垃圾焚烧飞灰处置与资源化利用研究进展

随着生活垃圾焚烧处理方式的不断推广，焚烧飞灰的产生量也不断增加。按照我国固体废物分类方法，焚烧飞灰属于危险废物，必须进一步处置才能进入填埋场或资源化利用。本文分析了飞灰物理化学特性，论述了常规处置技术（水泥固化、化学药剂稳定化、酸溶剂提取和熔融固化等）存在的问题。将原始飞灰直接应用于水泥、混凝土或路基材料，飞灰中高含量的重金属和盐类会产生新的环境问题。飞灰水洗可以高效去除其中的可溶性盐类，水洗飞灰在焙烧后重金属的浸出浓度远低于原始飞灰烧结后的相应浓度，飞灰水洗-焙烧技术具有很好的应用前景。     

生活垃圾焚烧飞灰主要处置技术及其发展趋势

文章归纳了我国生活垃圾焚烧飞灰的特点,总结了飞灰固化/稳定化-填埋、高温烧结制陶粒、等离子体熔融、水泥窑协同处置和低温热解处置技术特点,并分析了它们的发展趋势。     

垃圾焚烧飞灰的处理与处置技术

通过分析垃圾焚烧飞灰的物理化学性质,对目前国内外城市垃圾焚烧飞灰处理技术进行了系统分析和讨论归纳。水泥固化、烧结法等原料廉价、易得,但处理效果并不理想,需要进行预处理;熔融固化、水热法、电化学法等需要大量的能耗,经济可行性差;化学药剂处理对于具有差异性的飞灰难以普遍适用;浸提法、超临界流体萃取法等方法工艺要求高,生产条件要求严格,需要大量资金投入。分析目前国内垃圾焚烧飞灰处理方式的优势及局限性,结果表明,水泥固化和熔融固化是当前飞灰综合利用的发展方向。     

我国南方某城市垃圾焚烧飞灰特性及固化/稳定化处置实验

我国南方某城市主要采用焚烧法处理生活垃圾,已建7个焚烧厂日产生飞灰量为101.62 t/d。文章分析了各个垃圾焚烧厂飞灰的化学组成和重金属浸出毒性,其主要成分为CaO、SiO2、MgO、Al2O3、Fe2O3、Na2O、SO3和Cl,所有焚烧飞灰都有至少一种重金属浸出浓度超标,属于危险废物。在飞灰处置出路亟待解决的背景下,实验探讨了飞灰稳定化工艺,结果表明10%的水泥添加量可以使飞灰中超标重金属(Cd、Pb和Zn)的浸出浓度满足危险废物鉴别浓度限值和安全填埋场入场浓度限值。同时,通过人体健康风险评价分析了飞灰豁免管理的可行性,并对近期和远期该城市焚烧厂飞灰的处理处置及管理提出建议。     

城市生活垃圾焚烧发电技术的研究及应用

基于我国城市生活垃圾多水分、低热值的特点,某市城市生活垃圾焚烧发电项目,采用新型"顺推干燥+逆推燃烧燃尽"结构的复合式机械炉排炉。运用"SNCR脱硝+半干法脱酸+消石灰干粉喷射+活性炭喷射装置+布袋除尘器"烟气净化系统处理、炉渣有效利用+飞灰采用稳定剂+水泥固化/稳定化的灰渣处理系统,"预处理+混凝沉淀+厌氧+外置式MBR(膜生物反应器)+NF(纳滤)/RO(反渗透)"渗滤液处理系统,解决了焚烧发电产生的废气、废渣、废水问题。     

生活垃圾焚烧中重金属行为的研究进展

垃圾中的金属以氧化物、氮化物、碳化物及其它形态转移到焚烧产物如烟气、飞灰和底灰中，需严格控制焚烧过程中重金属的排放，故清楚了解金属在焚烧中的行为是很必要的。经研究发现，飞灰中重金属含量远远大于底灰中的含量，因此以垃圾焚烧飞灰中重金属的稳定化处理为目标，分析了目前国内外处理垃圾焚烧飞灰的方法和重金属在各种影响因素下的行为，并进行了比较，为飞灰的无害化和资源化处理提供参考。     

垃圾焚烧飞灰中重金属高温挥发影响因素分析

随着垃圾焚烧技术的推广,产生了大量的飞灰。重金属是垃圾焚烧飞灰中最重要的污染成分之一,其所具有的不可降解性和在生物体内的富集效应,决定了其将长期存在并对生态环境构成极大的潜在威胁。主要阐述了重金属的来源,并分析了重金属在各种影响因素下的迁移行为,为飞灰的稳定化和资源化处理提供参考。     

生物炭对土壤中复合重金属的固化/稳定化研究

土壤重金属污染逐渐变成全球关注的环境问题。而固化/稳定化技术是修复重金属污染土壤快速、有效及经济的方式。概括土壤中重金属的来源和危害、固化/稳定化技术的机理,探讨了以独特物化性质的生物炭作为治理土壤中重金属的固化/稳定化剂时对重金属和砷的处理研究。最后,对未来生物炭的安全性和长期稳定性的研究作出了展望。     

