CN103058303B - Method for separating inorganic salt substances from high-salt liquid waste - Google Patents
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Abstract
一种高含盐废液中无机盐物质的分离处理方法属于废水处理的环境保护领域。系统依次包括以下设备:蒸发器、汽化器、薄膜蒸发器、冷却螺旋推料机;使用泵将高含盐废液从蒸发器下端送入进行加热后通过管道进入汽化器,进行汽化、闪蒸分离;蒸气由汽化器上端出口出来冷凝;进入汽化器中的高含盐废液,经过汽化、闪蒸分离后得到浓缩液;浓缩液通过管道从汽化器下端循环出料口再次从蒸发器下端的进料口进入,与高含盐废水混合再次加热、汽化、蒸发,进一步浓缩得到浓缩液,该浓缩液通过管道从汽化器下端进入薄膜蒸发器得到盐浆;盐浆进入冷却螺旋推料机,得到盐泥,从而实现无机盐类物质的有效分离。该方法效率高、能耗较低。
A method for separating and treating inorganic salt substances in high-salt waste liquid belongs to the field of environmental protection of waste water treatment. The system includes the following equipment in turn: evaporator, vaporizer, thin-film evaporator, cooling screw pusher; use a pump to send high-salt waste liquid from the lower end of the evaporator for heating, and then enter the vaporizer through the pipeline for vaporization and flash separation; The steam is condensed from the upper outlet of the evaporator; the high-salt waste liquid entering the evaporator is evaporated, flashed and separated to obtain a concentrated liquid; the concentrated liquid is circulated through the pipeline from the lower end of the evaporator to the discharge port and then enters from the feed port at the lower end of the evaporator , mixed with high-salt waste water, heated again, vaporized, evaporated, and further concentrated to obtain a concentrated liquid, which enters a thin-film evaporator through a pipeline from the lower end of the vaporizer to obtain a salt slurry; the salt slurry enters a cooling screw feeder to obtain salt mud, thereby Realize the effective separation of inorganic salts. The method has high efficiency and low energy consumption.
Description
技术领域technical field
本发明涉及高含盐废液中无机盐的分离处理,属于废水处理的环境保护领域。The invention relates to the separation and treatment of inorganic salts in high-salt waste liquid, and belongs to the field of environmental protection of waste water treatment.
背景技术Background technique
高含盐废液是指含有有机物和至少总溶解固体TDS的质量分数大于两倍海水浓度即6%以上的废水。通常这类废水中除了含有大量的无机盐,如Cl-、Na+、SO4 2-、Ca2+等外,还含有有机污染物。主要来源于:(1)化工生产:化学反应不完全或化学反应副产物,尤其农药、染料等化工产品生产过程中产生大量高COD、高盐的有毒废水。(2)废水处理、循环再利用产生的。在废水处理过程中,水处理剂及酸、碱的加入带来的废水本身含盐量增大;废水经过处理,COD达标水循环再利用过程中产生的盐度较高浓缩液。所有这些都称之为高含盐度废液。这类高含盐废液,不但较普通污水有更大的污染性,而且会对土壤盐化、形成盐碱地,从而破坏土壤的植被。High-salt waste liquid refers to waste water containing organic matter and at least a mass fraction of total dissolved solids TDS greater than twice the concentration of seawater, that is, more than 6%. Usually this type of wastewater contains not only a large amount of inorganic salts, such as Cl - , Na + , SO 4 2- , Ca 2+ , but also organic pollutants. Main sources: (1) Chemical production: Incomplete chemical reaction or chemical reaction by-products, especially pesticides, dyes and other chemical products, produce a large amount of toxic wastewater with high COD and high salt. (2) Produced by waste water treatment and recycling. In the wastewater treatment process, the addition of water treatment agents, acids and alkalis will increase the salt content of the wastewater itself; after the wastewater is treated, the concentrated solution with high salinity will be produced during the recycling process of COD up to standard water. All of these are referred to as high salinity effluents. This kind of high-salt waste liquid is not only more polluting than ordinary sewage, but also salinizes the soil and forms saline-alkali land, thereby destroying the vegetation of the soil.
