首页> 外文OA文献 >Destruction and formation of PCDD/Fs in a fluidised bed combustor co-incinerating automotive shredder residue with refuse derived fuel and wastewater treatment sludge
【2h】

Destruction and formation of PCDD/Fs in a fluidised bed combustor co-incinerating automotive shredder residue with refuse derived fuel and wastewater treatment sludge

机译:通过垃圾衍生燃料和废水处理污泥的流化床燃烧器中的破坏和形成PCDD / FS的PCDD / FS

代理获取
本网站仅为用户提供外文OA文献查询和代理获取服务,本网站没有原文。下单后我们将采用程序或人工为您竭诚获取高质量的原文,但由于OA文献来源多样且变更频繁,仍可能出现获取不到、文献不完整或与标题不符等情况,如果获取不到我们将提供退款服务。请知悉。

摘要

During an eight day trial automotive shredder residue (ASR) was added to the usual waste feed of a Fluidized Bed Combustor (FBC) for waste-to-energy conversion; the input waste mix consisted of 25% ASR, 25% refuse-derived fuel (RDF) and 50% wastewater treatment (WWT) sludge. All inputs and outputs were sampled and the concentration of the 17 PCDD/Fs with TEF-values was determined in order to obtain "PCDD/F fingerprints". The ASR contained approximately 9000 ng PCDD/Fs/kg(DW), six times more than the RDF and 10 times more than the WWT sludge. The fingerprint of ASR and RDF was dominated by HpCDD and OCDD, which accounted for 90% of the total PDDD/F content, whereas the WWT sludge contained relatively more HpCDFs and OCDF (together 70%). The flue gas cleaning residue (FGCR) and fly and boiler ash contained approximately 30,000 and 2500 ng PCDD/Fs/kg(DW), respectively. The fingerprints of these outputs were also dominated by HpCDFs and OCDF. The bottom ash contained only OCDD and OCDF. in total 8 ng PCDD/Fs/kg(DW). From the comparison of the bottom ash fingerprints with the fingerprints of the other output fractions and of the inputs, it could be concluded that the PCDD/Fs in the waste were destroyed and new PCDD/Fs were formed in the post combustion process by de novo synthesis. During the ASR-co-incineration, the PCDD/F congener concentrations in the fly and boiler ash, FGCR and flue gas were 1.25-10 times higher compared to the same output fractions generated during incineration of the usual waste mix (70% RDF and 30% WWT sludge). The concentration of the higher chlorinated PCDD/Fs increased most. As these congeners have the lowest TEF-factors, the total PCDD/F output, expressed in kg TEQ/year, of the FBC did not increase significantly when ASR was co-incinerated. Due to the relatively high copper levels in the ASR, the copper concentrations in the FBCs outputs increased. As copper catalysis the de novo syntheses, this could explain the increase in PCDD/F concentrations in these outputs. (C) 2011 Elsevier B.V. All rights reserved.
机译:在一个八天的试用汽车粉碎残渣(ASR)中的溶液加入到一个流化床燃烧(FBC)为废物转化为能量转换的一般废物进料;输入的废物混合物由25%ASR,25%的垃圾衍生燃料(RDF)和50%的废水处理(WWT)污泥。所有输入和输出进行取样和17 PCDD的浓度/与TEF-Fs的值,以获得“PCDD / F指纹”进行了测定。的ASR含有约9000纳克的PCDD / F /公斤(DW),比RDF和10倍超过WWT污泥多六倍。 ASR和RDF的指纹是由HpCDD和OCDD,其占总PDDD / F含量的90%,而WWT污泥包含相对更HpCDFs和OCDF(一起70%)为主。烟道气净化残余物(FGCR)和飞和锅炉灰含有约30000和2500毫微克的PCDD / F /公斤(DW),分别。这些输出的指纹也受到HpCDFs和OCDF为主。底灰中只有OCDD和OCDF。在总共8纳克PCDD / FS /千克(DW)。从与其它输出馏分和输入的指纹底灰指纹的比较,可以得出结论的是,PCDD / Fs的在废物被摧毁,新PCDD通过从头形成在后燃烧过程中/ Fs的合成。在ASR - 共 - 焚烧,在飞和锅炉灰的PCDD / F同类的浓度,FGCR和烟道气是1.25-10倍通常的废物混合物的焚化过程中产生的相同的输出级分更高(70%RDF和30%WWT污泥)。更高氯化PCDD的浓度/ Fs的最增加。由于这些同系具有最低的TEF-因素,总PCDD / F输出,以kg TEQ /年表示,根据FBC并没有显著当ASR被共同焚烧增加。由于ASR相对高的铜含量,在FBCS输出铜的浓度增加。铜催化中从头合成,这可以解释在这些输出PCDD / F浓度的增加。 (C)2011爱思唯尔B.V.保留所有权利。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
代理获取

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号