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脱矿对食物垃圾生物炭共燃的影响:碱金属和碱土金属及氯的行为。

Effects of demineralization on food waste biochar for co-firing: Behaviors of alkali and alkaline earth metals and chlorine.

机构信息

Department of Environmental Research, Korea Institute of Civil Engineering and Building Technology, Goyang- daero 283, Ilsanseo-gu Goyang-si, Gyeonggi-do 10223, Republic of Korea.

Department of Environmental Research, Korea Institute of Civil Engineering and Building Technology, Goyang- daero 283, Ilsanseo-gu Goyang-si, Gyeonggi-do 10223, Republic of Korea.

出版信息

Waste Manag. 2022 Jan 1;137:190-199. doi: 10.1016/j.wasman.2021.10.040. Epub 2021 Nov 15.

Abstract

A significant amount of chlorine, and alkali and alkaline earth metal (AAEM) in food waste has been a major limitation to the utilization of food waste as fuel. The present study aims to investigate the behavior of chlorine and AAEM in food waste biochar during pyrolysis, demineralization, and combustion. Food waste compost (FWC) and food waste feedstock (FWF) were selected as raw materials. Three different pyrolysis temperatures from 300 to 500 °C and two demineralization processes, water and COsaturated water, were employed. As the pyrolysis temperature increased, crystallized salt was removed through demineralization, which further increased the heating value. Effective removal of chlorine was demonstrated in both demineralization methods. During demineralization, re-adsorption of Ca on food waste biochar occurred, which was alleviated by CO-water demineralization. The total amounts of volatilized Cl and AAEM after CO-water demineralization were reduced by 74.79-99.38% for FWF and 98.34-99.9% for FWC compared to raw biochar. Furthermore, slagging and fouling potentials for all food waste biochar samples were estimated using various indices. The proposed behavior of Cl and AAEM in food waste biochar during various fabrication conditions provides insight into how food waste biochar can be applied in thermos-electric power plant for co-firing with coal.

摘要

食物垃圾中的大量氯、碱和碱土金属(AAEM)一直是将食物垃圾作为燃料利用的主要限制因素。本研究旨在探讨食物垃圾生物炭在热解、脱盐和燃烧过程中氯和 AAEM 的行为。选择食物垃圾堆肥(FWC)和食物垃圾原料(FWF)作为原料。采用 300 至 500°C 的三种不同热解温度和两种脱盐工艺,即水和 CO2饱和水。随着热解温度的升高,结晶盐通过脱盐去除,从而进一步提高了热值。两种脱盐方法均能有效去除氯。在脱盐过程中,Ca 在食物垃圾生物炭上重新吸附,而 CO2水脱盐缓解了这一问题。与原始生物炭相比,CO2 水脱盐后 FWF 和 FWC 的总挥发 Cl 和 AAEM 量分别减少了 74.79-99.38%和 98.34-99.9%。此外,还使用各种指标估算了所有食物垃圾生物炭样品的结渣和积灰潜力。在各种制造条件下食物垃圾生物炭中氯和 AAEM 的行为提供了如何在热电联产厂中与煤共烧应用食物垃圾生物炭的见解。

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