CN111302505A - A kind of method and system of reverse osmosis concentrated water regeneration and recovery of calcium carbonate - Google Patents
A kind of method and system of reverse osmosis concentrated water regeneration and recovery of calcium carbonate Download PDFInfo
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Abstract
Description
技术领域technical field
本发明属于水处理技术领域,特别是涉及一种反渗透浓水再生回收碳酸钙的方法和系统。The invention belongs to the technical field of water treatment, and in particular relates to a method and a system for regenerating and recovering calcium carbonate from reverse osmosis concentrated water.
背景技术Background technique
使用反渗透设备制纯水已经被众多的工业企业和家庭广泛采用。但是,这一技术的缺点是获得纯水同时,不得不将接近50%量的高盐离子浓水淘汰掉。虽然这部分淘汰掉的浓水不会对环境造成危害,并且这种水还可以为绿化浇花和道路抑尘派上用途,但对于用水量大的工业行业诸如电厂、钢厂、化工等企业,由于淘汰水量太大,根本无法消化利用,只能选择做为工业废水排放,形成对水资源的巨大浪费。不仅如此,排放污水需要缴纳的高额费用也推高了企业成本。从长远来看,废水零排放的政策要求越来越高,反渗透浓水回收治理以及资源化利用迫在眉睫。The use of reverse osmosis equipment to produce pure water has been widely used by many industrial enterprises and households. However, the disadvantage of this technology is that when pure water is obtained, nearly 50% of the high-salt ion concentrated water has to be eliminated. Although this part of the eliminated concentrated water will not cause harm to the environment, and this water can also be used for greening watering flowers and road dust suppression, but for industrial industries with large water consumption, such as power plants, steel mills, chemical and other enterprises , Due to the large amount of eliminated water, it cannot be digested and utilized at all, and can only be discharged as industrial wastewater, resulting in a huge waste of water resources. Not only that, the high fees to be paid for discharging sewage also push up the cost of enterprises. In the long run, the policy requirements for zero discharge of wastewater are getting higher and higher, and the recovery and management of reverse osmosis concentrated water and the utilization of resources are imminent.
在反渗透浓水处理方面,众多企业采取的做法是使用高压反渗透将浓水进行二次浓缩处理,得到增浓的高盐浓水排放,以求尽量减少浓水的数量,但这种做法在付出较高代价后,也只能将浓水再回收50%,并没有取得实质性效果;还有一些企业,采用浓缩结晶手段,将浓水中的可溶性盐结晶出来,使浓水恢复到接近原水属性加以回收,这种技术,可以解决浓水回收利用问题,但是,也存在少量可溶性混合盐固废问题,特别是高额的治理成本限制了技术发展;还有一种技术趋势,是采用化学沉降法将钙镁离子从浓水中沉淀出来,将沉淀物分离后使浓水转变成原水,这种技术趋势在理论上是行得通的,但是也存在理论研究薄弱、实践缺乏认证以及形成的固废处理方面的问题。例如,中国发明专利申请号201410641681.X公开的《一种高效高回收率反渗透浓水回收处理方法及系统》,虽然提到了“采用熟石灰和纯碱对反渗透浓水进行软化或化学沉淀处理,以去除导致结垢的钙离子、镁离子和硅”的较好设想,但是,该方案本身带来的2个严重缺点却决定了该技术尚不完善和难以达到环保要求:一是该方案的浓水处理使用了碳酸钠和盐酸,将会导致浓水中氯化钠可溶性盐成分增加,终将增加废盐排放的环保隐患;二是该方案得到的固废混合物没有其它用途选择了填埋处理,这无异是造成了环境的二次污染。这也很客观地反映出现有技术存在的回收率较低、高回收率与成本急剧提高并存、高回收率与环保隐患共存的突出问题。In terms of reverse osmosis concentrated water treatment, the practice adopted by many enterprises is to use high-pressure reverse osmosis to carry out secondary concentration treatment of concentrated water to obtain concentrated high-salt concentrated water for discharge, in order to minimize the amount of concentrated water, but this approach After paying a high price, only 50% of the concentrated water can be recovered, and no substantial effect has been achieved; some companies use the method of concentration and crystallization to crystallize the soluble salt in the concentrated water, so that the concentrated water can be restored to close to Recycling the properties of raw water, this technology can solve the problem of concentrated water recycling, but there is also a small amount of soluble mixed salt solid waste, especially the high treatment cost restricts the development of technology; there is also a technical trend, which is to use chemical The sedimentation method precipitates calcium and magnesium ions from concentrated water, and separates the sediment to convert the concentrated water into raw water. This technical trend is theoretically feasible, but there are also weak theoretical research, lack of certification in practice and the formation of problems. The problem of solid waste treatment. For example, "a kind of high-efficiency and high-recovery reverse osmosis concentrated water recovery and treatment method and system" disclosed in Chinese Patent Application No. 201410641681.X, although it is mentioned that "use slaked lime and soda ash to soften or chemically precipitate the reverse osmosis concentrated water, It is a better idea to remove calcium ions, magnesium ions and silicon that cause scaling. However, the two serious shortcomings brought about by this solution determine that the technology is not perfect and it is difficult to meet environmental protection requirements: first, the Concentrated water treatment uses sodium carbonate and hydrochloric acid, which will increase the soluble salt content of sodium chloride in the concentrated water, which will eventually increase the environmental protection hazard of waste salt discharge; second, the solid waste mixture obtained in this scheme has no other uses and chooses landfill treatment , which is tantamount to causing secondary pollution to the environment. This also objectively reflects the outstanding problems of the existing technology, such as low recovery rate, coexistence of high recovery rate and sharp increase in cost, and coexistence of high recovery rate and hidden dangers of environmental protection.