危险废物焚烧飞灰固化处理技术应用探讨

危险废物焚烧处理过程产生的飞灰中含有重金属、二英等有害成分,必须进行处理。目前工程中常用的飞灰固化处理技术主要包括水泥固化、石灰固化、塑性材料固化、玻璃固化等。水泥固化是所有固化技术中应用最多的,但在工程应用中也存在自动化水平不高、成本高、占地面积大、对环境有潜在威胁等问题,需进一步克服。     

垃圾焚烧飞灰的处置及资源化利用工艺研究

论述了目前国内对于生活垃圾焚烧飞灰处理处置及利用的情况,介绍了一种垃圾焚烧飞灰资源化技术的工艺流程、特点以及应用情况,为改善生活垃圾焚烧飞灰利用技术水平有限的局面,避免其造成二次污染环境风险提供了技术参考。     

The reuse of municipal solid waste incinerator fly ash slag as a cement substitute

The results of the treatment of fly ash from a municipal solid waste incinerator (MSWI) by melting are described, and the safety and the effectiveness of using the slag produced by this melting treatment are studied. The properties of the MSWI fly ash slag were analyzed, to evaluate the feasibility of its reuse as a substitute for part of the cement required in mortar preparation. This MSWI fly ash slag was found to be comprised mainly of SiO₂ and CaO, which can be substituted for up to 20% of the cement content in mortar, without sacrificing the quality of the resultant concrete. In fact, the concrete thus produced has greater compressive strength, 10% higher than that without the substitution. The setting time of the fresh mortar becomes lengthens as increasing amounts of cement are replaced; while the spread flow value increases with the increasing percentage of cement substitution. X-ray diffraction analysis reveals that when the W/C=0.38 and the curing AGE=28 days, the crystal patterns in the mortar samples, prepared with different amounts of cement having been replaced by MSWI fly ash slag are similar. According to the results of the toxic characteristic leaching procedure analysis, MSWI fly ash slag should be classified as general non-hazardous industrial waste, that meets the effluent standard. Therefore, the reuse of MSWI fly ash slag is feasible, and will not result in pollution due to the leaching of heavy metals.     

Utilization of washed MSWI fly ash as partial cement substitute with the addition of dithiocarbamic chelate

The management of the big amount of fly ash as hazardous waste from the municipal solid waste incinerator (MSWI) has encountered many problems in China. In this study, a feasibility research on MSWI fly ash utilization as partial cement substitute in cement mortars was therefore carried out. MSWI fly ash was subjected to washing process to reduce its chlorine content (from 10.16% to 1.28%). Consequently, it was used in cement mortars. Ten percent and 20% replacement of cement by washed ash showed acceptable strength properties. In TCLP and 180-day monolithic tests, the mortars with washed ash presented a little stronger heavy metal leachability, but this fell to the blank level (mortar without washed ash) with the addition of 0.25% chelate. Therefore, this method is proposed as an environment-friendly technology to achieve a satisfactory solution for MSWI fly ash management.     

Characterization of MSWI fly ash through mineralogy and water extraction

This paper investigates the mineralogical characteristics of fresh, aged and hot water extracted MSWI fly ash for providing the baseline information of minerals stability which controls the released heavy metals into the environment. Quantitative determination of bulk phase abundance in the fresh fly ash by the XRD Rietveld refinement method provided composition levels for amorphous and crystalline phases such as potassium tetrachlorozincate (K₂ZnCl₄), gehlenite, halite, quartz, anhydrite, and feldspar. The minerals association in the fly ash is clearly unstable and subject to mineralogical reactions. The phases of K₂ZnCl₄, halite and anhydrite in the fresh fly ash were involved in hydration and dissolution/precipitation processes to form new minerals such as the Zn-bearing mineral gordaite, syngenite, gypsum and hydrocalumite. The solubility-controlling phases and extractability of heavy metals were examined in a Soxhlet hot water-extractor. Here the soluble salts were simply removed from fly ash while Ca-, Al-, Si- and SO₄²⁻-bearing hydrate minerals were precipitated from the extraction solution. Furthermore, a low release of heavy metals Zn, Pb and Cd in hot water was noticed, indicating a strong retention of the trace metals in the mineral phases remaining in the insoluble fly ash residues.     

湿法预处理对垃圾焚烧飞灰中重金属的形态及风险影响研究

以某典型城市生活垃圾焚烧飞灰为研究对象,采用X射线荧光光谱仪（XRF）、X射线衍射仪（XRD）和电感耦合等离子体光谱仪（ICP）测定了焚烧飞灰的主要成分、矿物学组成和重金属含量,探讨了湿法预处理工艺对飞灰的化学组成、矿物学形态、化学形态及风险水平的影响.结果表明,飞灰的主要化学组成为O、Ca、Cl、Na、K等,占飞灰总质量的93.54％,其次含有0.04％ ～0.68％的Zn、Pb、Cu、Cr等微量重金属元素;经过湿法预处理,飞灰中可溶性氯盐具有较好的去除效果,且几乎所有重金属元素的不稳定形态（弱酸提取态和可还原态）比例都有一定程度的减少,有效降低了重金属的毒性、生物有效性及环境风险水平.本研究有助于降低焚烧飞灰的环境风险和探寻其资源化的有效途径.     