对于农药、染料等化工生产过程中产生的高含盐、高COD废水通常采用直接焚烧的方法进行处理。该法是将废水呈雾状喷入高温燃烧炉中,使水雾完全汽化,让废水中的有机物在炉内氧化,分解成为完全燃烧产物二氧化碳和水及无机盐灰分。一般认为COD≥100000mg/L、热值≥2500kcal/kg的高含盐废液或有机成分质量分数≥10%的含盐有机废液采用焚烧法处理较其他方法更加经济、合理。显然,对于其它高含盐废水采取直接焚烧的方法是十分不经济的。毕竟,焚烧耗能高、容易产生烟气造成对大气的污染。The high-salt and high-COD wastewater produced in the chemical production process of pesticides and dyes is usually treated by direct incineration. This method is to spray waste water into a high-temperature combustion furnace in the form of mist, so that the water mist is completely vaporized, and the organic matter in the waste water is oxidized in the furnace, and decomposed into carbon dioxide, water and inorganic salt ash, which are complete combustion products. It is generally believed that incineration is more economical and reasonable than other methods for high-salt waste liquid with COD ≥ 100,000 mg/L and calorific value ≥ 2500 kcal/kg or saline organic waste liquid with organic component mass fraction ≥ 10%. Obviously, it is very uneconomical to directly incinerate other high-salt wastewater. After all, incineration consumes a lot of energy and easily produces flue gas, which pollutes the atmosphere.
通常采用蒸发的原理对高含盐废水进行蒸发浓缩,得到高含盐浓缩废液。最后,采取深度冷却技术,通过冷却结晶工艺,使其中的无机盐得到分离处理。同时,得到回收水和含盐量仍然很高的浓缩液。其中,浓缩液返回前段工序再进行蒸发、浓缩,冷却结晶,实现无机盐类物质的进一步分离。然而,由于废水中的盐大都是可溶性的氯化物,溶解度很大、且受温度影响较小。因此,采用冷却结晶技术对浓缩含盐废液进行无机盐类物质的分离效率很低。特别是,结晶母液返回前段工艺进行再加热蒸发。导致整个工艺流程长、能耗高。由此,迫切需要开发一种高效、能耗较低的高含盐废液中无机盐物质的分离方法。Usually, the principle of evaporation is used to evaporate and concentrate high-salt wastewater to obtain high-salt concentrated waste liquid. Finally, the deep cooling technology is adopted to separate the inorganic salts through the cooling and crystallization process. At the same time, reclaimed water and a concentrate with a still high salt content are obtained. Among them, the concentrated solution is returned to the previous process for evaporation, concentration, cooling and crystallization to realize further separation of inorganic salts. However, since most of the salts in wastewater are soluble chlorides, the solubility is very large and is less affected by temperature. Therefore, the efficiency of separating inorganic salts from concentrated saline waste liquid by cooling crystallization technology is very low. In particular, the crystallization mother liquor is returned to the previous process for reheating and evaporation. Cause the whole technological process to be long, energy consumption is high. Therefore, it is urgent to develop a high-efficiency, low-energy-consumption separation method for inorganic salt substances in high-salt waste liquid.
发明内容Contents of the invention
本发明目的是开发一种高效、能耗较低的高含盐废液中无机盐物质的分离方法。The purpose of the invention is to develop a method for separating inorganic salt substances in high-salt waste liquid with high efficiency and low energy consumption.
