CN101157504B - Process for Softening Hard Water Using SO2 and CO2 in Tail Gas - Google Patents
Process for Softening Hard Water Using SO2 and CO2 in Tail Gas Download PDFInfo
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- CN101157504B CN101157504B CN2007100357714A CN200710035771A CN101157504B CN 101157504 B CN101157504 B CN 101157504B CN 2007100357714 A CN2007100357714 A CN 2007100357714A CN 200710035771 A CN200710035771 A CN 200710035771A CN 101157504 B CN101157504 B CN 101157504B
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Abstract
Description
技术领域technical field
本发明属于环境保护领域,具体涉及一种利用尾气中SO2、CO2软化硬水的新工艺。The invention belongs to the field of environmental protection, and in particular relates to a new process for softening hard water by utilizing SO 2 and CO 2 in tail gas.
背景技术Background technique
有色企业在废水处理工序中会经常产生含钙在1000mg/L左右的净化水,而这种净化水由于硬度高,其回用价值有限,为实现循环经济,企业需准备实施工业废水“零排放”。为确保废水“零排放”,首先必须降低该净化水的硬度。Non-ferrous enterprises often produce purified water with a calcium content of about 1000mg/L in the wastewater treatment process. Due to the high hardness of this purified water, its reuse value is limited. ". To ensure "zero discharge" of wastewater, the hardness of this purified water must first be reduced.
而目前,国内外对硬水软化方法主要有加热煮沸法、药剂软化法、离子交换法、吸附法、蒸馏、反渗透等。这些方法主要是原料或能量消耗大,成本较高,均有待改进,及创新。At present, the hard water softening methods at home and abroad mainly include heating and boiling method, chemical softening method, ion exchange method, adsorption method, distillation, reverse osmosis and so on. These methods mainly consume a lot of raw materials or energy, and the cost is relatively high, and all of them need to be improved and innovated.
发明内容Contents of the invention
本发明所要解决的技术问题是克服现有硬水软化处理成本高的不足,提供一种新型工艺,达到“以废治废”、节约成本的新工艺。The technical problem to be solved by the present invention is to overcome the disadvantage of high cost of existing hard water softening treatment, and provide a new process to achieve "treat waste with waste" and save costs.
本发明解决上述技术问题采用的技术方案是:The technical solution adopted by the present invention to solve the problems of the technologies described above is:
将含SO2、CO2尾气与硬水在吸收塔中反应,检测反应混合液的pH为2.5-5.5时,停止反应,将反应后的混合液过滤,得到软化水及滤渣;所述的硬水为含Ca2+浓度0.6-0.7g/L,pH为9-11的溶液,含SO2、CO2尾气中二氧化硫和二氧化碳体积浓度分别为1-10%、5-30%。Tail gas containing SO2 and CO2 is reacted with hard water in the absorption tower, and when the pH of the reaction mixture is detected to be 2.5-5.5, the reaction is stopped, and the reacted mixture is filtered to obtain demineralized water and filter residue; the hard water is The solution containing Ca 2+ concentration of 0.6-0.7g/L, pH of 9-11, and volume concentration of sulfur dioxide and carbon dioxide in tail gas containing SO 2 and CO 2 are 1-10% and 5-30% respectively.
所述的硬水还含Mg2+浓度50-100mg/l。The hard water also contains Mg 2+ concentration of 50-100mg/l.
将反应后的混合液用碱液调整pH值为6.5-7.5,然后过滤,得到软化水及滤渣。Adjust the pH value of the reacted mixed solution to 6.5-7.5 with lye, and then filter to obtain demineralized water and filter residue.
吸收塔内的液气比控制在2-3l/m3。The liquid-gas ratio in the absorption tower is controlled at 2-3l/m 3 .