Management of Fly Ash Through Vermicomposting: A Rational Approach

Fly ash is a by‐product of coal combustion in thermal power plants. Its generation poses several environmental problems, the most important ones being its capacity for causing pollution and the need for large storage areas to keep it out of the environment. Fly ash management remains a major concern in the 21st century; however, despite these challenges, the material has great potential for beneficial use in agriculture due to its efficacy in modifying and improving soil health and improving crop performance. Vermicomposting is an excellent technique for reducing the toxic heavy metals in fly ash through the introduction of earthworms. The activities of several earthworm species minimize the solubility of heavy metals and increase the bioavailability of major nutrient elements such as phosphorous (P) and nitrogen (N). This article provides a comprehensive review of the scope and benefits of vermiremediating fly ash, demonstrating the abilities of different species of earthworms to accumulate heavy metals and increase the availability of plant nutrients. On the basis of a literature survey, the authors have concluded that adopting vermicomposting technology promises increased, effective fly ash utilization for agricultural benefits.     

FACTORS INFLUENCING ACUTE TOXICfrY OF COAL ASH TO RAINBOW TROUT (SALMO GAIRDNERI) AND BLUEGILL SUNFISH (LEPOMIS MACROCHIRUS)1

ABSTRACT: The potentially toxic components in coal ash (ash particles, heavy metals) were evaluated in laboratory static, acute (96 hr) bioassays, both separately and in various combinations with extreme pH (5.0 and 8.5), using rainbow trout (Salmo gairdneri) and bluegifi sunfish (Lepomis macrochirus). Ash particle morphology and metal distribution anlaysis, using electron microscopy and surface-subsurface analysis by ion microscopy, showed that metals could be either clumped or evenly distributed on the surface of fly ash. Surface enrichment on fly ash particles from electrostatic precipitators, as measured by ion microscopy, was found for cadmium, copper, chromium, nickel, lead, mercury, titanium, arsenic, and selenium. Bottom (heavy) ash was not acutely toxic to either fish species at concentrations of up to 1500 mg/l total suspended solids (TSS) at pH 5.0, 7.5, or 8.5. Fly ash particles were not acutely toxic to blue-gill at levels up to 1360 mg/l TSS. Rainbow trout were highly sensitive to fly ash (25 to 60 percent mortality) at concentrations of 4.3 to 20.5 mg/I TSS when dissolved metal availability was high but were not sensitive at higher particulate concentrations (58 to 638 mg/I TSS) when dissolved metals were low. When metals were acid-leached from fly ash prior to testing, no rainbow trout mortality occurred at TSS concentrations of up to 2,350 mg/l TSS. When the percent of dissolved metal was high (e.g., 50–90 percent of the total), fish mortality was increased. Rainbow trout were nearly two orders of magnitude more sensitive than bluegill when subjected to a blend of cadmium, chromium, copper, nickel, lead, and zinc. The two species were similar in their acute sensitivity to acidic pH at levels at or below 4.0 and alkaline pH of 9.1. If the pH of coal ash effluent is contained within the range 6.0 to 9.0, acute toxicity to fish can be attributed to trace element availability from fly ash but not heavy ash. Control of holding pond and effluent pH and maximizing pond residence time are important strategies for minimizing effects of ash pond discharges on fish.     

铁尾矿路用对土壤环境质量影响及安全修复研究

为分析铁尾矿路用对道路沿线土壤环境质量影响的程度,对铁尾矿化学成分及有害物质进行测定,以秦巴山区的山地黄棕壤作为道路建设的耕土环境,把铁尾矿按70%~90%的推荐比例掺入,铁尾矿中的重金属按照最不利的全浸入式扩散进行分析,对黄棕壤中重金属含量超过限制要求的重金属进行安全修复,使铁尾矿道路沿线黄棕壤的重金属含量满足限制要求。结果表明:铁尾矿硫化物含量高达到2.89%,不满足配制混凝土的硫化物限量要求;铁尾矿路用的土壤中重金属Cr最大含量103.24 mg/kg、Cu最大含量116.4 mg/kg,国评标准污染等级均为Ⅱ级,其余重金属元素含量都在国家标准正常范围以内;高生物量的非超富集植物、细菌微生物、城市的污泥、工业粉煤灰(5%粉煤灰+50%尾矿砂+45%黄褐土)能够很好修复重金属Cr、Cu污染的土壤;含钙类物质的钝化剂处置重金属Cr、Cu污染效果好,腐殖酸、凹凸棒土、膨润土可以钝化土壤中的重金属Cu;高生物量非超富集植物、微生物钝化剂联合使用,具有更好的修复效果;当控制铁尾矿掺加比例不超过73%时,铁尾矿道路沿线的土壤重金属含量能够满足国家标准限值的要求。