因此,在反渗透浓水处理领域,还普遍存在废水不能全部利用、运行成本过高、使用某些化学药剂导致环保隐患、以及形成固废导致的二次污染问题,即使在用化学手段处理浓水方面,比如沉淀法处理技术领域还存在理论空白,现有技术缺乏理论依据和实践支撑,甚至还存在误区和谬误,需要各个行业技术的交互渗透与革新。Therefore, in the field of reverse osmosis concentrated water treatment, there are still common problems that the wastewater cannot be fully utilized, the operating cost is too high, the use of certain chemicals causes environmental protection hazards, and the formation of solid waste results in secondary pollution. In terms of water, for example, there are still theoretical gaps in the field of precipitation treatment technology. The existing technology lacks theoretical basis and practical support, and there are even misunderstandings and fallacies. Interpenetration and innovation of technologies in various industries are needed.
发明内容SUMMARY OF THE INVENTION
本发明的目的是提供一种反渗透浓水再生回收碳酸钙的方法及其系统,在将浓水中钙、镁、铁、铝、锌等硬度离子资源化沉淀分离同时,将浓水再生为成分接近原水的清水,在实现废水和固废零排放同时获得碳酸钙,在大幅降低成本同时获得较高经济效益。The purpose of this invention is to provide a kind of method and system for reclaiming calcium carbonate by reverse osmosis concentrated water regeneration, and at the same time of recycling and precipitation of hardness ions such as calcium, magnesium, iron, aluminum, zinc in concentrated water, and regenerating concentrated water into components Clean water close to raw water can achieve zero discharge of wastewater and solid waste while obtaining calcium carbonate, greatly reducing costs and obtaining high economic benefits.
本发明依据的技术理论是:以北方地下水水质为基础,大多呈现碳酸氢钙型暂时硬度的原水水质,所以反渗透排出浓水成分主要为Ca(HCO3)2和少量Mg(HCO3)2,存在少量Fe2 +、AL3+、Zn2+等高价金属离子盐和Na+、K+、NH4 +等低价离子盐,还存在一些SO4 2-、CI-、NO3 -等离子,其中:Ca(HCO3)2和Mg(HCO3)2两盐占浓水含盐量的95%以上,总含量为8-15mmol/L。通过化学沉淀法将浓水中钙镁离子以及高价金属离子沉淀分离出来得到含有少量镁及微量铁、铝、锌的碳酸钙产品,使浓水再生转化为原水。向浓水中加入Ca(OH)2浆乳,可以使Ca(HCO3)2反应形成CaCO3沉淀,使Mg(HCO3)2反应形成MgCO3沉淀;由于Ca(OH)2浆乳加入,水的PH值升高,其微量存在的铁、铝、锌离子便以氢氧化物状态从浓水中沉淀出来;在高效分离了钙镁离子以及铁、铝、锌离子后,浓水的总硬度降低至与原水成分接近的清水获得再生,这里,清水即为原水,也可称之为再生原水。The technical theory on which the present invention is based is: based on the quality of groundwater in the north, most of the raw water quality has calcium bicarbonate type temporary hardness, so the components of the concentrated water discharged by reverse osmosis are mainly Ca(HCO 3 ) 2 and a small amount of Mg(HCO 3 ) 2 , there are a small amount of high-valent metal ion salts such as Fe 2 + , AL 3+ , Zn 2+ and low-valent ion salts such as Na + , K + , NH 4 + , and some SO 4 2- , CI - , NO 3 - plasma , wherein: the two salts of Ca(HCO 3 ) 2 and Mg(HCO 3 ) 2 account for more than 95% of the salt content of the concentrated water, and the total content is 8-15mmol/L. The calcium and magnesium ions and high-valent metal ions in the concentrated water are precipitated and separated by chemical precipitation to obtain calcium carbonate products containing a small amount of magnesium and trace amounts of iron, aluminum and zinc, and the concentrated water is regenerated and converted into raw water. Adding Ca(OH) 2 slurry to concentrated water can make Ca(HCO 3 ) 2 react to form CaCO 3 precipitation, and make Mg(HCO 3 ) 2 react to form MgCO 3 precipitation; due to the addition of Ca(OH) 2 slurry, water The PH value of the iron, aluminum and zinc ions in trace amounts will be precipitated from the concentrated water in the form of hydroxides; after the calcium and magnesium ions and iron, aluminum and zinc ions are efficiently separated, the total hardness of the concentrated water will decrease. The clean water whose composition is close to the raw water is regenerated. Here, the clean water is the raw water, which can also be called the regenerated raw water.
