焦煤与不同种类废塑料共焦化的研究

采用10g常压固定床反应器、热天平和偏光显微镜,对太钢炼焦煤中添加不同种类废塑料（如HDPE,LDPE,PP和PS）后热解的产品分布、半焦的光学特性以及热重行为进行了研究。结果表明：煤和塑料的热解温度范围和峰温的差异决定二者协同作用的程度;四种塑料的添加对净焦煤的半焦收率无明显影响;当添加HDPE、LDPE、PP时,焦煤的焦油收率增加,热解水收率下降,但添加PS时的情况正相反;除了PP外,添加其它各类的塑料能增加半焦中的光学各向异性组织的含量。     

基于热重红外联用分析的PE、PS、PVC热解机理研究

利用TGA-FTIR联用技术考察了PE、PS、PVC三种典型塑料的热解特性。结果表明,热稳定性从弱到强依次为PVC、PS、PE。PE热解反应过程为典型的一段式反应,红外光谱分析结果表明,PE热解过程为无规则断链形式,生成产物成分复杂,且随热解过程而改变,开始以饱和烃基团为主,中后期以烯烃基团为主,同时有少量炔烃;PS热解过程同样为一段式反应,红外光谱显示主要热解产物为苯乙烯单体,说明热解过程主要是苯乙烯的解聚过程;PVC热解过程较为复杂,主要分为脱氯阶段和共轭多烯重构阶段,红外光谱结果表明,产物中有芳香族化合物。脱氯过程和共轭多烯重构、环化过程在时间和空间上有重合,给二噁英类污染物的生成制造了可能。     

成都市农业土壤重金属污染特征初步研究

对成都市农业土壤中七种重金属元素Pb、Hg、Cr、As、Cu、Zn和Cd进行了测定和研究,并进行了潜在生态风险评价。结果表明,成都市农业土壤重金属元素含量分别为:Pb 77.27mg/kg,Hg 0.31 mg/kg,Cr 59.50 mg/kg,As 11.27 mg/kg,Cu 42.52 mg/kg,Zn 227.00 mg/kg,Cd0.36 mg/kg;重金属潜在的生态危害因子表明,Hg和Cd达到中等生态危害程度,Pb、As、Cu、Zn、Cr达到轻微生态危害;多种重金属的生态系统的潜在生态风险指数(RI)表明,成都市农业土壤生态危害级别为中等生态危害。     

湘潭市土壤重金属地球化学特征的统计分析

运用相关性分析、聚类分析、因子分析及直方图分析对湘潭市土壤重金属地球化学特征进行了研究。结果表明：（1）As、Cd、Cu、zn与pH值呈显著正相关;As与Cd、Cu、Ph、zn呈显著正相关;Cd与As、Cu、Pb呈显著正相关;Cu与As、Cd、Pb、Zn呈显著正相关;Pb与As、Cu、zn呈显著正相关;Zn与As、Cd、Cu、Pb呈显著正相关;Hg与其他重金属及pH值不具有显著相关关系。（2）本区重金属分为两类,即Cr、pH、As、Zn、Cu、Cd;Hg、Pb。（3）区内重金属存在3种主要元素组合即As—Cd—Cu—Pb—Zn—pH;Cr—Hg;Cd—pH;（4）区内重金属As、Cd、Cr、Cu、Hg、Zn服从正态分布。（5）通过前人对湘潭市土壤重金属进行生态地球化学评价可知,区内Cd、Hg属重污染,从统计分析结果来看,Cd随着本区pH值变化而变化,并与As、Cu、Pb相关性显著;而Hg与pH值及其它重金属之间没有必然联系。     

