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Volume 38 Issue 8
Nov.  2020
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YE Chun-mei, WU Jian-qiang, HUANG Shen-fa, SHA Chen-yan, XU Zhi-hao, WANG Jing, ZHOU Dong, SUN Hai-tong, HAN Li-ming. SOLIDIFICATION/STABILIZATION OF HEAVY METAL CONTAMINATED SEDIMENT BY COMPOUD MATERIALS[J]. ENVIRONMENTAL ENGINEERING , 2020, 38(8): 125-130,51. doi: 10.13205/j.hjgc.202008021
Citation: YE Chun-mei, WU Jian-qiang, HUANG Shen-fa, SHA Chen-yan, XU Zhi-hao, WANG Jing, ZHOU Dong, SUN Hai-tong, HAN Li-ming. SOLIDIFICATION/STABILIZATION OF HEAVY METAL CONTAMINATED SEDIMENT BY COMPOUD MATERIALS[J]. ENVIRONMENTAL ENGINEERING , 2020, 38(8): 125-130,51. doi: 10.13205/j.hjgc.202008021

SOLIDIFICATION/STABILIZATION OF HEAVY METAL CONTAMINATED SEDIMENT BY COMPOUD MATERIALS

doi: 10.13205/j.hjgc.202008021
  • Received Date: 2019-05-24
  • A compound materials (FP) with a combination of Portland cement and efficient heavy metal stabilization material was used to solidify and stabilize river sediment containing heavy metals. In this paper, we set three FP dosages of 10%, 20%, 30%, three curing times of 7, 28, 42 d, and selected Portland cement as the control (CK). The compressive strength and leaching concentration were selected as indicators to test the solidifying and stabilizing effect of FP. The results showed that compared to the direct leaching of sediment, the leaching concentration of As in the sediment was reduced by more than 93%, that of Pb was reduced by 82.5%~97.68% under different FP dosages after 28 days. The leaching concentration of Cu and Zn reached the lowest value when the FP dosage was 30% and curing time was 42 days, which were 60.97% and 89.07% lower than the direct leaching of the sediment, respectively. Under different treatments, the leaching concentration of Cu and As in FP group was all significantly lower than that in CK (P<0.01); that of Zn in FP group was significantly lower than in CK after 42 days under 30% FP dosage (P<0.05). With the dosage of FP or the curing time increased, compressive strength of the solidified products was also significantly enhanced (P<0.05). Compressive strength of the solidified products of FP was significantly higher than that of CK (P<0.05) after 42 days, and when the dosage of FP increased to 30%, the compressive strength reached 2.1 MPa.
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  • 王凡, 赵琛, 潘海宁, 等. 城市黑臭水体底泥治理现状及建议[J]. 环境保护, 2018, 46(17):29-31.
    GENG J J, WANG Y P, LUO H J. Distribution, sources, and fluxes of heavy metals in the Pearl River Delta, South China[J]. Marine Pollution Bulletin, 2015, 101(2):914-921.
    马锐,杨长明,李建华.崇明岛典型河道底泥重金属污染及农用潜在风险评价[J].净水技术,2009,28(4):1-5.
