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首页> 外文期刊>Waste Management >Classification and characterisation of SRF produced from different flows of processed MSW in the Navarra region and its co-combustion performance with olive tree pruning residues
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Classification and characterisation of SRF produced from different flows of processed MSW in the Navarra region and its co-combustion performance with olive tree pruning residues

机译:纳瓦拉地区不同处理的城市固体废弃物产生的SRF的分类,表征及其与橄榄树修剪残留物的共燃性能

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摘要

The scope of this work is to study the co-combustion of a solid recovered fuel (SRF) produced from household wastes and packaging wastes recovered from selective collection (SC) in the autonomous community of Navarra, located in the northeast of Spain. The municipal solid waste (MSW) is subjected to a mechanical biological treatment (MBT) in order to stabilize the organic matter and recover the recyclable materials as it is done for packaging wastes. Afterwards, rejects from this treatment plant were preconditioned and compressed by a pelletizing process to produce a secondary fuel according to quality and classification criteria of EN 15359, producing the so-called SRF. A fuel characterisation was carried out according to CEN standards and the SRF was classified as follows: NCV 2; Cl 3; Hg 1. SRF pellets were cofired with residual biomass pellets from olive tree pruning (OTP) in a bubbling fluidised bed combustor, as an option of energy recovery. The mixture of fuels, with a mixing ratio close to 50% by weight, showed a significant calorific value of 18.25 MJ/kg at 8% of moisture content. In addition, elemental composition of the mixture based on nitrogen (N), sulphur (S) and chlorine (Cl) (1% N, 0.2% S and 0.4% Cl) was not far from some herbaceous biomasses. The co-combustion showed good results as an energy recovery technology because of the synergies of both fuels, improving notably the combustion conditions and reducing significantly CO concentration, regarding to the combustion of OTP, though other contaminants such as NO_x and HC1 increased. During eight hours of stable operation, the concentration of dioxins and furans was measured obtaining a value of 7.68 ng/Nm3 (toxic equivalence: i-TEQ of 0.33 ng/Nm~3). Proportions of SRF lower than 50% in the mixtures should be tested in order to cut down the emissions of these pollutants, or an abatement system for organochloride compounds may be required.
机译:这项工作的范围是在西班牙东北部的纳瓦拉自治社区研究由家庭废物产生的固体回收燃料(SRF)和从选择性收集(SC)回收的包装废物的共燃烧。对市政固体废物(MSW)进行机械生物处理(MBT),以便在处理包装废物时稳定有机物并回收可循环利用的材料。之后,根据EN 15359的质量和分类标准,对来自该处理厂的废料进行预处理和压片工艺,以生产二次燃料,从而生产出所谓的SRF。根据CEN标准进行了燃料特性分析,SRF分为以下类别:NCV 2; NV 2; NV 2; NV 2。 Cl 3;汞1.将SRF颗粒与来自橄榄树修剪(OTP)的残留生物质颗粒在鼓泡的流化床燃烧器中共烧,作为能量回收的一种选择。混合比接近50%(重量)的燃料混合物在8%的水分含量下显示出18.25 MJ / kg的显着热值。此外,基于氮(N),硫(S)和氯(Cl)(1%N,0.2%S和0.4%Cl)的混合物的元素组成与一些草本生物质相距不远。由于两种燃料的协同作用,共燃烧作为一种能量回收技术显示出良好的效果,尽管与其他污染物如NO_x和HC1相比增加,但与OTP的燃烧相比,这两种燃料的协同作用显着改善了燃烧条件并显着降低了CO浓度。在稳定运行的八小时内,测得的二恶英和呋喃浓度为7.68 ng / Nm3(毒性当量:i-TEQ为0.33 ng / Nm〜3)。为了减少这些污染物的排放,应测试混合物中SRF的比例低于50%,或者可能需要减少有机氯化物的系统。

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