万宁小海表层沉积物中重金属物质的空间分布特征及生态风险分析

为了解万宁小海海域表层沉积物重金属污染状况,2020年5月在小海潟湖采集18个沉积物样品,采用电感耦合等离子体质谱法（ICP-MS）同时测定5种重金属含量,采用原子荧光光度计测定总汞和砷,并分析归纳出重金属分布特征。采用Hakanson的潜在生态风险指数法识别小海表层沉积物潜在生态风险程度,以及运用富集系数和地累积法进一步评价小海表层沉积物重金属的污染程度。结果表明：Cu、Pb、Zn、Cd、Cr、Hg和As含量平均值分别为7.26 mg/kg、27.08 mg/kg、75.06 mg/kg、0.16 mg/kg、38.43 mg/kg、0.054 mg/kg、4.66 mg/kg,均符合第一类海洋沉积物质量标准。7种元素的潜在生态风险程度依序为Hg＞Cd＞Pb＞As＞Cu＞Cr＞Zn,其中Hg和Cd为主要潜在生态危害因子,其综合潜在生态风险等级已达到中等级风险;富集系数评价和地质累积系数评价污染程度依次为：Cd＞Hg＞Pb＞Zn＞Cr＞As＞Cu;表层沉积物中TOC 含量与 Cu、Pb、Zn、Cd 和 Cr 含量具存在显著正相关,与粒度呈一定的负相关。     

生物炭改性策略及其在铬(Ⅵ)污染修复中的研究进展

六价铬（Cr（Ⅵ））是自然环境中毒性很强的重金属污染物之一,对生态系统构成严重威胁。生物炭是生物质在缺氧条件下热解产生的一种富碳固体物质,因具有比表面积大、孔结构发达和官能团丰富等优点,可作为修复Cr（Ⅵ）污染的高效吸附材料。目前,研究人员主要通过物理改性、化学改性、负载金属改性及生物改性等多种策略进一步增强生物炭对Cr（Ⅵ）的吸附能力。本文综述了近年来生物炭改性的研究进展,系统梳理了不同生物炭改性策略,比较了不同改性策略制备的生物炭对Cr（Ⅵ）污染的修复效率,分析了其作用机制,并对生物炭的改性修饰及其在实际应用中的未来发展方向进行了讨论。     

典型聚乙烯、聚丙烯、聚苯乙烯废塑料共热解初期反应特性的ReaxFF分子模拟研究

利用反应力场分子模拟(ReaxFF MD)结合反应机理自分析(AutoRMA)工具,从动力学、热解产物及热解反应过程三方面在原子层面上,探究了典型聚乙烯(PE)、聚丙烯(PP)、聚苯乙烯(PS)废塑料共热解的反应机理.结果表明,PE/PP/PS共热解的动力学参数可通过C–C键和C–H键断裂的活化能加权求和(即Char ...     

固体添加剂对垃圾掺烧污泥焚烧飞灰高温过程中重金属挥发特性的影响

在研究垃圾与污泥掺烧后焚烧飞灰中重金属浸出特征的基础上,重点研究了飞灰在1 000 ℃条件下高温处置过程中重金属(Cu、Zn 、Pb、Cd)随不同停留时间的挥发特性及添加剂(CaO、Al₂O₃、SiO₂、高岭土、粉煤灰)对重金属转化与挥发特性的影响。研究结果表明,飞灰中重金属Zn、Pb、Mn含量较高,Ni的含量较低,而毒性较大的Cd达到29.4 mg/kg。浸出液中七种金属都满足危险废物鉴别标准(GB5085.3-1996),并且重金属的浸出浓度受浸取时间及浸取液pH值影响较大。在同样的高温处置条件下,焚烧飞灰中不同重金属的挥发特性有较大的差别。其中,Pb表现出易挥发的特性,其挥发率超过80%,而Cu挥发性较小,其挥发率小于30%。综合来看,飞灰中重金属的挥发性大小依次为Pb>Cd>Zn>Cu。飞灰中添加Al₂O₃和高岭土可以抑制Cd的挥发,添加Al₂O₃后Pb的挥发率有所减少,添加SiO₂、CaO、高岭土、粉煤灰均使Zn的挥发率降低,而对Cu的挥发率没有抑制作用,这与飞灰中高Cl含量及各痕量元素化合物对固体添加剂活性位选择性的竞争吸附有关。     