二氧化硫、二氧化碳软化硬水的生产原理:The production principle of sulfur dioxide and carbon dioxide softening hard water:
SO2+H2O→H2SO3→H++HSO3 -→2H++SO3 2- SO 2 +H 2 O→H 2 SO 3 →H + +HSO 3 - →2H + +SO 3 2-
CO2+H2O→H2CO3→H++HCO3 -→2H++CO3 2- CO 2 +H 2 O→H 2 CO 3 →H + +HCO 3 - →2H + +CO 3 2-
Ca2++SO3 2-→CaSO3 Ca 2+ +SO 3 2- →CaSO 3
Ca2++CO3 2-→CaCO3 Ca 2+ +CO 3 2- →CaCO 3
Mg2++SO3 2-→MgSO3 Mg 2+ +SO 3 2- →MgSO 3
Mg2++CO3 2-→MgCO3 Mg 2+ +CO 3 2- →MgCO 3
SO2+CaCO3→CaSO3+CO2 SO 2+ CaCO 3 →CaSO 3 +CO 2
SO2+MgCO3→MgSO3+CO2 SO 2 +MgCO 3 →MgSO 3 +CO 2
2CaSO3+O2+4H2O→2CaSO4·2H2O2CaSO 3 +O 2 +4H 2 O→2CaSO 4 2H 2 O
2MgSO3+O2→2MgSO4 2MgSO 3 +O 2 →2MgSO 4
本发明是一种利用尾气中SO2、CO2软化硬水的新工艺。尾气中二氧化硫与硬水反应生成SO3 2-,SO3 2-与Ca2+和Mg2+反应分别生成亚硫酸钙和亚硫酸镁沉淀;尾气中二氧化碳和硬水发生反应,进而生成CO3 2-,CO3 2-与Ca2+和Mg2+反应分别生成碳酸钙和碳酸镁沉淀;碳酸钙与二氧化硫反应生成亚硫酸钙。反应过程中采用逆向气液洗涤,洗涤温度:常温;反应终点pH值(出口pH值):2.5-5.5;一次过滤液为除Ca2+、Mg2+净化液,即软化水;滤渣为亚硫酸钙、硫酸钙、碳酸钙、亚硫酸镁、硫酸镁、和碳酸镁沉淀。The invention is a new process for softening hard water by utilizing SO 2 and CO 2 in tail gas. Sulfur dioxide in the tail gas reacts with hard water to generate SO 3 2- , and SO 3 2- reacts with Ca 2+ and Mg 2+ to form calcium sulfite and magnesium sulfite precipitates respectively; carbon dioxide in the tail gas reacts with hard water to generate CO 3 2- , CO 3 2- reacts with Ca 2+ and Mg 2+ to form calcium carbonate and magnesium carbonate precipitates respectively; calcium carbonate reacts with sulfur dioxide to form calcium sulfite. Reverse gas-liquid washing is used in the reaction process, washing temperature: normal temperature; pH value at the end of the reaction (outlet pH value): 2.5-5.5; the primary filtrate is Ca 2+ , Mg 2+ purification liquid, that is, softened water; the filter residue is sub Calcium sulfate, calcium sulfate, calcium carbonate, magnesium sulfite, magnesium sulfate, and magnesium carbonate precipitate.
本发明的有益效果在于:The beneficial effects of the present invention are:
1.为软化硬水提供了一个新的工艺方法。1. Provide a new process method for softening hard water.
2.较好的解决了硬水软化成本高以及尾气中二氧化硫难处理的问题。2. It better solves the problems of high cost of hard water softening and difficult treatment of sulfur dioxide in tail gas.
3.本发明工艺“以废治废”,不仅解决了废气处理和硬水软化的问题,具有显著的环境效益、经济效益及社会效益。3. The process of the present invention "uses waste to treat waste" not only solves the problems of waste gas treatment and hard water softening, but also has significant environmental, economic and social benefits.
附图说明Description of drawings
图1为本发明实施例1的工艺流程图Fig. 1 is the process flow chart of embodiment 1 of the present invention
具体实施方式Detailed ways
实施例1:Example 1:
参照附图1,先将一定浓度硬水(Ca2+400mg/L;Mg2+100mg/L)送入到鼓泡吸收塔中。利用液体二氧化硫配制二氧化硫浓度为1%的气体,气体流量约为20Nm3/h,然后由控制阀控制鼓入一个鼓泡吸收塔(塔径Φ200mm,塔高1m),由于空气搅拌,可避免悬浮物沉降。反应在常压,常温的条件下进行,吸收反应后的尾气经由吸收塔的顶部排出。气液吸收1min后,pH值为3,用碱液调整吸收液pH值至7,得悬浮液。沉清池固液分离,沉淀时间为30min,滤液即为软化水,Ca2+为18mg/L;Mg2+为10mg/L。With reference to accompanying drawing 1, first send certain concentration hard water (Ca 2+ 400mg/L; Mg 2+ 100mg/L) into the bubbling absorption tower. Use liquid sulfur dioxide to prepare a gas with a sulfur dioxide concentration of 1%, and the gas flow rate is about 20Nm 3 /h, and then controlled by a control valve to blow into a bubbling absorption tower (tower diameter Φ200mm, tower height 1m), due to air stirring, it can avoid suspension Subsidence. The reaction is carried out under the conditions of normal pressure and normal temperature, and the tail gas after the absorption reaction is discharged through the top of the absorption tower. After gas-liquid absorption for 1 minute, the pH value is 3, and the pH value of the absorption liquid is adjusted to 7 with lye to obtain a suspension. The solid-liquid separation in the sedimentation tank, the precipitation time is 30min, the filtrate is demineralized water, the Ca 2+ is 18mg/L; the Mg 2+ is 10mg/L.
监测分析报告显示:该厂脱硫处理前SO2的体积百分含量为1%,经过脱硫处理后,SO2体积百分含量降低为0.01%,脱硫率达到90%以上。The monitoring and analysis report shows that before the desulfurization treatment, the volume percentage of SO 2 is 1%. After the desulfurization treatment, the volume percentage of SO 2 is reduced to 0.01%, and the desulfurization rate reaches more than 90%.
