The Curing Effect of Goethite on Heavy Metal Ions in Fly Ash from Waste Incineration and Mechanism Analysis
-
摘要:
垃圾焚烧飞灰是一种危险固体废弃物,必须经过固化稳定化,满足《生活垃圾填埋场污染控制标准》后方能填埋。针铁矿是一种表面带有丰富羟基功能基的固体表面活性剂,利用其表面羟基对金属离子的络合作用能够对垃圾焚烧飞灰进行固化。本论文探讨了工艺参数对针铁矿固化飞灰毒性浸出效果的影响;又利用酸碱滴定表征了针铁矿表面羟基化特性;用格氏图处理酸碱滴定数据,计算出针铁矿表面羟基活性位点密度。结果表明:在针铁矿添加量为15%、液固比为0.4、固化时间为3 d的条件下,固化后的飞灰能够满足生活垃圾填埋场进场要求;金属离子能够进入针铁矿表面stern层被紧密吸附,碱性条件下则更加有利于离子在针铁矿双电层的扩散层中吸附。
Abstract:Fly ash from municipal solid waste incineration is a kind of hazardous solid waste. It must be cured and stabilized to meet the "Standard for Pollution Control of Domestic Waste Landfills" before it can be landfilled. Goethite is a kind of solid surfactant with abundant hydroxyl functional groups on its surface, which can be used to solidify waste incineration fly ash by complexing metal ions with hydroxyl groups on its surface. In this paper, the influence of technological parameters on toxic leaching effect of goethite cured fly ash was discussed, and the hydroxylation characteristics of goethite surface were characterized by acid-base titration, and the density of hydroxyl active sites on goethite surface was calculated by processing acid-base titration data with Gran diagram. The results show that under the conditions of 15% goethite, 0.4 liquid-solid ratio and 3 days solidification time, the cured fly ash can meet the entry requirements of domestic refuse landfill; metal ions can enter stern layer on goethite surface and be adsorbed tightly, while alkaline conditions are more conducive ion to adsorb on diffusion layer on goethite double layer.
-
表 1 原子吸收分光光度计仪器工作条件
Table 1. Working conditions of atomic absorption spectrophotometer instrument
Element Wavelength /nm Passband width /nm Lamp current /mA Flame type 铜 324.7 0.4 8 空气-乙炔,氧化性蓝色火焰 铅 283.3 0.4 6 空气-乙炔,氧化性蓝色火焰 表 2 飞灰固化物二噁英及重金属浸出毒性测试结果
Table 2. The leaching toxicity test results of dioxin and heavy mental in cured fly ash
项目 单位 飞灰原样 固化后飞灰样品 生活垃圾填埋场限值 检出限 含水率 % 25 15 30 - 二噁英 μg/kg 3.15 2.31 3 - 汞(Hg) mg/L 0.001 1 0.000 1 0.05 0.000 05 铜(Cu) mg/L 7.19 0.02 40 0.008 锌(Zn) mg/L 31.43 0.003 100 0.002 铅(Pb) mg/L 2.13 0.12 0.25 0.01 镉(Cd) mg/L 0.98 0.02 0.15 0.001 铍(Be) mg/L ND ND 0.02 0.000 4 钡(Ba) mg/L ND ND 25 0.000 4 镍(Ni) mg/L 0.05 0.01 0.5 0.004 砷(As) mg/L 0.007 0.001 0.3 0.007 总铬(Cr) mg/L 0.57 0.05 4.5 0.01 六价铬(Cr6+) mg/L 0.021 0.003 1.5 0.004 硒(Se) mg/L ND ND 0.1 0.004 注:ND为未检出。 -
[1] 田书磊.垃圾焚烧飞灰重金属热分离工艺及挥发特性研究[D].哈尔滨: 哈尔滨工业大学, 2007.
http://cdmd.cnki.com.cn/Article/CDMD-10213-2008193213.htm [2] 熊祖鸿, 范根育, 鲁敏, 等.垃圾焚烧飞灰处置技术研究进展[J].化工进展, 2013, 32(7):1678-1684. http://d.old.wanfangdata.com.cn/Periodical/sn201411008
[3] 罗忠涛, 肖宇领, 杨久俊.等.垃圾焚烧飞灰有毒重金属固化稳定技术研究综述[J].环境污染与防治, 2012, 34(8):58-62. doi: 10.3969/j.issn.1001-3865.2012.08.013
[4] 郭晓潞, 施惠生.MSWIFA制阿利尼特水泥基材料的耐久性[J].材料科学与工程学报, 2013, 31(4):479-483. http://d.old.wanfangdata.com.cn/Periodical/clkxygc201304001
[5] 彭雯.城市生活垃圾焚烧飞灰中重金属浸出的特性及沥青固化飞灰的实验研究[D].杭州: 浙江大学, 2004.
