• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

洗涤时间、洗涤温度和颗粒尺寸对稻壳燃烧及灰分形成特性影响的实验研究

Experimental Study on the Effects of Washing Time, Washing Temperature, and Particle Size on the Combustion and Ash Formation Characteristics of Rice Husk.

作者信息

Yang Shuo, Luo Jintao, Gao Yu, Wang Shaohui, Zhang Yupeng, Wang Yuhang, Ge Pushi, Li Wanqi, Zheng Yunyi, Cui Jie, Fu Yudong, Pan Honggang

机构信息

Laboratory of Liaoning Province for Clean Combustion Power Generation and Heating Supply Technology, Shenyang Institute of Engineering, Shenyang 110136, China.

出版信息

ACS Omega. 2024 Dec 11;9(51):50705-50719. doi: 10.1021/acsomega.4c08820. eCollection 2024 Dec 24.

DOI:10.1021/acsomega.4c08820
PMID:39741802
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11683596/
Abstract

There are many problems in the direct combustion of biomass, such as low combustion efficiency and easy slagging. In this paper, rice husk (RH) was taken as the research object, and the effects of different washing pretreatment conditions (washing time (WTI), washing temperature (WTE), and particle size) on the combustion characteristics and ash formation characteristics were discussed. The results show that the combustion characteristics of RH were significantly coupling-affected by the WTE and WTI, and the comprehensive characteristics of volatile release were significantly coupling-affected by the particle size and WTI. Specifically, under the condition of high-temperature washing, prolonging the WTI will increase the ignition temperature of washed RH powder. The particle size could affect the temperature of the maximum rate of decomposition. Under the same conditions, the temperature difference of maximum rate of decomposition between washed RH powder and RH was 5-10 °C. For the original RH, the longer the WTI, the more unfavorable it was to increase the maximum weight loss rate, and the opposite was true for RH powder. With the increase in WTE, the flammability index, burnout temperature, and volatile devolatilization initial temperature increased obviously. In addition, washing pretreatment could reduce the ashing quality of RH and RH powder to varying degrees, and the ash quality was decreased by about 15% compared with that of unwashed RH. The alkali metal removal effect of washed RH powder was better than that of washed RH. The proportion of alkali metal K was decreased from 1 to 4% (washed RH) to 0.2-1% (washed RH powder). The ash deposit and slagging phenomenon were obviously improved. Under the same WTI, the higher the WTE was, the better the removal effect of alkali metals was. Correspondingly, the proportion of the eutectic composite salt of Mg-Fe-Al with a high melting point increased in the high-temperature sintering stage, which effectively improved the ash melting point and reduced the probability of ash deposit and slagging.