为达到上述目的,本发明提供了一种反渗透浓水再生回收碳酸钙的方法,包括以下步骤:In order to achieve the above object, the invention provides a method for reclaiming calcium carbonate from reverse osmosis concentrated water regeneration, comprising the following steps:
a、沉淀剂Ca(OH)2浆乳制备:采用生石灰CaO块或者粉、再或者熟石灰粉消解法制备,以生石灰CaO粉计,在搅拌状态向消解器中定量加入浓水和生石灰,浓水与生石灰CaO的质量比为10∶5-3,发生消解反应得到Ca(OH)2浆乳,消解放热反应完成后,加浓水将Ca(OH)2浆乳调整成含一定CaO固含量的浆乳,用石灰乳泵将调整好的Ca(OH)2浆乳泵入石灰乳计量罐待用;即:a. Preparation of precipitant Ca(OH) 2 slurry milk: use quicklime CaO block or powder, or slaked lime powder digestion method to prepare, based on quicklime CaO powder, quantitatively add concentrated water and quicklime to the digester in a stirring state, and concentrated water The mass ratio with quicklime CaO is 10:5-3, and the digestion reaction occurs to obtain Ca(OH) 2 slurry. After the digestion and exothermic reaction is completed, the Ca(OH) 2 slurry is adjusted to contain a certain solid content of CaO by adding concentrated water. The adjusted Ca(OH) 2 slurry is pumped into the lime milk metering tank with a lime milk pump for use; namely:
CaO+H2O→Ca(OH)2;CaO+H 2 O→Ca(OH) 2 ;
b、用沉淀剂与浓水反应沉淀出硬度离子再生出原水:在沉淀反应器中定量加入浓水和一定量的沉淀剂Ca(OH)2浆乳,使之与浓水中的硬度离子发生沉淀反应,将主含量的钙离子Ca2+沉淀反应形成难溶解的CaCO3沉淀,将次含量的镁离子Mg2+沉淀反应形成难溶解的MgCO3沉淀,将微量存在的铁离子Fe2+沉淀反应形成Fe(OH)2沉淀,铝离子AL3+沉淀反应形成AL(OH)3沉淀,锌离子Zn2+沉淀反应形成Zn(OH)2沉淀,沉淀剂Ca(OH)2浆乳的加入量改变了再生原水的总硬度、总碱度以及酚酞碱度,当沉淀反应器中再生原水总硬度稳定在2-4mmoL/L之间,且总碱度稳定在1-3mmoL/L之间时,以酚酞碱度不大于0.1mmoL/L指标作为判断反应终点标准,表示浓水经去掉大部分硬度离子后再生成原水或者清水,即:b. Use precipitant to react with concentrated water to precipitate hardness ions to regenerate raw water: quantitatively add concentrated water and a certain amount of precipitant Ca(OH) 2 slurry to the precipitation reactor to precipitate it with the hardness ions in the concentrated water Reaction, the main content of calcium ions Ca 2+ precipitation reaction to form insoluble CaCO 3 precipitation, the secondary content of magnesium ions Mg 2+ precipitation reaction to form insoluble MgCO 3 precipitation, the trace presence of iron ions Fe 2+ precipitation Reaction to form Fe(OH) 2 precipitation, aluminum ion AL 3+ precipitation reaction to form AL(OH) 3 precipitation, zinc ion Zn 2+ precipitation reaction to form Zn(OH) 2 precipitation, addition of precipitant Ca(OH) 2 slurry The amount changes the total hardness, total alkalinity and phenolphthalein