电石渣脱硫运行存在问题的探讨

石灰石—石膏湿法脱硫技术是我国燃煤电厂烟气脱硫的首选工艺,以电石渣代替石灰石进行烟气脱硫,可以达到废物利用、循环经济的目的。分析了以电石渣为脱硫剂时,系统运行存在的问题,并提出相关建议。     

小龙谭电厂冲渣水闭式循环系统改造工程

分析了小龙谭电厂不回收系统改造前系统不合理的原因及渣水水质特点,详细介绍了改造成闭式循环后的回收工艺,并作了简要经济分析。     

脱硫用电石渣的重金属浸出特性及其对环境的影响

针对电厂用脱硫剂电石渣,分析了其基本组成及重金属浸出特性,为电厂脱硫设施的参数设计和环境影响评价提供依据和参考。研究结果表明,脱硫用电石渣主要成分为Ca（OH）2,含量在40%～50%之间;在8种重金属的含量中,只有Cd的含量超出土壤质量三级标准的要求,基本不会对土壤造成污染。浸出毒性试验表明,电石渣及其脱硫产物属于非危险废物,其各种重金属的浸出浓度主要受其本身重金属含量和最终pH的影响,这种影响在Pb、Cu和Cd上表现得较为突出,酸性环境下更有利于他们的浸出;碱性环境下有利于Pb和Ni的浸出。     

铬渣钡渣代替天然砂制作混凝土的研究

用铬渣、钡渣代替部分天然砂制作强度等级为C15的普通混凝土,混凝土的强度等级与钡渣、铬渣的加入量关系较大.用PO32.5标号水泥,铬、钡渣的质量代替砂子质量的50%时,混凝土的抗压强度达到18.9MPa,比普通混凝土设计的抗压强度提高26%,混凝土的收缩量为1/300,优于国家标准,对混凝土作浸出毒性试验,Cr6+和Ba2+都远小于国家规定的标准值.     

钡渣的综合利用

钡渣的综合利用１前言锦州炼油厂在生产聚异丁烯硫磷化钡盐的过程中，每年约产生４００ｔ含钡废渣。钡渣有两种：一种是干渣，是由Ｔ１０８产品沉降罐排出的；另一种是稀渣，是由离心分离机分离而出的。干渣量占总渣量的６０％－７０％，稀渣量占总渣量的３０％－４０％。...     

钡渣用于三相流化床烟气脱硫

提出了在三相流化床内用钡渣进行烟气脱硫的方法。分析了钡渣湿法脱硫原理，并进行了工艺改进实验，对两种不同溶渣方式工艺进行了静态和动态模拟实验，考察了两种方式的离子浓度和吸收容量等因素。实验表明，将渣先和水混合再用脱硫废水调整水质、脱硫塔进水pH在7．5左右时有利于系统的稳定运行。当液气比为2．88、气速为9．5m／s时，脱硫效率可以达到85％以上。这种方法可大大降低脱硫成本，实现以废治废。     

铬渣的无害化处理和综合利用

铬渣产量大、毒性剧烈,是严重污染生态环境和危害人类健康的危险废物.介绍了铬渣各种无害化处理方法的解毒机理、工艺过程和应用实践,阐述了对铬渣进行综合利用的途径,并就铬渣的防治前景提出了建议.     

用钡渣制取硫酸钡

用盐酸浸取钡渣，所得的氯化钡溶液再和硫酸反庆，得到硫酸钡沉淀，母液返回去浸取钡渣。浸取钡渣的适宜条件为：浸取时间５０ｍｉｎ、ｐＨ２－３、钡渣粒度１２０目、浸取温度４０－４５℃、液固比３：１。     

