PRETREATMENT OPTIMIZATION FOR MULTIPLE MEMBRANE TREATMENT AND REUSE OF WATER PROCED PRODUCED BY THREE-GAS CO-PRODUCTION FROM COAL MEASURES
-
摘要: 以煤层气、致密砂岩气和页岩气共存为特征的煤系"三气"是一类重要的非常规天然气资源。针对鄂尔多斯盆地东北缘临兴区块煤系"三气"合采产出水的超高盐度和高浊度等特点,首先研究了原位水样的处理工艺,然后采用加载絮凝-微电解-纳滤-反渗透方法进行了中试处理,并对预处理阶段进行了优化试验。研究结果表明:加载絮凝单元出水浊度和ρ(COD)分别为11.66 NTU和1711 mg/L,去除率分别为98.9%和34.57%;微电解单元的COD去除率为66.9%,出水电导率为52.5 mS/cm。再经过纳滤-反渗透处理后,出水可达到GB 5084—2005《农田灌溉水质标准》旱作标准。Abstract: Three natural gases in coal measure, including coalbed methane (CBM), tight sandstone gas and shale gas, are important unconventional gas resources. Firstly, the treatment process of the collected in-situ water sample was studied, according to the characteristics of ultra-high salinity and high turbidity of the water produced by three-gas co-production from coal measures in Linxing block on the eastern edge of the Erdos basin. Then, pilot treatment was carried out by the process of loading flocculation-microelectrolysis-nanofiltration-reverse osmosis for CBM produced water, on basis of characteristics of high salinity and turbidity. The process parameters and effect of pretreatment units was optimized. The effluent turbidity and COD of the loaded flocculation was 11.66 NTU and 1711 mg/L, respectively, and the removal rates were 98.9% and 34.57%, respectively. The removal of COD was 66.9% and the conductivity of effluent was 52.5 mS/cm by micro electrolysis unit. After NF-RO treatment, the effluent met the dry farming standard of irrigation water quality standard (GB 5084-2005).
-
[1] 刘贺,罗勇,雷坤超,等. 煤层气井产水、产气动态变化特征研究[J]. 城市地质,2018, 13(4):60-66. [2] HIMSTEDT H H, SENGUPTA A, QIAN X, et al. Magnetically responsive nano-filtration membranes for treatment of coal bed methane produced water[J]. Journal of the Taiwan Institute of Chemical Engineers, 2019, 94:97-108. [3] JIMÉNEZ S, MICÓ M M, ARNALDOS M, et al. State of the art of produced water treatment[J]. Chemosphere, 2018, 192:186-208. [4] ASHRAF S N, RAJAPAKSE J, DAWES L A, et al. Electrocoagulation for the purification of highly concentrated brine produced from reverse osmosis desalination of coal seam gas associated water[J]. Journal of Water Process Engineering, 2019, 28:300-310. [5] 费琼,王少坡,罗伟,等. 电絮凝法在水处理过程中影响因素研究现状[J]. 工业水处理, 2016, 36(12):16-21. [6] ASHRAF S N, RAJAPAKSE J, DAWES L A, et al. Coagulants for removal of turbidity and dissolved species from coal seam gas associated water[J]. Journal of Water Process Engineering,2018, 26:187-199. [7] LIN J, COUPERTHWAITE S J, MILLAR G J. Applicability of iron based coagulants for pre-treatment of coal seam water[J]. Journal of Environmental Chemical Engineering, 2017, 5(1):1119-1132. [8] 李志远. 芬顿氧化混凝沉淀处理煤化工废水生化出水试验研究[D]. 