http://cdmd.cnki.com.cn/Article/CDMD-10335-2004109801.htm [6] 周建国, 张曙光, 李萍, 等.城市生活垃圾焚烧飞灰中重金属的固化/稳定化处理[J].天津城建大学学报, 2015, 21(2):109-113. http://www.wanfangdata.com.cn/details/detail.do?_type=perio&id=tjcsjsxyxb201502007
[7] 倪文, 张玉燕, 丁嫚.垃圾焚烧飞灰的资源化处置前景[J].环境污染与防治, 2008, 30(4):1-5. doi: 10.3969/j.issn.1001-3865.2008.04.001
[8] 邹庐泉, 吴长淋, 张晓星, 等.满足《生活垃圾填埋污染控制标准》的生活垃圾焚烧飞灰重金属药剂稳定化研究[J].环境污染与防治, 2011, 33(3):61-64. doi: 10.3969/j.issn.1001-3865.2011.03.013
[9] 张玲.不同条件下焚烧飞灰浸出特性的试验研究[D].北京: 北京化工大学, 2008.
http://cdmd.cnki.com.cn/article/cdmd-10010-2008149865.htm [10] 袁玲, 施惠生, 岳鹏.垃圾焚烧飞灰胶凝活性初探[J].同济大学学报(自然科学版), 2003, 31(12):1444-1448. doi: 10.3321/j.issn:0253-374X.2003.12.013
[11] 李润东, 聂永丰, 王雷, 等.成分对垃圾飞灰熔融过程重金属迁移的影响[J].清华大学学报:自然科学版, 2004, 44(9):1180-1183. http://d.old.wanfangdata.com.cn/Periodical/qhdxxb200409008
[12] 谢亚巍.铁氧化物及其腐殖酸复合物对砷的吸持特性研究[D].重庆: 西南大学, 2012.
http://cdmd.cnki.com.cn/article/cdmd-10635-1012343981.htm [13] 王慧.铁氧化物及其胡敏酸复合体对磷酸盐的吸附研究[D].武汉: 中国农业大学, 2015.
http://cdmd.cnki.com.cn/Article/CDMD-10504-1015387493.htm [14] Kalmykova Y, Knutsson J, Strmvall A M, et al. Blast-furnace sludge as sorbent material for multi-metal contaminated water[J]. Alliance for global sustainability book series, 2009, 17:307-317. doi: 10.1007/978-90-481-3043-6
[15] Tsutsumi T, Nishimoto S, Kameshima Y, et al. Hydrothermal preparation of to bermorite from blast furnace slag for Cs+ and Sr2+ sorption[J]. Journal of hazardous materials, 2014, 266(2):174-181.
[16] Wang F, Zhang F, Chen Y, et al. A comparative study on the heavy metal solidification/stabilization performance of four chemical solidifying agents in municipal solid waste incineration fly ash[J]. Journal of hazardous materials, 2015, 300:451-458. doi: 10.1016/j.jhazmat.2015.07.037
[17] Shi D Z, Zhang C, Zhang J, et al. Seed-assisted hydrothermal treatment with composite silicon-aluminum additive for solidification of heavy metals in MSW incineration fly ash[J]. Energy & fuels, 2016, 30:10. https://www.researchgate.net/publication/309602495_Seed-assisted_hydrothermal_treatment_with_composite_silicon-aluminum_additive_for_solidification_of_heavy_metals_in_MSW_incineration_fly_ash
[18] Haha M, Lothenbach B, Saout G L, et al. Influence of slag chemistry on the hydration of alkali-activated blast-furnace slag-part Ⅱ:effect of Al2O3[J]. Cement & concrete research, 2012, 42(1):74-83. http://www.sciencedirect.com/science/article/pii/S0008884611001414
[19] Das B, Prakash S, Reddy P S R, et al. An overview of utilization of slag and sludge from steel industries[J]. Resources conservation & recycling, 2007, 50(1):40-57. http://www.wanfangdata.com.cn/details/detail.do?_type=perio&id=fdc94b2feb92670074ccfbb7e2b158f7
[20] Kovtun M, Kearsley E P, Shekhovtsova J. Chemical acceleration of a neutral granulated blast-furnace slag activated by sodium carbonate[J]. Cement & concrete research, 2015, 72:1-9. http://www.wanfangdata.com.cn/details/detail.do?_type=perio&id=14ccd744e5d7196ef1c5386b63275b68
[21] Tian S L, Wang Q, Wang Q H, et al. Curing characteristics of heavy metals in melting process of fly ash from municipal solid waste incineration[J]. Journal of Harbin institute of technology, 2008, 40(10):1576-1580. http://academic.hep.com.cn/fese/cn/10.1007/s11783-008-0060-6