CN114291916A - System and method for recycling o-aminophenol from o-aminophenol acidification wastewater - Google Patents
System and method for recycling o-aminophenol from o-aminophenol acidification wastewater Download PDFInfo
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Abstract
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技术领域technical field
本发明涉及一种化工品生产中废水处理方法,具体涉及一种邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理方法,还涉及配套的回收处理装置结构的改进。The invention relates to a method for treating wastewater in the production of chemical products, in particular to a method for recovering and treating o-aminophenol in o-aminophenol acidification wastewater, and also relates to the improvement of the structure of a matching recovery and treatment device.
背景技术Background technique
邻氨基苯酚即2-氨基苯酚,它是一种重要的医药精细化工中间体,化学式为CH(OH)NH,白色或浅灰色结晶粉,久置时转变为棕色或黑色,广泛应用于制造硫化染料、偶氮染料、毛皮染料和荧光增白剂,以及医药、塑料固化剂等,随着医药和印染行业的快速发展,对邻氨基苯酚这一化工中间体的市场需求持续上升,其价位随即水涨船高,但国内目前大规模的邻氨基苯酚生产工艺主要以催化加氢法为主,在生产过程中产生的废水具有盐含量高、水量大、有机物浓度高、难生化并具有一定的毒性,不但造成生产企业的排放负担,而且由于生产废水中含有的邻氨基苯酚不能回收而造成企业的经济损失,因此,该废水处理迫在眉睫。Ortho-aminophenol is 2-aminophenol. It is an important pharmaceutical fine chemical intermediate. The chemical formula is CH(OH)NH. It is white or light gray crystalline powder. Dyestuffs, azo dyes, fur dyes and optical brighteners, as well as pharmaceuticals, plastic curing agents, etc. With the rapid development of the pharmaceutical and printing and dyeing industries, the market demand for o-aminophenol, a chemical intermediate, continues to rise, and its price immediately rises However, the current large-scale o-aminophenol production process in China is mainly based on catalytic hydrogenation. The wastewater produced in the production process has high salt content, large water volume, high organic matter concentration, difficult to biochemically and has certain toxicity. Not only It causes the discharge burden of the production enterprise, and the economic loss of the enterprise is caused because the o-aminophenol contained in the production wastewater cannot be recovered. Therefore, the wastewater treatment is imminent.
目前邻氨基苯酚酸化废水处理应用的工艺主要有以下几种:一是活性炭脱色配合芬顿氧化法,但存在大量的污泥成为危废,而且污泥中的邻氨基苯酚无法回收利用,造成一定的经济损失;二是电化学氧化法,其特征在于由三维电极体系构成的单室反应器,通过电化学氧化法深度处理邻氨基苯酚废水。但其工艺较为复杂、对人员以及设备要求过高导致使用具有局限性;三是采用配合芬顿氧化法的应用对邻氨基苯酚酸化废水处理,该工艺以微电解及芬顿氧化法几种工艺相结合的处理方法,工艺相对复杂、操作难度较大,期间大量用到酸、碱等腐蚀性液体,增加处理风险,处理费用较高,而且处理效率相对较低。At present, there are mainly the following processes for o-aminophenol acidification wastewater treatment application: First, activated carbon decolorization combined with Fenton oxidation method, but there is a large amount of sludge that becomes hazardous waste, and the o-aminophenol in the sludge cannot be recycled, resulting in certain The second is the electrochemical oxidation method, which is characterized by a single-chamber reactor composed of a three-dimensional electrode system, and the o-aminophenol wastewater is further treated by the electrochemical oxidation method. However, its process is relatively complicated, and the requirements for personnel and equipment are too high, which leads to limitations in its use; the third is to use the application of Fenton oxidation method to treat o-aminophenol acidification wastewater. This process uses several processes of micro-electrolysis and Fenton oxidation method. The combined treatment method has relatively complex process and relatively difficult operation. During the period, a large amount of corrosive liquids such as acid and alkali are used, which increases the treatment risk, the treatment cost is high, and the treatment efficiency is relatively low.