alkalinity of the regenerated raw water. When the total hardness of the regenerated raw water in the precipitation reactor is stable between 2-4 mmoL/L, and the total alkalinity is stable between 1-3 mmoL/L , with the phenolphthalein alkalinity not greater than 0.1 mmoL/L as the criterion for judging the end point of the reaction, indicating that the concentrated water will generate raw water or clear water after removing most of the hardness ions, namely:
Ca(HCO3)2+Ca(OH)2→2CaCO3↓+2H2OCa(HCO 3 ) 2 +Ca(OH) 2 →2CaCO 3 ↓+2H 2 O
Mg(HCO3)2+Ca(OH)2→CaCO3↓+MgCO3↓+2H2OMg(HCO 3 ) 2 +Ca(OH) 2 →CaCO 3 ↓+MgCO 3 ↓+2H 2 O
Ca(OH)2→Ca2++2OH- Ca(OH) 2 →Ca 2+ +2OH -
Fe2++2OH-→Fe(OH)2↓Fe 2+ +2OH - →Fe(OH) 2 ↓
AL3++3OH-→AL(OH)3↓AL 3+ +3OH - →AL(OH) 3 ↓
Zn2++2OH-→Zn(OH)2↓;Zn 2+ +2OH - →Zn(OH) 2 ↓;
c、回收碳酸钙:将步骤b得到的含有沉淀物的再生原水用料浆泵泵入过滤机中进行固液分离,滤液为成分接近原水的清水,送清水储槽储存为原水使用,用清水泵将再生原水送入原水系统;滤饼为本发明所回收碳酸钙的原料,通过皮带机将滤饼输送至干燥器中干燥,将干燥产物送粉碎机粉碎,将粉料包装获得含镁轻质碳酸钙产品。c. Recovering calcium carbonate: the regenerated raw water containing the precipitate obtained in step b is pumped into a filter for solid-liquid separation with a slurry pump, the filtrate is clean water with a composition close to raw water, and is sent to a clean water storage tank for storage as raw water for use. The water pump sends the regenerated raw water into the raw water system; the filter cake is the raw material of the recovered calcium carbonate in the present invention. Quality calcium carbonate products.
作为优选,步骤a中定量加入浓水和生石灰质量比例为3∶1,消解放热反应完成后,加浓水调整成CaO固含量为10%w/w左右的Ca(OH)2浆乳。Preferably, in step a, the mass ratio of concentrated water and quicklime is quantitatively added to be 3:1, and after the digestion and exothermic reaction is completed, the concentrated water is added to adjust the Ca(OH) 2 slurry with a CaO solid content of about 10% w/w.
作为优选,步骤a中加入生石灰的性状为石灰粉,质量要求为CaO≥93%,细度200目筛余物≤1%,Fe≤0.1%。Preferably, the properties of quicklime added in step a are lime powder, the quality requirements are CaO≥93%, fineness 200 mesh sieve residue≤1%, Fe≤0.1%.
作为优选,步骤a可直接用熟石灰粉Ca(OH)2制备沉淀剂Ca(OH)2浆乳,并可直接加入步骤b与浓水反应沉淀出硬度离子再生出原水。Preferably, in step a, slaked lime powder Ca(OH) 2 can be directly used to prepare precipitant Ca(OH) 2 slurry, and step b can be directly added to react with concentrated water to precipitate hardness ions to regenerate raw water.
