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PYROLYSIS AND GASIFICATION OF LIGNOCELLULOSIC SOLID WASTES FOR ACTIVATED-CARBON PRODUCTION.

机译:用于活性炭生产的木质纤维素固体废物的热解和气化。

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摘要

This work was conceived as a preliminary experimental evaluation of the technical feasibility of converting solid-waste materials into powdered activated-carbon adsorbents suitable for wastewater treatment. Lignocellulosic materials (i.e. natural or modified plant tissues) were selected as the class of solid wastes to be studied. The production process under consideration was pyrolysis of the raw material (precursor) to form a carbonaceous char followed by "activation," or expansion of the pore system of the char by gasification with carbon dioxide at 900(DEGREES)C. The primary focus of the research was the influence of the conditions during pyrolysis (heating rate, final temperature) on the yield and porosity of the chars and final activated-carbon products. The pyrolysis conditions investigated were heating rates of 1, 15 and greater than 100(DEGREES)C/min and final temperatures of 500(DEGREES), 700(DEGREES) and 900(DEGREES)C.;Selected chars prepared by pyrolysis at the lower heating rates (1 and 15(DEGREES)C/min) to 500(DEGREES), 700(DEGREES), and 900(DEGREES)C were gasified for various lengths of time in a CO(,2) atmosphere at 900(DEGREES)C. Pore-volume analysis of the final products was performed by nitrogen adsorption 77K and mercury porosimetry. The rate of mass loss and development of the pore system during gasification was found to vary with prior pyrolysis conditions: e.g., low heating rate or longer exposure to high temperature during pyrolysis led to lower rate of gasification. However, the pore volume developed for a given mass loss due to gasification reactions was independent of prior pyrolysis conditions. The latter result was apparently due to the similarity of the pore systems present in the chars immediately prior to the onset of the gasification reactions, i.e. after the char had heated to the gasification temperature. Because the heating rate during pyrolysis below 500(DEGREES)C was the critical factor controlling char yield at 900(DEGREES)C, the final yield of activated carbon (i.e. gasified char) of a specified pore volume was also influenced mainly by the pyrolysis heating rate below 500(DEGREES)C.;Char yield was found to be determined by precursor composition (percent lignin, holocellulose, etc.) and pyrolysis heating rate. Both factors were found to exert their main influence on char yield during pyrolysis below 500(DEGREES)C. Neither factor was found to have a significant effect on the open micropore volume in the char (i.e., that measurable by CO(,2) adsorption at 298K). The fact that the absolute volume of open micropores did not change significantly as temperatures rose from 500(DEGREES)C to 900(DEGREES)C suggested that the char microstructure was effectively established at or below 500(DEGREES)C.
机译:这项工作被认为是对将固体废物转化为适合废水处理的粉末状活性炭吸附剂的技术可行性的初步实验评估。选择木质纤维素材料(即天然或改性的植物组织)作为要研究的固体废物类别。所考虑的生产过程是将原料(前体)热解形成碳质炭,然后“活化”或通过在900°C下用二氧化碳气化使炭的孔系统膨胀。研究的主要重点是热解条件(加热速率,最终温度)对焦炭和最终活性炭产品的产率和孔隙率的影响。所研究的热解条件是加热速率为1,15和大于100(DEGREES)C / min,最终温度为500(DEGREES),700(DEGREES)和900(DEGREES)C。加热速率(1和15(DEGREES)C / min)到500(DEGREES),700(DEGREES)和900(DEGREES)C在900(DEGREES)的CO(,2)气氛中气化不同的时间C。最终产品的孔体积分析是通过氮气吸附77K和汞孔隙率法进行的。发现气化期间质量损失的速率和孔系统的发展随先前的热解条件而变化:例如,低的加热速率或热解期间长时间暴露于高温导致较低的气化速率。然而,由于气化反应而在给定质量损失下形成的孔体积与先前的热解条件无关。后一结果显然是由于在气化反应开始之前即炭加热到气化温度之后立即存在于炭中的孔系统的相似性。因为热解过程中加热速率低于500(DEGREES)C是控制炭在900(DEGREES)C产率的关键因素,所以在指定孔体积下活性炭(即气化焦炭)的最终产率也主要受到热解加热的影响。炭的产率由前体组成(木质素,全纤维素等的百分数)和热解加热速率决定。发现这两个因素在低于500(DEGREES)C的热解过程中都对焦炭产率产生主要影响。均未发现这两个因素对焦炭中的开放微孔体积有显着影响(即,可以通过在298K吸附CO(,2)来测量)。随着温度从500(DEGREES)C升高到900(DEGREES)C,开放微孔的绝对体积没有明显变化的事实表明炭的微观结构有效地建立在500(DEGREES)C或以下。

著录项

  • 作者

    MACKAY, DOUGLAS MCDUFF.;

  • 作者单位

    Stanford University.;

  • 授予单位 Stanford University.;
  • 学科 Engineering Sanitary and Municipal.
  • 学位 Ph.D.
  • 年度 1981
  • 页码 232 p.
  • 总页数 232
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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