近年来有树脂应用于邻氨基苯酚废水处理的应用案例,例如:公布号为CN102910757A【一种邻硝基苯酚生产废水处理工艺】中提出了一种用XDA系列大孔吸附树脂处理邻硝基苯酚生产废水的方法,并用臭氧对吸附液中剩余有机物进行氧化处理,该方法由于未对树脂进行激活处理,因此导致邻硝基苯酚的回收率偏低,同时存在臭氧氧化去除COD的处理成本较高,并且效果有限等局限性。In recent years, there have been application cases of resins used in the treatment of o-aminophenol wastewater. For example, in the publication number CN102910757A [a process for the treatment of o-nitrophenol production wastewater], a method of treating o-nitrophenol with XDA series macroporous adsorption resins was proposed. The method of producing wastewater, and using ozone to oxidize the remaining organic matter in the adsorption liquid, this method does not activate the resin, so the recovery rate of o-nitrophenol is low, and the treatment cost of ozone oxidation to remove COD is high at the same time. , and has limitations such as limited effects.
公布号为CN 107129078 A【邻氨基苯酚废水处理及资源化方法】,该工艺结合树脂吸附、微电解及芬顿氧化法几种工艺相结合的处理方法,对邻氨基苯酚废水进行处理,高效去除废水中的邻氨基苯酚和色度,但该处理方法存在的缺陷是工艺相对复杂、操作难度大,期间大量用到酸、碱等腐蚀性液体,处理费用较大。The publication number is CN 107129078 A [O-aminophenol wastewater treatment and resource utilization method]. This process combines resin adsorption, micro-electrolysis and Fenton oxidation process to treat the o-aminophenol wastewater and remove it efficiently. o-aminophenol and chroma in wastewater, but the defects of this treatment method are that the process is relatively complicated, the operation is difficult, and a large amount of corrosive liquids such as acid and alkali are used during the period, and the treatment cost is relatively large.
公布号为CN108793493A【一种浓盐水中邻氨基苯酚回收处理方法】,公开了一种利用物理吸附法将高盐废水中含有的大量邻氨基苯酚进行回收利用,其将浓盐水中的高浓邻氨基苯酚生产废水进行调pH值后通入大孔苯乙烯系吸附树脂,将邻氨基苯酚吸附在大孔苯乙烯系吸附树脂上,然后用有机溶剂对吸附饱和的大孔苯乙烯系吸附树脂进行洗脱,最后对溶剂脱附液进行邻氨基苯酚的回收。该工艺主要是针对高盐废水处理,其技术方案存在的缺陷为①需要先用浓硫酸调ph到2左右即强酸条件下后再通过吸附柱,强酸条件不仅对设备要求高,且存在安全隐患;②吸附完成后采用了有机溶剂(具体实施例中指出是工业甲醇)脱附再生,后期则需要增加精馏系统进行有机溶剂的回收处理,从而增加了设备成本和回收工艺流程;③还需要对脱附液进行氨基苯酚成品的回收处理,也增加了回收运行成本。The publication number is CN108793493A [a method for recovering o-aminophenol in concentrated brine], which discloses a method for recycling a large amount of o-aminophenol contained in high-salt wastewater by using a physical adsorption method. After adjusting the pH value of the wastewater from aminophenol production, it is passed into the macroporous styrene-based adsorption resin, and the o-aminophenol is adsorbed on the macroporous styrene-based adsorption resin. Elution, and finally the recovery of o-aminophenol is carried out on the solvent desorbed liquid. This process is mainly aimed at the treatment of high-salt wastewater, and its technical solution has the following drawbacks: (1) It is necessary to adjust the pH to about 2 with concentrated sulfuric acid, that is, under strong acid conditions, and then pass through the adsorption column. The strong acid conditions not only require high equipment, but also have potential safety hazards. 2. adopted organic solvent (indicated to be industrial methanol in the specific embodiment) desorption regeneration after the adsorption is completed, and then needs to increase the rectification system to carry out the recovery process of organic solvent in the later stage, thereby increasing equipment cost and recovery process flow; 3. also need The recovery and treatment of the aminophenol product in the desorption liquid also increases the recovery operation cost.
因此,研究一种处理效果好、运行成本低、操作简单、邻氨基苯酚回收量大且适于工业规模化处理的邻氨基苯酚工艺废水处理及回收方法显得尤为重要。Therefore, it is particularly important to develop an o-aminophenol process wastewater treatment and recovery method with good treatment effect, low operating cost, simple operation, large amount of o-aminophenol recovery and suitable for industrial-scale treatment.
发明内容SUMMARY OF THE INVENTION
针对上述现有技术中的不足,本发明目的在于提供一种邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理系统,其利用现有的设备进行改装,可以实现废水的处理,且处理成本较低,处理效率提高。In view of the deficiencies in the above-mentioned prior art, the object of the present invention is to provide a recovery and treatment system for o-aminophenol in the o-aminophenol acidification wastewater, which utilizes existing equipment for refit, can realize the treatment of wastewater, and the treatment cost is relatively high. low, the processing efficiency is improved.