污泥中典型氨基酸热解生成NOx前驱体的反应机理研究

污泥热解是实现污泥减量化、无害化和资源化的重要技术.城市污泥含氮量高,在热解过程中含氮物质会转化成NO_x前驱体（NH₃,HCN）,限制了污泥热解技术的应用和推广.本研究选取污泥中氮的基本存在单元甘氨酸和谷氨酸作为污泥的含氮模型化合物,采用B3LYP方法和6-31++G（d,p）基组,探究了甘氨酸和谷氨酸热解形成NO_x前驱体的机理.结果表明,甘氨酸热解生成NO_x前驱体有2种反应方式,一是甘氨酸发生脱氨反应生成NH₃;二是甘氨酸发生脱水反应生成甘氨酸酐（DKP）.谷氨酸在热解过程中直接发生脱氨反应生成NH₃.同时发现NH₃和HCN存在竞争关系.根据生成NH₃和HCN的难易程度可知甘氨酸和谷氨酸热解得到NO_x的前驱体主要是NH₃,并根据不同氨基酸热解时的脱基团反应机理提出了加入水蒸气的建议来减轻污泥热解中氮氧化物的产生.     

冶炼厂烟囱降尘农田土壤重金属含量及潜在生态风险评价

摘要：为了研究冶炼厂下风向烟囱降尘对农田土壤重金属污染影响程度,以济源市某一冶炼厂工业烟囱下风向降尘覆盖农田土壤为研究对象,依次对距离该厂烟囱大约为750m-3000m的7个农田研究区（P1-P7）土壤中重金属（Hg、As、Pb、Cd、Cu、Zn、Ni、Cr、）含量进行污染状况分析,采用了单项潜在生态风险指数法和综合潜在生态风险指数法对冶炼厂下风向烟囱降尘土壤中重金属的潜在生态风险进行评价。结果表明：在3 km2研究区域范围内,距离冶炼厂越近土壤重金属含量越高,Pb、Cd为重度污染,超过了《土壤环境质量农用地土壤污染风险管控标准》（GB15618-2018）农用地土壤污染风险管制值的1.2倍,距离冶炼厂烟囱下风向P1区土壤中重金属As、Pb、Cd、Cu、Zn超过土壤环境质量农用地土壤风险筛选值,Cd 在浓度值均超过农用土壤污染风险管制值1.8倍,As元素平均浓度值超农用土壤污染风险管制值1.7倍,Pb、Cu和Zn污染较严重,Cd、Hg对综合指数（RI）贡献值较大分别为68.63和22.4。单项潜在生态风险指数评价结果显示Cd存在极严重的潜在生态风险,Pb、Cu存在较严重潜在生态风险,冶炼厂下风向土壤中综合潜在生态风险指数评价显示,冶炼厂下风向降尘土壤重金属具有较强的生态风险。     

Comparison of thermal degradation products from real municipal waste plastic and model mixed plastics

The thermal degradation of real municipal waste plastic (MWP) obtained from Sapporo, Japan and model mixed plastics was carried out at 430 °C in atmospheric pressure by batch operation. The chlorinated hydrocarbons found in PE/PP/PS/PVC [poly(ethylene)/poly(propylene)/poly(styrene)/poly(vinyl chloride)] degradation liquid products were also observed in PE/PP/PS/PVC/PET (poly(ethylene terephalate)) and MWP degradation liquid products. The presence of PET in MWP produced the additional chlorinated hydrocarbons, which are similar to the chlorinated hydrocarbons observed during the PE/PP/PS/PVC/PET degradation liquid products. In addition, the presence of PET facilitated the formation of more organic chlorine content in liquid products and drastic decrease in the formation of inorganic chlorine content.     