实施例2:Example 2:
先将一定浓度硬水(Ca2+1000mg/L),一次性送入到到喷淋吸收塔中。从某厂管道尾气中引出排量约为200mN 3/h的支路,先用布袋除尘器除尘,然后由控制阀控制鼓入一个鼓泡吸收塔(塔径Φ400m,塔高3m),吸收塔底部液体(硬水)用泵抽出循环从顶部送入,由于水泵连续地抽出,送入,底部液体被搅拌,避免悬浮物沉降。液气比控制在2-3l/m3左右。在常压,反应温度为常温的条件下,进行喷淋反应,吸收反应后的尾气经由吸收塔的顶部排出。气液吸收1min后,pH值为3,用碱液调整吸收液pH值至7,得悬浮液。沉清池固液分离,沉淀时间为30min,滤液即为软化水。Ca2+为18mg/L;Mg2+为10mg/L。First, a certain concentration of hard water (Ca 2+ 1000mg/L) is sent to the spray absorption tower at one time. A branch with a displacement of about 200m N 3 /h is drawn from the exhaust gas of a certain factory pipeline. First, dust is removed by a bag filter, and then controlled by a control valve to blow into a bubbling absorption tower (tower diameter Φ400m, tower height 3m), absorbing The liquid (hard water) at the bottom of the tower is pumped out and circulated from the top, and the liquid at the bottom is stirred because the water pump is continuously pumped out and sent in to prevent the suspension from settling. The liquid-gas ratio is controlled at about 2-3l/ m3 . Under the conditions of normal pressure and normal temperature, the spray reaction is carried out, and the tail gas after the absorption reaction is discharged through the top of the absorption tower. After gas-liquid absorption for 1 minute, the pH value is 3, and the pH value of the absorption liquid is adjusted to 7 with lye to obtain a suspension. The solid-liquid separation in the sedimentation tank, the precipitation time is 30min, and the filtrate is demineralized water. Ca 2+ is 18mg/L; Mg 2+ is 10mg/L.
监测分析报告显示:该厂脱硫处理前SO2的体积百分含量为1%,经过脱硫处理后,SO2体积百分含量降低为0.01%,脱硫率达到90%以上。CO2体积百分含量为14%,经过洗涤脱钙处理后,CO2体积百分含量降低为5.6%,CO2脱除率达到60%左右。The monitoring and analysis report shows that before the desulfurization treatment, the volume percentage of SO 2 is 1%. After the desulfurization treatment, the volume percentage of SO 2 is reduced to 0.01%, and the desulfurization rate reaches more than 90%. The volume percentage of CO 2 is 14%. After washing and decalcification treatment, the volume percentage of CO 2 is reduced to 5.6%, and the removal rate of CO 2 reaches about 60%.
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CN102091516A (en) * | 2010-12-06 | 2011-06-15 | 李在水 | De-scaling and anti-scaling device by using smoke |
CN103570144B (en) * | 2012-12-28 | 2015-09-23 | 青岛啤酒股份有限公司 | The carbonic acid gas utilizing dress wine machine to arrange outward stops the method for bottle washing machine fouling |
CN103553246A (en) * | 2013-11-21 | 2014-02-05 | 武汉森泰环保工程有限公司 | Device and method for softening hard water by using carbon dioxide in flue gas |
CN103752155A (en) * | 2013-12-31 | 2014-04-30 | 上海宝钢磁业有限公司 | Method for spraying and neutralizing by wastewater generated in pure water preparation |
CN104291452B (en) * | 2014-07-02 | 2016-10-19 | 中国石油天然气集团公司 | Flue gas hardness removing device and using method thereof |
CN108483683A (en) * | 2018-06-12 | 2018-09-04 | 南京林业大学 | A kind of method and its dedicated unit removing waste water hardness using flue gas successive reaction |
CN109534537A (en) * | 2018-11-20 | 2019-03-29 | 常州大学 | A kind of gas heater waste gas utilization device for softened water |
CN114669182A (en) * | 2022-03-21 | 2022-06-28 | 云南磷化集团有限公司 | Phosphorus chemical industry by-product CO2Coupling technology for reverse flotation of phosphorite by using tail gas |
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US4085194A (en) * | 1972-05-08 | 1978-04-18 | Hitachi, Ltd. | Waste flue gas desulfurizing method |
CN1066833A (en) * | 1992-04-04 | 1992-12-09 | 淄博市周村水处理设备厂 | Make the equipment of trade effluent dealkalize with sulfurous gas |
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US4085194A (en) * | 1972-05-08 | 1978-04-18 | Hitachi, Ltd. | Waste flue gas desulfurizing method |
CN1066833A (en) * | 1992-04-04 | 1992-12-09 | 淄博市周村水处理设备厂 | Make the equipment of trade effluent dealkalize with sulfurous gas |
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JP特开2005-161224A 2005.06.23 |
JP特开2007-209942A 2007.08.23 |
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