酸渣制备无水硫酸钠

采用炼油厂酸渣经水稀释后,添加含钠化合物进行中和反应,制备无水Na_2SO_4.最佳工艺条件为:将酸渣用水稀释20倍,按n(Na_2CO_3):n(SO_4~(2-))=1.10或n(NaOH):n(SO_4~(2-))=1.20的比例加入Na_2CO_3,溶液或NaOH溶液,油水分离去除油相后蒸发、干燥,在650℃下灼烧后溶解、过滤、蒸发、结晶,得到Na_2SO_4产品.NaCO_3法可将酸渣中约78%的SO_4~(2-)转化到产品Na_2SO_4中;NaOH法可将酸渣中约66%的SO_4~(2-)转化到产品Na_2SO_4中.制备的无水Na_2SO_4产品均达到GB/T6009-2003<工业无水硫酸钠>二类标准.     

湿法排渣在磷酸生产中的应用

磷酸生产中产生的废渣量大，生产1t磷酸产生7t磷石膏(湿渣)，因此，排渣自然成为磷酸生产中的一项大问题。排渣方式有车辆运输、皮带传输、管道或沟道水力输送等，采用哪种方式，要根据实际情况而定。     

用铬渣作水泥矿化剂

介绍了铬渣作水泥矿化剂的原理和生产控制条件,通过经济和环境效益分析证明,铬渣作水泥矿化剂确实是一种处理和利用铬渣的好方法。     

Pyrolysis characteristics of bean dregs and in situ visualization of pyrolysis transformation

Biomass is an important renewable and sustainable source of energy. Waste products from biomass are considered as attractive feedstocks for the production of fuel. This work deals with the pyrolysis of bean dregs, a biomass waste from soybean processing industry. A technique has been developed to study bean dregs pyrolysis by in situ visualization of bean dregs transformation in a quartz capillary under a microscope using a charge-coupled device (CCD) camera monitoring system. The technique enables us to observe directly the processes and temperatures of bean dregs transformation during pyrolysis. In situ visualization of reaction revealed that how oily liquids are generated and expulsed concurrently from bean dregs during pyrolysis. Pyrolysis characteristics were investigated under a highly purified N₂ atmosphere using a thermogravimetric analyzer from room temperature to 800 °C at different heating rates of 10, 30 and 50 °C/min. The results showed that three stages appeared in this thermal degradation process. The initial decomposition temperature and the peak shifted towards higher temperature with an increase in heating rate. Kinetic parameters in terms of apparent activation energy and pre-exponential factor were determined.     

Using a second-order polynomial model to determine the optimum dregs/bark ratio for industrial-biosolid composting: the initial conditioning stage.

Increasing pulp industry production has generated additional solid waste (i.e. biological sludge, dregs, etc.) and therefore an increasing disposal problem. On the other hand, composting is emerging as an interesting alternative for the disposal of residues. The objective of this study was to evaluate the physical and chemical properties of sludge, dregs and bark and the effect on their initial conditioning stage prior to composting, using pine chips as bulking agent. After their characterization, these solid wastes were combined in different mixture proportions defined by a 32 experimental design based on the response surface methodology (RSM), in which 18 observations were required for the independent variables (dregs and bark) and the C: N ratio, moisture content and pH were the dependent variables. The characterization indicated that the dregs have alkaline properties with the presence of some essential plant nutrients, such as phosphorous (0.37%), potassium (0.76%), magnesium (1.4%) and calcium (27%). The combination of the macronutrients (phosphorous: 0.39%, potassium: 0.24%, calcium: 1.7%, magnesium: 0.44%) and micronutrients such as ferrous material (0.47%) and zinc (0.12%) found in the sludge suggest a promising alternative despite the potential problem due to the high pH of the dregs. The RSM design indicated a feasible region that satisfied the optimal dregs: bark ratio of 0.25 without exceeding the addition of 12.5% dregs, due to the alkaline properties of these inorganic wastes and the quadratic influence over the C:N ratio. The experimental results indicated that the composting process of dregs, bark and sludge is technically suitable, although the use of a rapidly available C source needs to be evaluated.