城市生活垃圾焚烧飞灰重金属的浸出特性

对用流化床焚烧炉混烧垃圾和煤的布袋飞灰进行了重金属的TCLP(Toxicity Characteristic Leaching Procedure)浸出特性实验，探讨了液固比、初始pH值及浸出时间对飞灰中重金属Pb、Cr、Cd、Ni、Cu、Zn的浸出影响。结果表明，重金属的浸出量都随着液固比的增加而增加，其中Cr、Cu一般呈上升趋势，Cd、Ni、Zn在液固比大于20时曲线变化较平缓，Pb的浸出规律比较特殊，有一个明显的波峰和波谷。重金属在浸取液的pH≤2.90时的浸出浓度远远大于pH≥4.03时的浸出浓度。Pb、Cr、Zn随着浸出时间的增加，浸出浓度下降，而Cd、Ni上升，Cu是先上升后下降。在液固比、初始pH值及浸出时间这三个影响因素中，pH值对重金属的浸出影响较大，重金属在酸性环境下较易浸出。     

The effect of PVC on thermal and catalytic degradation of polyethylene, polypropylene and polystyrene by a continuous flow reactor

A continuous flow reactor was operated at atmospheric pressure and feed rate of 0–1.5 kg h⁻¹ for degradation of PE, PP and PS in presence of 1–2 wt% PVC. The degradation temperatures were between 360 and 440 °C depending on the feeding material. The influence of PVC, temperature and silica-alumina catalysts on degradation behavior and on the properties of the products was studied and discussed. Different effects were observed for binary PE/PVC, PP/PVC, PS/PVC and complex PE/PP/PS/PVC mixtures due to specific interactions between PVC and each hydrocarbon polyolefin. Silica-alumina catalysts decreased the Cl concentration in oils but it seems to generate high amounts of Cl-containing organic compounds in gases.     

Controlled pyrolysis of polyethylene/polypropylene/polystyrene mixed plastics with high impact polystyrene containing flame retardant: Effect of decabromo diphenylethane (DDE)

The pyrolysis of polyethylene(PE)/polypropylene(PP)/polystyrene(PS) mixed with high impact polystyrene (HIPS-Br) containing decabromo diphenylethane (DDE) as a brominated flame retardant with antimony trioxide as a synergist was performed under controlled temperature programmed pyrolysis (two steps) conditions to understand the decomposition behaviour and evolution of brominated hydrocarbons from flame-retardant additives. The liquid products were extensively analyzed by gas chromatographs equipped with FID, ECD, MSD, TCD, AED and FT-IR. The solid residue samples were analyzed by powder X-ray diffraction and combustion followed by ion-chromatography. The controlled pyrolysis of PE/PP/PS/HIPS-Br significantly affected the decomposition behaviour of HIPS-Br and subsequently the formation of decomposition products. GC/ECD analysis confirmed that the brominated hydrocarbons were concentrated in step 1 liquid products leaving less brominated hydrocarbons in the step 2 liquid products, similar to the decabromo diphenyl ether flame retardant containing mixed plastics. The yield of liquid products in step 1 from 3P/DDE-Sb(5) was 5 wt% and from 3P/DDE-Sb(0) was 2.4 wt%. The presence of antimony in the DDE containing plastics affected the yield of liquid, gas and residue products. ECD analysis showed that the presence of antimony increased the Br containing hydrocarbons and step 1 has 3-4 times higher brominated compounds than step 2 hydrocarbons in both the samples.     

Estimation of environmental mobility of heavy metals using a sequential leaching of particulate material emitted from an opencast chrome mine complex