为达到上述目的,本发明还提供了一种反渗透浓水再生回收碳酸钙的系统,其特征在于:包括通过管道依次连接的消解器、石灰乳泵、石灰乳计量罐、沉淀反应器、料浆泵、清水泵、过滤机、清水槽及由物料输送连接或者匹配连接的皮带机、干燥器、粉碎机,其中:In order to achieve the above object, the present invention also provides a system for regenerating and reclaiming calcium carbonate from reverse osmosis concentrated water, which is characterized in that it includes a digester, a lime milk pump, a lime milk metering tank, a sedimentation reactor, a material Slurry pump, clean water pump, filter, clean water tank and belt conveyor, dryer and pulverizer connected or matched by material conveying, among which:
所述消解器包括搅拌器、石灰加料口、与反渗透浓水管相连接的反渗透浓水加入口,用于进行浓水与生石灰块/或者石灰粉/再或者熟石灰粉的消解反应,制备Ca(OH)2浆乳;The digester includes an agitator, a lime feeding port, and a reverse osmosis concentrated water feeding port connected with the reverse osmosis concentrated water pipe, which is used for the digestion reaction of the concentrated water and quicklime block/or lime powder/and then slaked lime powder to prepare Ca. (OH) 2 Serum milk;
所述石灰乳泵通过管道连接在消解器与石灰乳计量罐之间,用于将消解器制备好的Ca(OH)2浆乳泵送到石灰乳计量罐中;The milk of lime pump is connected between the digester and the milk of lime metering tank through a pipeline, and is used to pump the Ca (OH) slurry prepared by the digester into the milk of lime metering tank;
所述的石灰乳计量罐进料口与石灰乳泵连接,所述的石灰乳计量罐出料口与沉淀反应器加料口相连接;The feeding port of the milk of lime metering tank is connected with the milk of lime pump, and the discharging port of the milk of lime metering tank is connected with the feeding port of the precipitation reactor;
所述沉淀反应器包括搅拌器、与石灰乳计量罐相连接的加料口、与反渗透浓水管相连接的反渗透浓水加入口,用于完成用沉淀剂与浓水反应沉淀出硬度离子获得/或者再生出原水的反应;The precipitation reactor includes a stirrer, a feeding port connected with the lime milk metering tank, and a reverse osmosis concentrated water feeding port connected with the reverse osmosis concentrated water pipe, which is used to complete the reaction of precipitating agent and concentrated water to precipitate hardness ions to obtain / or the reaction of regenerating raw water;
所述的料浆泵通过管道连接在沉淀反应器与过滤机之间,用于将沉淀反应器中再生的原水与沉淀混合料浆泵入过滤机中进行固液分离;The slurry pump is connected between the precipitation reactor and the filter through a pipeline, and is used for pumping the regenerated raw water and the precipitation mixed slurry in the precipitation reactor into the filter for solid-liquid separation;
所述的清水槽与过滤机清水出口相连接,用于储存过滤机滤液分离出的再生原水,所述清水泵连接在清水槽与原水系统之间,用于将再生好的原水送回原水系统;The clean water tank is connected with the clean water outlet of the filter, and is used to store the regenerated raw water separated from the filtrate of the filter. The clean water pump is connected between the clean water tank and the raw water system to return the regenerated raw water to the raw water system. ;
所述的皮带机设置在过滤机滤饼出口,用于将滤饼输送至干燥器中;The belt conveyor is arranged at the filter cake outlet of the filter, and is used for conveying the filter cake to the dryer;
所述的干燥器设置在皮带机与粉碎机之间,用于将皮带机输送的滤饼干燥,所述的干燥器进口与皮带机出口相匹配连接,所述的干燥器出口与粉碎机进口匹配连接;The dryer is arranged between the belt conveyor and the pulverizer, and is used to dry the filter cake conveyed by the belt conveyor. The inlet of the dryer is matched and connected with the outlet of the belt conveyor, and the outlet of the dryer is connected with the inlet of the pulverizer. matching connection;
所述的粉碎机包括与干燥器出口相对接的进料口以及粉料碳酸钙出口,用于将干燥好的物料粉碎成碳酸钙成品。The pulverizer includes a feeding port connected to the outlet of the dryer and an outlet for powdered calcium carbonate, which is used for pulverizing the dried material into a finished product of calcium carbonate.