一种高含盐废液中无机盐物质的分离处理方法,其特征在于:A method for separating and treating inorganic salt substances in high-salt waste liquid, characterized in that:
应用的系统依次包括以下设备:蒸发器、汽化器、薄膜蒸发器、冷却螺旋推料机;The applied system includes the following equipment in order: evaporator, evaporator, thin film evaporator, cooling screw pusher;
使用泵将高含盐废液从蒸发器下端送入进行加热,控制蒸发器出口温度105~120℃.被加热的高含盐废液从蒸发器上端通过管道进入汽化器,进行汽化、闪蒸分离;其中,60~70%的水变成水蒸气,并且由汽化器上端出口出来进入冷凝器进行冷凝,成为回收水;Use a pump to send high-salt waste liquid from the lower end of the evaporator for heating, and control the outlet temperature of the evaporator to 105-120°C. The heated high-salt waste liquid enters the vaporizer from the upper end of the evaporator through a pipeline for vaporization and flash separation ; Among them, 60-70% of the water turns into water vapor, and enters the condenser from the upper outlet of the vaporizer to condense and become recycled water;
进入汽化器中的高含盐废液,经过汽化、闪蒸分离后,剩下30~40%的浓缩液体;浓缩液体通过管道从汽化器下端循环出料口再次从蒸发器下端的进料口进入,与高含盐废水混合再次加热、汽化、蒸发,进一步浓缩得到浓缩液,使浓缩液的比重达到1.4~1.6;The high-salt waste liquid entering the vaporizer is vaporized and flashed and separated, leaving 30-40% of the concentrated liquid; the concentrated liquid is circulated through the pipeline from the lower end of the vaporizer to the outlet and then enters from the feed port at the lower end of the evaporator. Mix with high-salt waste water, heat again, vaporize, evaporate, and further concentrate to obtain a concentrated solution, so that the specific gravity of the concentrated solution reaches 1.4 to 1.6;
该浓缩液通过管道从汽化器下端进入薄膜蒸发器上端,进行薄膜蒸发,使浓缩液中的水蒸发70~80%,水汽出口温度控制在100~110℃,剩下20-30%的盐浆;该盐浆进入冷却螺旋推料机,通过在螺旋输送过程中得到冷却,使其温度降低到30~40℃.最后,由冷却螺旋推料机排出,得到盐泥,从而实现无机盐类物质的有效分离;The concentrated liquid enters the upper end of the thin-film evaporator from the lower end of the vaporizer through the pipeline, and performs thin-film evaporation to evaporate 70-80% of the water in the concentrated liquid. The temperature of the water vapor outlet is controlled at 100-110°C, leaving 20-30% of the salt slurry; The salt slurry enters the cooling screw feeder, and is cooled during the screw conveying process to reduce its temperature to 30-40°C. Finally, it is discharged from the cooling screw feeder to obtain salt mud, thereby realizing the separation of inorganic salts. effective separation;
在整个工艺流程中,都采用引风机维持系统处于85~95kpa的微负压状态下操作、运行。In the whole process flow, the induced draft fan is used to maintain the system to operate and run under the micro-negative pressure state of 85-95kpa.
关键设备与工艺控制参数Key equipment and process control parameters
1.薄膜蒸发器1. Thin film evaporator
(1)薄膜蒸发器的材料为316L不锈钢,钛合金或者防腐耐高温石墨材料加工而成。其属于立式设备,采用蒸汽加热。薄膜蒸发器的高径比大于2,上端封头上布置由浓缩液进料口、水汽出口和清水冲洗口,下端封头布置由盐浆出料口。内部安装带刮板的旋转轴,并且在旋转轴的上部安装由浓缩液的受液盘。浓缩液由上端封头进料口首先进入受液盘。受液盘随着旋转轴一起旋转,其旋转速度控制在45~60转/分钟。将浓缩液摔洒在薄膜蒸发器的内壁,并受到加热而蒸发。在此过程中,浓缩液随着水的蒸发,逐渐变成盐浆,并且在旋转轴上的刮板作用下流动薄膜蒸发器底部排出。其中,水蒸气则由表面蒸发器上端的水汽出口排出。期间,控制水汽出口温度100~110℃.(1) The thin film evaporator is made of 316L stainless steel, titanium alloy or anti-corrosion and high-temperature resistant graphite material. It is a vertical device and is heated by steam. The height-to-diameter ratio of the thin-film evaporator is greater than 2. The upper end head is arranged with a concentrated liquid inlet, a water vapor outlet and a clean water flushing port, and the lower end head is arranged with a salt slurry outlet. A rotating shaft with a scraper is installed inside, and a liquid receiving plate for concentrated liquid is installed on the upper part of the rotating shaft. The concentrated liquid first enters the liquid receiving pan from the feed inlet of the upper end head. The liquid receiving plate rotates together with the rotating shaft, and its rotation speed is controlled at 45-60 rpm. The concentrated liquid is sprinkled on the inner wall of the thin film evaporator and evaporated by heating. During this process, the concentrated liquid gradually turns into a salt slurry as the water evaporates, and is discharged from the bottom of the thin-film evaporator under the action of the scraper on the rotating shaft. Wherein, the water vapor is discharged from the water vapor outlet at the upper end of the surface evaporator. During this period, control the water vapor outlet temperature to 100-110°C.
