Influence of calcium chloride on the thermal behavior of heavy and alkali metals in sewage sludge incineration

被引:45
作者
Han, Jun [1 ]
Xu, Minghou [2 ]
Yao, Hong [2 ]
Furuuchi, Masami [3 ]
Sakano, Takeo [3 ]
Kim, Hee Joon [4 ]
机构
[1] Wuhan Univ Sci & Technol, Coll Chem Engn & Technol, Wuhan 430070, Hubei, Peoples R China
[2] Huazhong Univ Sci & Technol, State Key Lab Coal Combust, Wuhan 430074, Hubei, Peoples R China
[3] Kanazawa Univ, Grad Sch Nat Sci & Technol, Kanazawa, Ishikawa 9208667, Japan
[4] Toyohashi Univ Technol, Dept Ecol Engn, Toyohashi, Aichi 4418580, Japan
关键词
D O I
10.1016/j.wasman.2007.01.015
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
In order to separate and reuse heavy and alkali metals from flue gas during sewage sludge incineration, experiments were carried out in a pilot incinerator. The experimental results show that most of the heavy and alkali metals form condensed phase at temperature above 600 degrees C. With the addition of 5% calcium chloride into sewage sludge., the gas/solid transformation temperature of part of the metals (As, Cu, Mg and Na) is evidently decreased due to the formation of chloride, while calcium chloride seems to have no significant influence on Zn and P. Moreover, the mass fractions of some heavy and alkali metals in the collected fly ash are relatively high. For example, the mass fractions for Pb and Cu in the fly ash collected by the filter are 1.19% and 19.7%, respectively, which are well above those in lead and copper ores. In the case of adding 5% calcium chloride, the heavy and alkali metals can be divided into three groups based on their conversion temperature: Group A that includes Na, Zn, K, Mg and P, which are converted into condensed phase above 600 degrees C; Group B that includes Pb and Cu which solidify when the temperature is above 400 degrees C; and Group C that includes As, whose condensation temperature is as low as 300 degrees C. (C) 2007 Elsevier Ltd. All rights reserved.
引用
收藏
页码:833 / 839
页数:7
相关论文
共 18 条
[1]  
BIEDERMANN F, 1998, P 10 EUR C TECHN EXH
[2]   The effects of solid absorbents on the emission of trace elements, SO2, and NOx during coal combustion [J].
Cheng, JF ;
Zeng, HC ;
Zhang, ZH ;
Xu, MH .
INTERNATIONAL JOURNAL OF ENERGY RESEARCH, 2001, 25 (12) :1043-1052
[3]   Chloride effects on the speciation and partitioning of heavy metal during the municipal solid waste incineration process [J].
Chiang, KY ;
Wang, KS ;
Lin, FL ;
Chu, WT .
SCIENCE OF THE TOTAL ENVIRONMENT, 1997, 203 (02) :129-140
[4]   Equilibrium analysis of the affect of temperature, moisture and sodium content on heavy metal emissions from municipal solid waste incinerators [J].
Durlak, SK ;
Biswas, P ;
Shi, J .
JOURNAL OF HAZARDOUS MATERIALS, 1997, 56 (1-2) :1-20
[5]  
HAN J, 2005, THESIS HUAZHONG U TE
[6]  
KEISUKE N, 2001, NKK TECHNICAL REV, V84, P8
[7]   REMOVAL OF GASEOUS ALKALI-METAL COMPOUNDS FROM HOT FLUE-GAS BY PARTICULATE SORBENTS [J].
LEE, SHD ;
JOHNSON, I .
JOURNAL OF ENGINEERING FOR POWER-TRANSACTIONS OF THE ASME, 1980, 102 (02) :397-402
[8]   Sorbent control of trace metals in sewage sludge combustion and incineration [J].
Naruse, I ;
Yao, H ;
Mkilaha, ISN .
JOURNAL DE PHYSIQUE IV, 2003, 107 :917-920
[9]   Recovery of zinc and lead from fly ash from ash-melting and gasification-melting processes of MSW - Comparison and applicability of chemical leaching methods [J].
Okada, T. ;
Tojo, Y. ;
Tanaka, N. ;
Matsuto, T. .
WASTE MANAGEMENT, 2007, 27 (01) :69-80
[10]  
Perry R.H, 1997, PRERRYS CHEM ENG HDB