本发明还提供一种邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理方法,其目的在于不仅可以解决企业排放困扰又可节约大量水资源,并实现环境治理与资源化利用,大大提高了企业的经济效益。The invention also provides a method for recovering o-aminophenol in the o-aminophenol acidification wastewater, which aims to not only solve the problem of enterprise discharge but also save a large amount of water resources, realize environmental management and resource utilization, and greatly improve the efficiency of enterprises. economic benefits.
为实现上述目的,本发明采用如下技术方案,一种邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理系统,包括:To achieve the above object, the present invention adopts the following technical solutions, a recovery and treatment system for o-aminophenol in the acidification wastewater of o-aminophenol, comprising:
邻氨基苯酚酸化废水池,用于废水储存和沉降;o-Aminophenol acidified wastewater tank for wastewater storage and sedimentation;
废水过滤槽,用于将沉降后的废水过滤达到澄清透明无漂浮油类物质的滤液;The waste water filter tank is used to filter the settled waste water to a clear, transparent filtrate without floating oil;
大孔吸附树脂解析处理装置,用于吸附废水滤液中含有的邻氨基苯酚,吸附饱和后,通过热碱喷淋方式解析处理后获得解析液;The macroporous adsorption resin analysis and treatment device is used to absorb the o-aminophenol contained in the wastewater filtrate. After the adsorption is saturated, the analysis solution is obtained by the hot alkali spraying method;
解析液收集罐,用于收集大孔树脂吸附解析处理后的解析液;Analytical liquid collection tank, used to collect the analytical liquid after adsorption and analytical treatment of macroporous resin;
污水排放池,用于废水处理后达标排放或进行反复利用,节约水资源;Sewage discharge pool, which is used to discharge wastewater up to the standard or reuse it repeatedly to save water resources;
邻氨基苯酚酸化废水池中的废水经过沉降后进入废水过滤槽内过滤,经过调ph值后进入大孔吸附树脂解析处理装置,在大孔吸附树脂解析处理装置中完成吸附、失效、水反冲、水洗碱、酸循环处理后获得的解析液进入解析液收集罐中,达到合格排放标准的处理后废水进入污水排放池。The wastewater in the o-aminophenol acidification wastewater tank enters the wastewater filter tank after sedimentation, and then enters the macroporous adsorption resin analysis and treatment device after adjusting the pH value. , The analytic solution obtained after washing alkali and acid circulation treatment enters into the analytic solution collection tank, and the treated wastewater that meets the qualified discharge standard enters the sewage discharge tank.
进一步的,所述大孔吸附树脂解析处理装置由至少一组大孔树脂吸附组件构成,优选为两组大孔树脂吸附组件,每组大孔树脂吸附组件均包括三个大孔树脂吸附柱,三个大孔树脂吸附柱采用两个吸附柱串连进行吸附,而另一个吸附柱解析的处理工艺。Further, the macroporous adsorption resin analytical treatment device is composed of at least one group of macroporous resin adsorption components, preferably two groups of macroporous resin adsorption components, each group of macroporous resin adsorption components includes three macroporous resin adsorption columns, The three macroporous resin adsorption columns use two adsorption columns in series for adsorption, and another adsorption column for desorption.
优先地,所述大孔吸附树脂解析处理装置由6个大孔吸附树脂柱构成,分别为四个1200*3000mm尺寸的和两个1600*3000mm尺寸的,其中,三个1200*3000树脂柱为一组大孔树脂吸附组件,另一个1200*3000树脂柱和两个1600*3000树脂柱为另一组大孔树脂吸附组件。Preferably, the macroporous adsorption resin analytical treatment device is composed of 6 macroporous adsorption resin columns, four 1200*3000mm in size and two 1600*3000mm in size, wherein the three 1200*3000 resin columns are One set of macroporous resin adsorption components, another 1200*3000 resin column and two 1600*3000 resin columns are another set of macroporous resin adsorption components.
优先地,所述1200*3000尺寸的树脂柱计划装填3方树脂,1600*3000尺寸的树脂柱装填4方树脂。Preferably, the 1200*3000 size resin column is planned to be packed with 3 square resins, and the 1600*3000 size resin column is packed with 4 square resins.
优先地,所述大孔吸附树脂柱均为衬胶树脂柱。Preferably, the macroporous adsorption resin columns are all rubber-lined resin columns.