(2)关键工艺控制参数(2) Key process control parameters
1)蒸发器的出口温度控制在105~120℃;浓缩液进入汽化器中的蒸发量为60~70%;1) The outlet temperature of the evaporator is controlled at 105-120°C; the evaporation rate of the concentrated liquid entering the evaporator is 60-70%;
2)盐浆在薄膜蒸发器中进行薄膜蒸发,水汽出口温度控制在100~110℃,盐浆中的水蒸发70-80%;2) The salt slurry is evaporated in a thin film evaporator, the temperature of the water vapor outlet is controlled at 100-110°C, and the water in the salt slurry evaporates by 70-80%;
3)汽化器下端进入薄膜蒸发器的浓缩液的比重控制在1.4~1.6;3) The specific gravity of the concentrated liquid entering the thin film evaporator at the lower end of the vaporizer is controlled at 1.4 to 1.6;
4)采用引风机维持系统处于微负压状态下操作、运行。4) Use the induced draft fan to maintain the operation and operation of the system in the state of slight negative pressure.
本发明是利用薄膜蒸发设备,采用一次闪蒸-薄膜蒸发-盐浆冷却工艺技术,实现高含盐废液中无机盐类物质的分离处理方法。该方法效率高、能耗较低。The invention utilizes thin-film evaporation equipment and adopts a flash evaporation-thin-film evaporation-salt slurry cooling process technology to realize the separation and treatment method of inorganic salts in high-salt waste liquid. The method has high efficiency and low energy consumption.
具体实施方式Detailed ways
实例1Example 1
一种农药生产产生的高含盐废水,其含盐量10~15%,COD为300~500mg/L。该废水使用泵从蒸发器下端送入进行加热,控制蒸发器出口温度115℃.被加热的高含盐废水从蒸发器上端通过管道进入汽化器,进行汽化、闪蒸分离。其中,70%的水变成水蒸气,并且由汽化器上端出口出来进入冷凝器进行冷凝,成为回收水。A high-salt wastewater produced by pesticide production, with a salt content of 10-15% and a COD of 300-500mg/L. The wastewater is pumped from the lower end of the evaporator for heating, and the outlet temperature of the evaporator is controlled to 115°C. The heated high-salt wastewater enters the vaporizer from the upper end of the evaporator through a pipeline for vaporization and flash separation. Among them, 70% of the water turns into water vapor, and exits from the upper end of the evaporator into the condenser for condensation to become recycled water.
进入汽化器中的高含盐废液,经过汽化、闪蒸分离后,剩下30%的浓缩液。浓缩液通过管道从蒸发器下端循环出料口再次从蒸发器下端的进料口进入,与高含盐废水混合再次加热、汽化、蒸发,进一步浓缩,使其浓缩液的比重达到1.3,再把该浓缩液通过管道从汽化器下端进入薄膜蒸发器上端,再次进行薄膜蒸发,水汽出口温度控制在100℃,使其浓缩液中的水再蒸发80%,剩下20%的盐浆。该盐浆进入冷却螺旋推料机,通过在螺旋输送过程中得到冷却,使其温度降低到30℃.最后,由冷却螺旋推料机排出,得到盐泥。The high-salt waste liquid entering the vaporizer is vaporized and flash-separated, leaving 30% of the concentrated liquid. The concentrated liquid enters through the pipeline from the outlet of the lower end of the evaporator to the feed port at the lower end of the evaporator, mixes with the high-salt waste water, heats again, vaporizes, evaporates, and further concentrates so that the specific gravity of the concentrated liquid reaches 1.3, and then puts The concentrated liquid enters the upper end of the thin-film evaporator from the lower end of the vaporizer through the pipeline, and then evaporates again. The temperature of the water vapor outlet is controlled at 100°C, so that 80% of the water in the concentrated liquid is evaporated again, leaving 20% of the salt slurry. The salt slurry enters the cooling screw feeder, and is cooled during the screw conveying process to reduce its temperature to 30°C. Finally, it is discharged from the cooling screw feeder to obtain salt mud.
盐泥在冷却螺旋推料机的作用下,将盐泥从旋转焚烧炉上端送入进行焚烧。焚烧温度控制450℃,停留焚烧时间3分钟。最后,高温固体盐渣在旋转焚烧炉的旋转作用下,从其下端排出。在焚烧过程中,将产生的高温烟气经过洗涤、降温、净化后排放。Under the action of the cooling screw pusher, the salt mud is sent from the upper end of the rotary incinerator for incineration. The incineration temperature is controlled at 450°C, and the residence incineration time is 3 minutes. Finally, the high-temperature solid salt slag is discharged from the lower end of the rotary incinerator under the action of rotation. During the incineration process, the high-temperature flue gas produced is washed, cooled, and purified before being discharged.