与现有技术相比,本发明的有益效果体现在:Compared with the prior art, the beneficial effects of the present invention are embodied in:
本发明提供的一种反渗透浓水再生回收碳酸钙的方法及其系统,采用Ca(OH)2浆乳沉淀浓水中的钙、镁、铁、铝、锌杂质离子,使之分别形成难溶解的碳酸钙、碳酸镁、氢氧化铁、氢氧化铝以及氢氧化锌沉淀,高效快速降低了浓水硬度,除回收出碳酸钙产品外,浓水获得再生变成原水。与现有技术相比:本发明在技术创新层面完善了化学沉淀法用于浓水再生的理论和实践基础,通过废水再生领域与无机盐工业技术的衔接突破,达到无废水和固废产生条件下浓水再生成原水的目的,显示出极其明显的技术进步,其浓水资源化利用且回收出高附加值碳酸钙成品变废为宝的能力代表了今后的发展方向,其技术方案本身表现的投资少、配套方便、操作简单、运行成本低等方面优点决定了其广阔的推广前景。 The invention provides a method and a system for regenerating and recovering calcium carbonate from reverse osmosis concentrated water. Calcium carbonate, magnesium carbonate, iron hydroxide, aluminum hydroxide and zinc hydroxide are precipitated, which effectively and quickly reduces the hardness of concentrated water. In addition to recovering calcium carbonate products, the concentrated water is regenerated and turned into raw water. Compared with the prior art: the present invention improves the theoretical and practical basis of the chemical precipitation method for the regeneration of concentrated water at the level of technological innovation, and achieves the conditions of no waste water and solid waste generation through the connection and breakthrough of the field of waste water regeneration and inorganic salt industrial technology. The purpose of regenerating concentrated water into raw water shows extremely obvious technological progress. Its ability to reuse concentrated water and recover high value-added calcium carbonate products and turn waste into treasure represents the future development direction. The advantages of low investment, convenient matching, simple operation and low operating cost determine its broad promotion prospects.
附图说明Description of drawings
以下结合附图及实施例,对本发明作进一步描述,显而易见地,下面描述中的附图仅仅是本发明的一种实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。The present invention will be further described below with reference to the accompanying drawings and embodiments. Obviously, the accompanying drawings in the following description are only an embodiment of the present invention. For those of ordinary skill in the art, under the premise of no creative work , other drawings can also be obtained from these drawings.
图1为本发明一种反渗透浓水再生回收碳酸钙的方法及其系统配置示意图;图中:1-消解器,2-石灰乳泵,3-石灰乳计量罐,4-沉淀反应器,5-料浆泵,6-清水泵,7-过滤机,8-皮带机,9-清水储槽,10-干燥器,11-粉碎机Fig. 1 is a kind of reverse osmosis concentrated water regeneration method and system configuration schematic diagram of calcium carbonate recovery of the present invention; among the figure: 1-digester, 2-lime milk pump, 3-lime milk metering tank, 4-precipitation reactor, 5-Slurry pump, 6-Clean water pump, 7-Filter, 8-Belt conveyor, 9-Clean water storage tank, 10-Dryer, 11-Pulverizer
具体实施方式Detailed ways
实施例1:由图1可见,本发明提供一种反渗透浓水再生回收碳酸钙的方法,包括以下步骤:Embodiment 1: as can be seen from Figure 1, the present invention provides a kind of method of reverse osmosis concentrated water regeneration reclaiming calcium carbonate, comprises the following steps:
a、沉淀剂Ca(OH)2浆乳制备:采用生石灰粉CaO消解法制备,在搅拌状态向消解器1中加入1000Kg浓水,再投入生石灰粉300Kg,使之发生消解反应生成Ca(OH)2浆乳,消解放热反应完成后,再加浓水1500Kg将Ca(OH)2浆乳调整成便于输送且CaO固含量10%的浆乳,用石灰乳泵2将调整好的Ca(OH)2浆乳泵入石灰乳计量罐3待用;a. Preparation of precipitant Ca(OH) 2 slurry: prepared by the digestion method of quicklime powder CaO, add 1000Kg of concentrated water to the
b、用沉淀剂与浓水反应沉淀出硬度离子再生出原水:在沉淀反应器4中加入100吨浓水,再加入0.6吨石灰乳计量罐3中的沉淀剂Ca(OH)2浆乳,使之与浓水中的硬度离子发生沉淀反应,将主含量的钙离子Ca2+沉淀反应形成难溶解的CaCO3沉淀,将次含量的镁离子Mg2+沉淀反应形成难溶解的MgCO3沉淀,将微量存在的铁离子Fe2+沉淀反应形成Fe(OH)2沉淀,铝离子AL3+沉淀反应形成AL(OH)3沉淀;沉淀剂Ca(OH)2浆乳的加入量改变了再生水的总硬度、总碱度以及酚酞碱度,当沉淀反应器4中再生原水总硬度稳定在2-4mmoL/L之间,且总碱度稳定在1-3mmoL/L之间时,以酚酞碱度不大于0.1mmoL/L指标作为判断反应终点标准,表示浓水经去掉大部分硬度离子后再生成原水;B, react with precipitant and concentrated water to precipitate hardness ions and regenerate raw water: add 100 tons of concentrated water in
c、回收碳酸钙:将步骤b得到的含有沉淀物的再生原水用料浆泵5压入过滤机7进行过滤分离,滤液为成分接近原水的清水,送清水储槽9储存,用清水泵6将再生原水送入原水系统;滤饼为本发明所回收碳酸钙的原料,通过皮带机8将滤饼输送至干燥器10进行干燥,干燥产物通过干燥器10出口匹配粉碎机11入口进行粉碎、粉料包装获得含镁轻质碳酸钙产品。c, reclaiming calcium carbonate: the regenerated raw water containing sediment obtained in step b is pressed into filter 7 with
实施例2:由图1可见,本发明提供一种反渗透浓水再生回收碳酸钙的方法,包括以下步骤:Embodiment 2: as can be seen from Figure 1, the present invention provides a kind of method that reverse osmosis concentrated water regeneration reclaims calcium carbonate, comprises the following steps:
a、沉淀剂Ca(OH)2浆乳制备:采用生石灰块CaO消解法制备,在搅拌状态向消解器1中加入1000Kg浓水,再投入生石灰块320Kg,使之发生消解反应得到Ca(OH)2浆乳,消解放热反应完成后,再加浓水1500Kg将Ca(OH)2浆乳调整成便于输送且CaO固含量10%左右的浆乳,用石灰乳泵2将调整好的Ca(OH)2浆乳泵入石灰乳计量罐3待用;a. Preparation of precipitant Ca(OH) 2 slurry milk: prepared by using quicklime block CaO digestion method, adding 1000Kg of concentrated water to
b、用沉淀剂与浓水反应沉淀出硬度离子再生出原水:在沉淀反应器4中加入100吨浓水,再加入0.7吨石灰乳计量罐3中的沉淀剂Ca(OH)2浆乳,使之与浓水中的硬度离子发生沉淀反应;通过检测再生水的总硬度、总碱度以及酚酞碱度控制反应终点,当沉淀反应器4中再生原水总硬度稳定在2-4mmoL/L之间,且总碱度稳定在1-3mmoL/L之间时,以酚酞碱度不大于0.1mmoL/L指标作为判断反应终点标准,表示浓水经去掉大部分硬度离子后再生成原水;B, react with precipitant and concentrated water to precipitate hardness ions and regenerate raw water: add 100 tons of concentrated water in
c、回收碳酸钙:将步骤b得到的含有沉淀物的再生原水用料浆泵5压入过滤机7进行过滤分离,滤液为成分接近原水的清水,送清水储槽9储存,用清水泵6将再生原水送入原水系统;滤饼为本发明所回收碳酸钙的原料,通过皮带机8将滤饼输送至干燥器10进行干燥,干燥产物送粉碎机11进行粉碎、包装获得含镁轻质碳酸钙产品。c, reclaiming calcium carbonate: the regenerated raw water containing sediment obtained in step b is pressed into filter 7 with
实施例3:由图1可见,本发明提供一种反渗透浓水再生回收碳酸钙的方法,包括以下步骤:Embodiment 3: as can be seen from Figure 1, the present invention provides a kind of method of reverse osmosis concentrated water regeneration reclaiming calcium carbonate, comprises the following steps:
a、沉淀剂Ca(OH)2浆乳制备:采用熟石灰Ca(OH)2粉直接化浆制Ca(OH)2浆乳,在搅拌状态向消解器1中加入3000Kg浓水,再投入熟石灰Ca(OH)2粉500Kg,使之化浆得到Ca(OH)2浆乳,之后用石灰乳泵2将调整好的Ca(OH)2浆乳泵入石灰乳计量罐3待用;a. Preparation of precipitating agent Ca(OH) 2 slurry milk: use slaked lime Ca(OH) 2 powder to directly pulp to make Ca(OH) 2 slurry milk, add 3000Kg of concentrated water to