哈尔滨:哈尔滨工业大学,2013:9-14. [9] 孙悦,冯启言,李向东. 微电解-Fenton联合工艺预处理煤层气井压裂废水[J]. 环境工程学报,2014, 8(3):864-868. [10] JIMÉNEZ S, ANDREOZZI M, MICÓ M M, et al. Produced water treatment by advanced oxidation processes[J]. Science of the Total Environment, 2019, 666:12-21. [11] 王毅博,冯民权,刘永红,等. 铁碳微电解技术在难治理废水中的研究进展[J]. 化工进展,2018, 37(8):3188-3196. [12] 王昌稳, 雷泽远, 李军, 等. 铁碳微电解预处理高盐腌制废水的运行方式研究[J]. 中国给水排水, 2018, 34(15):95-99. [13] 温彩哨, 余志晟, 刘新春, 等. 煤层气产出水水质特征及处理技术研究进展[J]. 工业水处理, 2014, 34(10):1-6. [14] VEDELAGO R, MILLAR G J. Process evaluation of treatment options for high alkalinity coal seam gas associated water[J]. Journal of Water Process Engineering, 2018, 23:195-206. [15] QIN M H, DESHMUKH A, EPSZTEIN R, et al. Comparison of energy consumption in desalination by capacitive deionization and reverse osmosis[J]. Desalination, 2019, 455:100-114. [16] SEVERIN B F, HAYES T D. Electrodialysis of concentrated brines:effects of multivalent cations[J]. Separation and Purification Technology, 2019, 218:227-241. [17] ZHANG Z Y, DU X W, CARLSON K H, et al. Effective treatment of shale oil and gas produced water by membrane distillation coupled with precipitative softening and walnut shell filtration[J]. Desalination, 2019, 454:82-90. [18] CHUN Y, KIM S, MILLAR G J, et al. Forward osmosis as a pre-treatment for treating coal seam gas associated water:Flux and fouling behavior[J]. Desalination, 2017, 403:144-152. [19] 任晓晶. 澳大利亚煤层气产出水脱盐处理方法[J]. 天然气工业,2012,32(6):78-81,113. [20] 冯礼奎,李广辉,葛雪静,等.反渗透预处理系统微生物污染原因分析及处理[J]. 工业水处理,2016,36(3):103-105. [21] 孙永超,解利昕,高婷婷,等.反渗透海水淡化预处理工艺[J].化工进展,2016,35(11):3658-3662. [22] 张寿恺,邱梅. KDF过滤介质在反渗透预处理中的应用[J].工业水处理,2001(3):8-9,36. [23] 徐进祥. 反渗透化学清洗及水预处理方式浅探[J].化工管理,2018(18):31-32. [24] 操家顺,浩长江,方芳. 印染废水回用的反渗透预处理技术[J].环境科学研究,2014,27(7):742-748. [25] 刘研萍,李文龙,朱佳,等. 加载絮凝-超滤-反渗透组合工艺处理PCB电镀废水[J].化工环保, 2019,39(1):16-21. [26] 兰淼. 煤系三气合采产出水的多元膜处理工艺优化研究[D].北京:北京化工大学,2019:33-37. [27] 黄俊. 加载絮凝沉淀工艺在重金属废水处理中的试验研究[D]. 广州:广州大学,2013:33. [28] 狄军贞,赵微,朱志涛,等. 响应曲面法优化强化混凝工艺处理微污染水[J]. 环境工程学报, 2017, 11(1):27-32. [29] 宋娟娟. 水处理絮凝过程絮体分形成长特性研究[D]. 哈尔滨:哈尔滨工业大学,2009:74. [30] 董文艺,朱佳,王延辉,等. 加载絮凝-污泥回流工艺处理重金属废水的研究[J]. 水利水电技术, 2012, 43(8):37-41. [31] 张勇, 何士龙. 响应面法优化混凝预处理垃圾渗滤液[J]. 河北师范大学学报(自然科学版), 2012,36(4):403-408. [32] SHU Z N, LV Y P, HUANG J, et al. Treatment of compost leachate by the combination of coagulation and membrane process[J]. Chinese Journal of Chemical Engineering, 2016, 24(10):1369-1374. [33] ZHENG X Y, JIN M Q, ZHOU X, et al. Enhanced removal mechanism of iron carbon micro-electrolysis constructed wetland on C, N, and P in salty permitted effluent of wastewater treatment plant[J]. Science of the Total Environment, 2019, 649:21-30.
点击查看大图
计量
- 文章访问数: 154
- HTML全文浏览量: 25
- PDF下载量: 3
- 被引次数: 0