在整个工艺流程中,都采用引风机维持系统处于微负压状态下操作、运行。In the whole process flow, the induced draft fan is used to maintain the system to operate and run under the state of slight negative pressure.
实例2Example 2
某废水处理厂废水经过处理,COD小于100mg/L。为了实现“零”排放,该合格排放水实现采用反渗透膜进行处理,回收80%的水循环利用。剩下的20%浓废水再经过多效闪蒸,将其蒸发,回收80%水。余下的20%浓废液。该废液利用泵从蒸发器下端送入进行加热,控制蒸发器出口温度105℃.被加热的浓废液从蒸发器上端通过管道进入汽化器,进行汽化、闪蒸分离。其中,60%的水变成水蒸气,并且由汽化器上端出口出来进入冷凝器进行冷凝,成为回收水。The wastewater of a wastewater treatment plant has been treated, and the COD is less than 100mg/L. In order to achieve "zero" discharge, the qualified discharge water is treated with reverse osmosis membrane, and 80% of the water is recovered for recycling. The remaining 20% of the concentrated wastewater is evaporated through multi-effect flash evaporation and 80% of the water is recovered. The remaining 20% concentrated waste. The waste liquid is sent from the lower end of the evaporator to be heated by a pump, and the outlet temperature of the evaporator is controlled to 105°C. The heated concentrated waste liquid enters the vaporizer from the upper end of the evaporator through a pipeline for vaporization and flash separation. Among them, 60% of the water turns into water vapor, and exits from the upper end of the vaporizer into the condenser for condensation to become recycled water.
进入汽化器中的高含盐废液,经过汽化、闪蒸分离后,剩下40%的浓缩液。浓缩液通过管道从蒸发器下端循环出料口再次从蒸发器下端的进料口进入,与高含盐废水混合再次加热、汽化、蒸发,进一步浓缩,使其浓缩液的比重达到1.3,再把该浓缩液通过管道从汽化器下端进入薄膜蒸发器上端,进行薄膜蒸发,水汽出口温度控制在110℃,使其浓缩液中的水再蒸发70%,剩下30%的盐浆。该盐浆进入冷却螺旋推料机,通过在螺旋输送过程中得到冷却,使其温度降低到30℃.最后,由冷却螺旋推料机排出,得到盐泥,实现无机盐类物质的有效分离。The high-salt waste liquid entering the vaporizer is vaporized and flash-separated, leaving 40% of the concentrated liquid. The concentrated liquid enters through the pipeline from the lower end of the evaporator to the lower end of the evaporator, and then enters from the lower end of the evaporator, mixes with high-salt waste water, heats again, vaporizes, evaporates, and further concentrates to make the specific gravity of the concentrated liquid reach 1.3. The concentrated liquid enters the upper end of the thin-film evaporator from the lower end of the evaporator through the pipeline to perform thin-film evaporation. The temperature of the water vapor outlet is controlled at 110°C, so that 70% of the water in the concentrated liquid is evaporated again, leaving 30% of the salt slurry. The salt slurry enters the cooling screw feeder, and is cooled during the screw conveying process to reduce its temperature to 30°C. Finally, it is discharged from the cooling screw feeder to obtain salt mud, which realizes the effective separation of inorganic salts.
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| SE366282B (en) * | 1972-08-28 | 1974-04-22 | Atomenergi Ab | |
| DE2531295A1 (en) * | 1975-07-12 | 1977-01-20 | Naman Azhari | DISTILLATION PLANT COMBINED WITH A STEAM POWER PLANT FOR DESALINATION OF SEA WATER |
| CN202063789U (en) * | 2011-05-06 | 2011-12-07 | 山东光大科技发展有限公司 | Treatment device for waste water containing salt |
| CN102433212B (en) * | 2011-10-19 | 2016-08-03 | 北京生态岛科技有限责任公司 | The method of purification of waste lubricating oil and device |
| CN102701303B (en) * | 2012-05-29 | 2013-11-13 | 汪亮亮 | Liquid-film low-temperature-evaporation zero-emission saline wastewater treatment method |
-
2012
- 2012-11-26 CN CN2012104894019A patent/CN103058303B/en not_active Expired - Fee Related
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