摘要

生物质直接燃烧存在诸多问题,如燃烧效率低和易结渣等。本文以稻壳(RH)为研究对象,探讨了不同水洗预处理条件(水洗时间(WTI)、水洗温度(WTE)和粒径)对燃烧特性及灰分形成特性的影响。结果表明,WTE和WTI对RH的燃烧特性有显著的耦合影响,粒径和WTI对挥发分释放综合特性有显著的耦合影响。具体而言,在高温水洗条件下,延长WTI会提高水洗RH粉末的着火温度。粒径会影响最大分解速率温度。在相同条件下,水洗RH粉末与RH之间最大分解速率的温差为5 - 10℃。对于原始RH,WTI越长,越不利于提高最大失重率,而对于RH粉末则相反。随着WTE的增加,可燃指数、 burnout温度和挥发分初始挥发温度明显升高。此外,水洗预处理能不同程度降低RH及RH粉末的灰化质量,与未水洗RH相比,灰分质量降低约15%。水洗RH粉末的碱金属去除效果优于水洗RH。碱金属K的比例从1 - 4%(水洗RH)降至0.2 - 1%(水洗RH粉末)。积灰和结渣现象明显改善。在相同WTI下,WTE越高,碱金属去除效果越好。相应地,在高温烧结阶段,高熔点的Mg - Fe - Al共晶复合盐比例增加,有效提高了灰熔点,降低了积灰和结渣的概率。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/883e5d6b0fd4/ao4c08820_0017.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/7107b63a1313/ao4c08820_0001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/c66df66030f4/ao4c08820_0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/3499927befd4/ao4c08820_0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/b7c47267a0b3/ao4c08820_0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/78e4af482969/ao4c08820_0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/6f147e8c64b3/ao4c08820_0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/6fcccf88af36/ao4c08820_0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/ba58a029f011/ao4c08820_0008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/f8053387c73d/ao4c08820_0009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/364d5f4d5137/ao4c08820_0010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/14d8d684ca69/ao4c08820_0011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/c20a81b061d7/ao4c08820_0012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/155b6be76992/ao4c08820_0013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/4ee4c858161d/ao4c08820_0014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/4b73dd58c9a8/ao4c08820_0015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/e280d032b28c/ao4c08820_0016.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/883e5d6b0fd4/ao4c08820_0017.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/7107b63a1313/ao4c08820_0001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/c66df66030f4/ao4c08820_0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/3499927befd4/ao4c08820_0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/b7c47267a0b3/ao4c08820_0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/78e4af482969/ao4c08820_0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/6f147e8c64b3/ao4c08820_0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/6fcccf88af36/ao4c08820_0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/ba58a029f011/ao4c08820_0008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/f8053387c73d/ao4c08820_0009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/364d5f4d5137/ao4c08820_0010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/14d8d684ca69/ao4c08820_0011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/c20a81b061d7/ao4c08820_0012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/155b6be76992/ao4c08820_0013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/4ee4c858161d/ao4c08820_0014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/4b73dd58c9a8/ao4c08820_0015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/e280d032b28c/ao4c08820_0016.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12a2/11683596/883e5d6b0fd4/ao4c08820_0017.jpg

相似文献

1
Experimental Study on the Effects of Washing Time, Washing Temperature, and Particle Size on the Combustion and Ash Formation Characteristics of Rice Husk.洗涤时间、洗涤温度和颗粒尺寸对稻壳燃烧及灰分形成特性影响的实验研究
ACS Omega. 2024 Dec 11;9(51):50705-50719. doi: 10.1021/acsomega.4c08820. eCollection 2024 Dec 24.
2
Study on Water Wash Pretreatment and Al-Si Additives to Relieve the Sintering Behavior of Fungus Bran Combustion Ash.水洗预处理及铝硅添加剂对缓解菌糠燃烧灰烧结行为的研究
Molecules. 2024 Oct 1;29(19):4675. doi: 10.3390/molecules29194675.
3
Phase diagram of SiO crystallization upon rice husk combustion to control silica ash quality.稻壳燃烧过程中二氧化硅结晶的相图控制硅灰质量。
Waste Manag. 2024 Jun 15;182:55-62. doi: 10.1016/j.wasman.2024.04.009. Epub 2024 Apr 17.
4
Effect of the Coal Fly Ash Blending Ratio on Biomass Slagging Structure Modification and Alkali Metal Migration.粉煤灰掺混比例对生物质结渣结构改性及碱金属迁移的影响
Energy Fuels. 2023 Aug 1;37(16):12018-12029. doi: 10.1021/acs.energyfuels.3c01506. eCollection 2023 Aug 17.
5
Reduced Pollutant Emissions and Slagging Rate of Biomass Pellet Combustion by Optimizing the Multilayer Distribution of Secondary Air.通过优化二次风多层分布降低生物质颗粒燃烧污染物排放及结渣率
ACS Omega. 2022 Aug 8;7(33):28962-28973. doi: 10.1021/acsomega.2c02587. eCollection 2022 Aug 23.
6
Effect of blending sewage sludge with coal on combustion and ash slagging behavior.将污水污泥与煤混合对燃烧和灰渣结渣行为的影响。
RSC Adv. 2019 Sep 19;9(51):29482-29492. doi: 10.1039/c9ra04243a. eCollection 2019 Sep 18.
7
Parametric and kinetic study of washing pretreatment for K and Cl removal from rice husk.稻壳脱钾脱氯水洗预处理的参数及动力学研究
Heliyon. 2021 Nov 15;7(11):e08398. doi: 10.1016/j.heliyon.2021.e08398. eCollection 2021 Nov.
8
Comparative Study of Different Pretreatment and Combustion Methods on the Grindability of Rice-Husk-Based SiO.不同预处理和燃烧方法对稻壳基SiO可磨性的对比研究
Nanomaterials (Basel). 2023 Nov 15;13(22):2951. doi: 10.3390/nano13222951.
9
Regulation of ash slagging behavior of palm oil decanter cake by alum sludge addition.添加铝污泥调节棕榈油分油器渣的结渣行为。
Chemosphere. 2023 Jul;330:138452. doi: 10.1016/j.chemosphere.2023.138452. Epub 2023 Mar 23.
10
Investigation on combustion characteristics and ash-related issues of Calliandra calothyrsus and Gliricidia sepium using thermogravimetric analysis and drop tube furnace.利用热重分析和沉降炉研究了银合欢和新银合欢的燃烧特性和灰分相关问题。
Bioresour Technol. 2024 Feb;394:130212. doi: 10.1016/j.biortech.2023.130212. Epub 2024 Jan 4.