A four-stage sequential leaching procedure was applied to assess the bioavailability and environmental mobility of heavy metals (Cr, Fe, Cu, Ni and Cd) in total suspended particulate (TSP) material emitted from an opencast chrome mine complex (Kemi, Northern Finland). TSP material was collected on glass fibre filters by a high-volume sampler, and a sequential leaching procedure was used to determine the distribution of heavy metals between the water-soluble fraction (H2O), environmentally mobile fraction (CH3COONH4), the fraction bound to carbonate and oxides (HONH3Cl + CH3COOH), and the fraction bound to silicates and organic matter, that is the environmentally immobile fraction (HNO3 + HF + HCl). The sequential leaching procedure was also applied to the certified reference materials VKI (QC Loam Soil A) and PACS-2 (Marine Sediment) to evaluate the accuracy and reproducibility of the leaching procedure. The heavy metals were determined by graphite furnace atomic absorption spectrometry (GFAAS) and flame atomic absorption spectrometry (FAAS). The concentrations of metals in the water-soluble fraction (H2O) decreased in the order Fe >Cu >Cr >Ni >Cd, and in the environmentally mobile fraction (CH3COONH4) in the order Cu >Fe >Ni >Cr >Cd.     

Pyrolysis of mixed polyolefins in a fluidised-bed reactor and on a pyro-GC/MS to yield aliphatic waxes

Polyolefins (PE, PP and PS) were pyrolysed in a fluidised-bed reactor on kilogram scale at 510°C. Pyrolysis products were analysed with GC, GC/MS and other methods. It was shown that valuable products, mostly aliphatic waxes, are received from polyolefins. It was also investigated if mixtures of different polyolefins (PE, PP, PS) interact with each other in fluidised bed pyrolysis yielding different pyrolysis products than received from the pure, individual polyolefins. The same polymer mixtures were also analysed using a pyro-GC/MS-device.     

煎煮对几种特色南药中重金属元素含量和形态影响

考察了几种特色南药中重金属(Cd,Cr,Cu,Fe,Mn,Ni,Pb,Sr,Zn)的含量状况,并采用形态连续萃取法分析重金属在药材中的形态分布,研究了药材煎煮时药材中重金属的释放及煎煮过程对药材中重金属形态分布的影响。结果表明,几种南药中Cr,Pb,Zn的含量较高,且巴戟天中的重金属总量高于限量标准;原药材中Cr,Cu,Mn,Ni,Pb和Zn主要存在于有机态和残留态,Fe和Sr主要存在于残留态。煎煮使南药中大量重金属迁移到药汤中;药汤中Cu,Mn,Cr,Pb和Zn主要来自于其在药材中的可交换态、碳酸盐结合态和有机态,而药汤中Sr,Ni和Fe不仅包含其非残留态,更多来自于它们的残留态。为减少药汤中重金属,对于Cu,Mn,Cr,Pb和Zn既要控制在药材中的总量,且需降低它们在药材中的非残留态含量;对于Fe,Ni和Sr则主要是控制其在药材中的总量。     

Optimizing pyrolysis temperature of contaminated rice straw biochar: Heavy metal(loid) deportment,properties evolution,and Pb adsorption/immobilization

Pyrolysis of rice straw (RS), a popular method for producing biochar, effectively treats heavy metal(loid)-contaminated RS. Here, we carried out this process at different temperatures and investigated the deportment of heavy metal(loid)s and the property evolution of biochars. Also, the optimal pyrolysis temperature for Pb adsorption and immobilization was studied. We observed that increasing the temperature could volatilize the heavy metal(loid)s. Cd was the most volatile metal therein, followed by As, while Ni, Cu, and Pb were relatively refractory. More than 75% of the remaining heavy metal(loid)s were non-exchangeable fractions at 700 °C, significantly reducing the environmental risk during subsequent application. Meanwhile, higher pyrolysis temperature resulted in higher pH values, higher surface areas, and stronger Pb adsorption capacity of RS biochars. The maximum adsorption capacity (Q_m) of biochars was in the order of BC300 (77.2 mg·g^?1) < BC500 (137.2 mg·g^?1) < BC700 (222.6 mg·g^?1). Besides, high-temperature biochar could significantly reduce the vertical Pb migration. And BC700 increased the fraction of residual Pb from 39.7% to 44.0% in the soil under the acid rain leaching condition. Therefore, we propose that the heavy metal(loid)-contaminated RS biochar produced at 700 °C might be more suitable for the remediation of soil heavily polluted in the Pb-smelting area.