    肖永丽,付晓萍,高阳俊. 上海市郊区河道底泥重金属污染状况评价[J].环境工程,2014,32(增刊1):879-884.
    GAO L, WANG Z W, SHAN J J, et al. Distribution characteristics and sources of trace metals in sediment cores from a trans-boundary watercourse:an example from the Shima River, Pearl River Delta[J]. Ecotoxicology & Environmental Safety, 2016, 134:186-195.
    刘伟, 杨富淋, 汪华安, 等. 珠三角河道底泥资源化利用探讨[J]. 环境科学与技术, 2018,41(增刊1):363-366.
    李涛,张志红,唐保荣. 荷兰填埋处置疏浚污染底泥的历程与实践[J]. 环境工程,2006,24(4):48-51.
    王慧,于伟鹏,黑亮,等.污染底泥处理及资源化利用研究进展[J].人民珠江,2015,36(3):,121-124.
    乔飞. 城市河流污染底泥处理技术探讨[J]. 环境与发展, 2017,29(7):44-45.
    赵明,刘宏,王文江,等.疏浚底泥重金属污染现状及其治理技术[J].盐业与化工,2016,45(8):1-7.
    CAROLIN C F, KUMAR P S, SARAVANAN A, et al. Efficient techniques for the removal of toxic heavy metals from aquatic environment:a review[J]. Journal of Environmental Chemical Engineering, 2017:5(3)2782-2799.
    AKCIL A, ERUST C, OZDEMIROGLU S, et al. A review of approaches and techniques used in aquatic contaminated sediments:metal removal and stabilization by chemical and biotechnological processes[J]. Journal of Cleaner Production, 2015, 86:24-36.
    SHIN W, KIM Y K. Stabilization of heavy metal contaminated marine sediments with red mud and apatite composite[J]. Journal of Soils & Sediments, 2016, 16(2):726-735.
    王川,杨朝晖,曾光明,等.DTCR协同水泥固化/稳定化重金属污染底泥的研究[J].中国环境科学,2012,32(11):2060-2066.
    黄鸽,姜霞,完颜华,等. 不同稳定剂对污染沉积物中重金属的稳定效果[J].环境科学研究,2012,25(5):563-567.
    王云,汪雅谷,罗海林, 等. 上海市土壤环境背景值[M].北京:中国环境科学出版社, 1992.
    国家环保总局. GB 8978-1996污水综合排放标准[S].北京:中国环境科学出版社,1996.
    国家环境保护总局,国家质量监督检验检疫总局. GB 5085.3-2007危险废物鉴别标准浸出毒性鉴别标准[S].北京:中国环境科学出版社,2007.
    苏良湖,梁美生,赵由才. 不同固化剂对底泥重金属稳定化效果的研究[J].环境工程学报,2010,4(7):1655-1658.
    王登权, 何伟, 王强,等. 重金属在水泥基材料中的固化和浸出研究进展[J]. 硅酸盐学报, 2018, 46(5):71-81.
    谢华明,曾光明,罗文连,等. 水泥、粉煤灰及DTCR固化/稳定化重金属污染底泥[J].环境工程学报,2013,7(3):1121-1127.
    吴平霄, 廖宗文. 黏土矿物质层域的研究进展[J]. 自然杂志, 2000(1):25-32.
    刘继娟. 锆改性凹土对水体与底泥中重金属的吸附与固定效果研究[D]. 南京:南京理工大学,2016.
    钟倩云,曾敏,廖柏寒,等. 2种固化剂对重金属和砷复合污染底泥的稳定化处理效果[J].水土保持学报,2012,26(6):190-193.
    杨克明,陶红,李飞鹏, 等.混合氯盐对水泥固化和河道底泥稳定化的影响[J]. 净水技术,2018,37(5):116-121.
    侯浩波,刘柳,周旻,等. 河道底泥重金属浸出毒性分析及其固化/稳定化效果[J].环境工程学报,2015,9(7):3339-3344.
    JGJ/T 293-2013淤泥多孔砖应用技术规程[S].
    王振,肖宇伦,胡倩,等.大冶红星湖重金属污染底泥固化/稳定化及浸出毒性的研究[J].湖北理工学院学报,2016,32(5):22-27

    ,39.
    陶子健,葛明星,邵俐,等. 利用水泥与矿渣固化河道底泥的强度特性试验研究[J].公路交通科技(应用技术版),2016,12(12):114-115.
    WANG Z, FA S F, YAN L L, et al. Shrinkage properties of cement solidified sludge with high water content[J]. Advanced Materials Research, 2011, 168/170(2):1496-1500.
    侯鑫,马巍,李国玉,等.木质素磺酸盐对兰州黄土力学性质的影响[J].岩土力学,2017,38(增刊2):18-26.
    李磊,朱伟,林城.骨架构建法进行污泥固化处理的试验研究[J].中国给水排水,2005,21(6):41-43.
    何思琪, 张薇, 林建伟,等. 锆改性沸石添加对重污染河道底泥磷释放和钝化的影响[J]. 环境科学, 2018,39(9):4179-4188.
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