本文引用的文献

1
Rice husk and husk biochar soil amendments store soil carbon while water management controls dissolved organic matter chemistry in well-weathered soil.稻壳和稻壳生物炭土壤改良剂在水土管理控制风化土壤中溶解有机质化学性质的同时储存土壤碳。
J Environ Manage. 2023 Aug 1;339:117936. doi: 10.1016/j.jenvman.2023.117936. Epub 2023 Apr 15.
2
Experimental investigation on composites incorporating rice husk nanoparticles for environmental noise management.复合材料中掺入稻壳纳米颗粒用于环境噪声管理的实验研究。
J Environ Manage. 2023 Jan 1;325(Pt A):116477. doi: 10.1016/j.jenvman.2022.116477. Epub 2022 Oct 20.
3
Pyrolysis and combustion characteristics of typical waste thermal insulation materials.
典型废保温材料的热解与燃烧特性。
Sci Total Environ. 2022 Aug 15;834:155484. doi: 10.1016/j.scitotenv.2022.155484. Epub 2022 Apr 23.
4
Microbial Pretreatment of Chicken Feather and Its Co-digestion With Rice Husk and Green Grocery Waste for Enhanced Biogas Production.鸡羽毛的微生物预处理及其与稻壳和蔬菜废弃物共消化以提高沼气产量
Front Microbiol. 2022 Apr 7;13:792426. doi: 10.3389/fmicb.2022.792426. eCollection 2022.
5
Enhanced crystallinity and thermal properties of cellulose from rice husk using acid hydrolysis treatment.采用酸水解处理提高稻壳纤维素的结晶度和热性能。
Carbohydr Polym. 2021 May 15;260:117789. doi: 10.1016/j.carbpol.2021.117789. Epub 2021 Feb 13.
6
Renewable energy from biomass surplus resource: potential of power generation from rice straw in Vietnam.生物质剩余资源的可再生能源:越南稻秆发电潜力。
Sci Rep. 2021 Jan 12;11(1):792. doi: 10.1038/s41598-020-80678-3.
7
Impact of Alkaline Pretreatment to Enhance Volatile Fatty Acids (VFAs) Production from Rice Husk.碱性预处理对提高稻壳挥发性脂肪酸(VFAs)产量的影响。
Biochem Res Int. 2019 Jan 23;2019:8489747. doi: 10.1155/2019/8489747. eCollection 2019.
8
Assessment of hydrothermal carbonization and coupling washing with torrefaction of bamboo sawdust for biofuels production.评估竹屑的水热碳化与热解耦合洗涤用于生物燃料生产。
Bioresour Technol. 2018 Jun;258:111-118. doi: 10.1016/j.biortech.2018.02.127. Epub 2018 Feb 28.
9
Evaluation of different water-washing treatments effects on wheat straw combustion properties.评价不同水洗处理对小麦秸秆燃烧性能的影响。
Bioresour Technol. 2017 Dec;245(Pt A):1075-1083. doi: 10.1016/j.biortech.2017.09.052. Epub 2017 Sep 8.
10
Energy potential from rice husk through direct combustion and fast pyrolysis: A review.稻壳通过直接燃烧和快速热解产生的能源潜力:综述。
Waste Manag. 2017 Jan;59:200-210. doi: 10.1016/j.wasman.2016.10.001. Epub 2016 Oct 15.