基于上述一种邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理系统而进行的邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理方法,具体包括如下步骤:The recovery and treatment method of o-aminophenol in the o-aminophenol acidification wastewater based on the recovery and treatment system of the o-aminophenol in the above-mentioned a kind of o-aminophenol acidification wastewater, specifically comprises the following steps:
S1前期处理:废水经沉降、过滤后(澄清透明无漂浮油类物质),调节PH值至5-6,调节为弱酸性,可去除废水中的碱性杂质,并且在酸性环境中利于大孔吸附树脂柱更好吸附废水滤液中的邻氨基苯酚;S1 Pre-treatment: After the wastewater is settled and filtered (clear and transparent without floating oil), the pH value is adjusted to 5-6, and adjusted to weak acidity, which can remove the alkaline impurities in the wastewater, and is conducive to large pores in an acidic environment The adsorption resin column can better adsorb the o-aminophenol in the wastewater filtrate;
S2吸附处理:调节废水滤液的进水温度≥30℃,防止邻氨基苯酚结晶析出堵塞管道,废水滤液通过废水泵和进料管道进入一组大孔吸附树脂吸附组件中,组件包括1#、2#、3#树脂柱,废水滤液先进入1#和2#串联的树脂柱中进行吸附,2#底部出水合格时吸附后的废水滤液直接排入污水排放池;S2 adsorption treatment: adjust the inlet water temperature of the wastewater filtrate to ≥30°C to prevent the crystallization of o-aminophenol from clogging the pipeline. The wastewater filtrate enters a set of macroporous adsorption resin adsorption components through the wastewater pump and the feed pipeline. The components include 1#, 2 #, 3# resin column, the wastewater filtrate first enters the resin column connected in series with 1# and 2# for adsorption, and the adsorbed wastewater filtrate is directly discharged into the sewage discharge tank when the effluent at the bottom of 2# is qualified;
S3失效处理:当2#树脂柱底部出水不合格时,与其串联的1#树脂柱已失效,此时停止废水滤液进入1#树脂柱内,并断开1#和2#的串联状态,而启动2#和3#的串联,即将废水滤液通过废水泵和进料管道进入2#和3#串联的树脂柱中进行吸附;S3 failure treatment: when the effluent at the bottom of the 2# resin column is unqualified, the 1# resin column connected in series with it has failed. At this time, the waste water filtrate is stopped from entering the 1# resin column, and the series connection of 1# and 2# is disconnected. Start the series connection of 2# and 3#, that is, the waste water filtrate enters the resin column of 2# and 3# through the waste water pump and the feed pipeline for adsorption;
S4反冲处理:对已经失效的1#树脂柱通过循环水泵和循环水管道进行正反水冲,以便去除1#树脂孔道中残留的废水滤液,出水通过正反洗管道排放到原水池中;S4 backflushing treatment: The 1# resin column that has failed is subjected to forward and reverse water flushing through the circulating water pump and the circulating water pipeline, so as to remove the residual waste water filtrate in the 1# resin channel, and the effluent is discharged into the original pool through the forward and reverse washing pipeline;
S5解析再生处理:通过进碱泵和进碱管道将升温到80℃的稀碱罐中的热碱液通入反冲处理后的1#树脂柱内,当1#树脂柱底部出水偏碱性时通过1#树脂柱底部的解析液管道将解析液送入解析液收集罐内;S5 Analytical regeneration treatment: Pass the hot alkali liquid in the dilute alkali tank heated to 80 °C into the 1# resin column after backflushing through the alkali feed pump and the alkali feed pipeline. When the water at the bottom of the 1# resin column is alkaline At the same time, the desorption liquid is sent to the desorption liquid collection tank through the desorption liquid pipeline at the bottom of the 1# resin column;
S6水洗碱处理:S5步骤中的热碱液进完后,停止热碱液进入1#树脂柱内,同时打开1#树脂柱的循环水管道进行水洗,一部分水洗碱液通过解析液管道进入解析液收集罐内,而另一部分水洗碱液通过解析液管道进入稀碱罐以循环使用;S6 water washing alkali treatment: after the hot lye in step S5 is finished, stop the hot lye from entering the 1# resin column, and open the circulating water pipeline of the 1# resin column for washing, and a part of the washing lye enters the analysis through the analysis solution pipeline. In the liquid collection tank, another part of the washing alkali liquid enters the dilute alkali tank through the analytical liquid pipeline for recycling;
S7酸循环处理:将一定量稀盐酸通过稀酸泵和稀酸管道打入S6处理后的1#树脂柱,循环一定时间,当树脂柱内PH在3左右时,循环结束。S7 acid circulation treatment: a certain amount of dilute hydrochloric acid is injected into the 1# resin column treated by S6 through the dilute acid pump and the dilute acid pipeline, and circulates for a certain period of time. When the pH in the resin column is about 3, the cycle ends.
