuir monolayer adsorption capacities, q_m, on peat A were found to be 0.57, 0.37, and 0.36 mmol/g for Pb²⁺, Cd²⁺, and Ni²⁺, respectively. The order of metal adsorption capacity on peat A was the same in the case of competitive multimetal adsorption conditions as it was for single-element adsorption, namely Pb²⁺ > Cd²⁺ ≥ Ni²⁺. The results show that peat alone (an inexpensive adsorbent) is a good adsorbent for heavy metal ions.     

袋式除尘器气流分布数值计算研究

采用结构化/非结构化混合网格技术、多孔介质模型及k-ε两方程湍流模型,对某袋式除尘器及进出口管道内的气体流场进行了数值计算.计算结果表明,合理布置导流板后,袋式除尘器两箱体流量偏差为1.8％;除尘器下游滤袋单元处理气量偏大,中游滤袋单元处理气量较小,最大流量与最小流量偏差为22.3％;靠近除尘器进口处灰斗内存在气流回流特性,易造成粉尘的二次附着现象.     

Effect of Degree of Substitution of Octenyl Succinate Starch on Enzymatic Degradation

Octenyl succinate starch of degree of substitution (ds) 0.03, 0.07, and 0.11 was synthesized in an aqueous medium. These compounds were then tested for the susceptibility to enzymatic degradation. The multiple-enzyme regime of -amylase, amyloglucosidase, and pullulanase was chosen for the evaluation. This combination of enzymes had been proven to degrade 99.5% of unmodified starch to glucose and hence was chosen for this study. It was found that even small amounts of subsituent caused a considerable decrease in the extent of degradation. The net extent of degradation decreased with increasing ds. Surprisingly, the amount of glucose from all three substituted substrates was quite similar, suggesting the effect small amounts of subtituent had on the enzymatic activity.     

Kinetics of Hydrolytic Degradation of PLA

The chemical recycling of poly(lactic acid) (PLA) to its monomer is crucial to reduce both the consumption of renewable resources for the monomer synthesis and the environmental impact related to its production and disposal. In particular, the production of lactic acid from PLA wastes, rather than from virgin raw materials, it is also possible to achieve considerable primary energy savings. The focus of this work is to analyse deeply the PLA hydrolytic decomposition by means of a kinetic model based on two reactions mechanism. To this end, new experimental data have been gathered in order to investigate a wider temperature range (from 140 to 180 °C) and to extend the water/PLA ratio up to 50 % of PLA by weight. The reported results clearly highlight that more than 95 % of PLA is hydrolyzed to water-soluble lactic acid within 120 min, when it is hydrolyzed within 160–180 °C. Furthermore, the kinetic constant is highly influenced by reaction temperature. The proposed “two reactions” kinetic mechanism complies satisfactorily with the experimental data under analysis.     

Effects of temperature on the release of nutrient elements of solid organic materials under conditions of oversaturation

The effects of temperature on the release of chemical components of six solid organic materials under conditions of oversaturation were investigated in this paper. The six materials were peat moss (PM), weathered coals (WC), charred rice husks (CRH), sawdust (Sd), turfgrass clippings (TC), and chicken manure (CM). Significant differences were observed in the available nitrogen and phosphorus content of the aqueous extracts of organic materials at different temperatures. The available nitrogen content in aqueous extracts of PM and WC at 25 °C was higher than that registered at 15 °C and 35 °C. Available nitrogen content in the aqueous extracts of CRH, Sd, TC, and WC at 35 °C was higher than at 15 °C and 25 °C. The available phosphorus content in the aqueous extracts of organic materials at 35 °C was higher than that available at 15 °C and 25 °C, with the exception of Sd. In addition, the release of available phosphorus in the aqueous solution of organic materials at different temperatures varied constantly for 108 h. The release of potassium (K⁺) and sodium (Na⁺) ions in the aqueous extracts of organic materials was basically steady over time, with the exception of CM. High temperature (35 °C) may significantly hasten the release of K⁺ from organic substrates (except for WC) with low temperatures significantly inhibiting release of K⁺ in Sd and CRH. High temperatures (35 °C) might significantly facilitate the release of Na⁺ in CM and TC. However, no significant differences were manifested in the release of Na⁺ from organic substrates at different temperatures, with the exception of CM and TC. Moreover, no significant differences were observed in the release of calcium, magnesium and iron ions with time, nor were there any significant differences in the contents of iron ions in the aqueous extracts of organic materials at different temperatures. The results indicate that multiple mediums should be pretreated in water for a week before being used for planting. They should be used when all mineral elements of organic materials are steady and ignoring the effect of organic mediums.