b、用沉淀剂与浓水反应沉淀出硬度离子再生出原水:在沉淀反应器4中加入100吨浓水,再加入0.6吨来自石灰乳计量罐3中的沉淀剂Ca(OH)2浆乳,使之与浓水中的硬度离子发生沉淀反应;通过检测再生原水的总硬度、总碱度以及酚酞碱度控制反应终点,当沉淀反应器4中再生原水总硬度稳定在2-4mmoL/L之间,且总碱度稳定在1-3mmoL/L之间时,以酚酞碱度不大于0.1mmoL/L指标作为判断反应终点标准,表示浓水经去掉大部分硬度离子后再生成原水;b, react with precipitant and concentrated water to precipitate hardness ions and regenerate raw water: add 100 tons of concentrated water in
c、回收碳酸钙:将步骤b得到的含有沉淀物的再生原水用料浆泵5压入过滤机7进行过滤分离,滤液为成分接近原水的清水,送清水储槽9储存,用清水泵6将再生原水送入原水系统;滤饼为本发明所回收碳酸钙的原料,通过皮带机8将滤饼输送至于燥器10进行干燥,干燥产物送粉碎机11进行粉碎、包装获得含镁轻质碳酸钙产品。c, reclaiming calcium carbonate: the regenerated raw water containing sediment obtained in step b is pressed into filter 7 with
实施例4:如图1所示,本发明还提供了一种反渗透浓水再生回收碳酸钙的系统,其特征在于:包括通过管道依次连接的消解器1、石灰乳泵2、石灰乳计量罐3、沉淀反应器4、料浆泵5、清水泵6、过滤机7、清水槽8及由物料输送连接或者匹配连接的皮带机9、干燥器10、粉碎机11,其中:Embodiment 4: as shown in Figure 1, the present invention also provides a kind of system of reverse osmosis concentrated water regeneration and reclaiming calcium carbonate, it is characterized in that: comprise
所述消解器1包括搅拌器、石灰加料口、与反渗透浓水管相连接的反渗透浓水加入口,用于进行浓水与生石灰块/或者石灰粉/再或者熟石灰粉的消解反应,制备Ca(OH)2浆乳;The
所述石灰乳泵2通过管道连接在消解器1与石灰乳计量罐3之间,用于将消解器1制备好的Ca(OH)2浆乳泵送到石灰乳计量罐3中;Described milk of
所述的石灰乳计量罐3进料口与石灰乳泵2连接,所述的石灰乳计量罐3出料口与沉淀反应器4加料口相连接;The feeding port of the milk of
所述沉淀反应器4包括搅拌器、与石灰乳计量罐3相连接的加料口、与反渗透浓水管相连接的反渗透浓水加入口,用于完成用沉淀剂与浓水反应沉淀出硬度离子再生出原水的反应;The
所述的料浆泵5通过管道连接在沉淀反应器4与过滤机7之间,用于将沉淀反应器4中再生的原水与沉淀混合料浆泵入过滤机7中进行固液分离;The
所述的清水槽9与过滤机7清水出口相连接,用于储存过滤机7滤液分离出的再生原水,所述清水泵6连接在清水槽9与原水系统之间,用于将再生好的原水送回原水系统;The
所述的皮带机8设置在过滤机7滤饼出口,用于将滤饼输送至干燥器10中;The
所述的干燥器10设置在皮带机8与粉碎机11之间,用于将皮带机8输送的滤饼干燥,所述的干燥器10进口与皮带机8出口相匹配连接,所述的干燥器10出口与粉碎机11进口匹配连接;The
所述的粉碎机11包括与干燥器10出口相对接的进料口以及粉料碳酸钙出口,用于将干燥好的物料粉碎成碳酸钙成品。The pulverizer 11 includes a feed port connected to the outlet of the
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Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1041340A (en) * | 1988-09-29 | 1990-04-18 | 水利电力部西北电力工程承包公司 | The lime treatment deslagging of water utilizes Processes and apparatus again |
US20060196836A1 (en) * | 2002-11-05 | 2006-09-07 | Aharon Arakel | Process and apparatus for the treatment of saline water |
CN102838235A (en) * | 2012-09-14 | 2012-12-26 | 北京市自来水集团有限责任公司 | Method for removing underground water hardness by combination of lime and ultrafiltration |
CN212315717U (en) * | 2020-02-25 | 2021-01-08 | 邢台润天环保科技有限公司 | System for reverse osmosis concentrated water regeneration retrieves calcium carbonate |
-
2020
- 2020-02-25 CN CN202010137464.2A patent/CN111302505A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1041340A (en) * | 1988-09-29 | 1990-04-18 | 水利电力部西北电力工程承包公司 | The lime treatment deslagging of water utilizes Processes and apparatus again |
US20060196836A1 (en) * | 2002-11-05 | 2006-09-07 | Aharon Arakel | Process and apparatus for the treatment of saline water |
CN102838235A (en) * | 2012-09-14 | 2012-12-26 | 北京市自来水集团有限责任公司 | Method for removing underground water hardness by combination of lime and ultrafiltration |
CN212315717U (en) * | 2020-02-25 | 2021-01-08 | 邢台润天环保科技有限公司 | System for reverse osmosis concentrated water regeneration retrieves calcium carbonate |
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