优选地,S2中所述的调节废水滤液的进水温度为30℃-80℃,防止邻氨基苯酚结晶析出堵塞管道。Preferably, the inlet water temperature of the regulated wastewater filtrate described in S2 is 30°C-80°C to prevent the crystallization of o-aminophenol from clogging the pipeline.
进一步的,1#、2#、3#为分开独立树脂柱,每次使用均是两个串联使用,一旦发现串联后面的水质不合格,立即将前面的切换失效,同时将另外两个串联使用,而对失效的依次进行循环水反冲、热碱水解析、解析液收集、酸循环处理。Further, 1#, 2#, and 3# are separate and independent resin columns, and two are used in series each time. Once the water quality behind the series is found to be unqualified, the previous switch will be invalid immediately, and the other two will be used in series at the same time. , and for the failed ones, circulating water backflushing, hot alkali water analysis, analysis liquid collection, and acid circulation treatment are performed in sequence.
优选地,S5中所述的解析液收集罐内解析液可直接返回生产车间使用,不需要回收成品,即循环套用处理。Preferably, the desorption solution in the desorption solution collection tank described in S5 can be directly returned to the production workshop for use, without the need to recycle the finished product, that is, recycling treatment.
优选的,S5中所述的出水偏碱性是指PH值为10-12时,具体而言,其出水情况是通过1#树脂柱底部取样进行PH试纸测量而定。Preferably, the alkaline effluent described in S5 refers to when the pH value is 10-12. Specifically, the effluent condition is determined by taking samples from the bottom of the 1# resin column for pH test paper measurement.
与现有技术相比,本发明至少具有以下有益效果:Compared with the prior art, the present invention at least has the following beneficial effects:
(1)本发明将氨基苯酚酸化废水中的高浓邻氨基苯酚生产废水汇集起来通过装有大孔树脂的吸附柱,使废水中含有的邻氨基苯酚吸附在吸附树脂上,吸附饱和的树脂经热碱水洗脱,洗脱下来的含有邻氨基苯酚的碱水可直接返回生产车间循环套用;采用的物理吸附和升温解析方式,未采用有机溶剂脱附、也未采用强酸强碱等,故,大大降低了回收运行成本;(1) the present invention brings together the high-concentration o-aminophenol production waste water in the aminophenol acidification waste water and passes through the adsorption column equipped with macroporous resin, so that the o-aminophenol contained in the waste water is adsorbed on the adsorption resin, and the saturated resin is adsorbed through Hot alkaline water is eluted, and the eluted alkaline water containing o-aminophenol can be directly returned to the production workshop for recycling; the physical adsorption and temperature rise analysis methods adopted do not use organic solvent desorption, nor strong acid and alkali, etc., so , greatly reducing the cost of recycling operation;
(2)本发明采用两个吸附柱串连进行吸附,而另一个吸附柱解析的处理工艺,结构简单合理,不仅可高效回收废水中大量的邻氨基苯酚及色度,还提高了处理效率,同时串联吸附处理后的废水无色透亮,从而解决企业水处理不达标的问题并最大程度提高经济效益,实现了废水治理与资源回收利用;(2) the present invention adopts two adsorption columns to be connected in series to carry out adsorption, and the other adsorption column is decomposed in the treatment process, which has a simple and reasonable structure, and can not only efficiently recover a large amount of o-aminophenol and chromaticity in the waste water, but also improve the treatment efficiency, At the same time, the wastewater after series adsorption treatment is colorless and translucent, so as to solve the problem of substandard water treatment of enterprises, maximize economic benefits, and realize wastewater treatment and resource recycling;
(3)本发明经过解析再生处理而收集到的解析液即含有邻氨基苯酚的碱水洗脱液是直接返回生产车间循环套用,不用回收成品,节省了回收后处理设备和工艺,故,大大简化了回收工序,降低了回收运行成本,提高了企业的经济效益。(3) the analytical solution collected by the present invention through the analytical regeneration treatment, namely the alkaline water eluent containing o-aminophenol, is directly returned to the production workshop for recycling, and the finished product does not need to be recovered, which saves the recovery post-processing equipment and technology. Therefore, greatly The recycling process is simplified, the recycling operation cost is reduced, and the economic benefit of the enterprise is improved.
附图说明Description of drawings
图1是本发明的回收处理系统的结构示意图;Fig. 1 is the structural representation of the recycling processing system of the present invention;
图2是本发明回收处理方法中的一实施例的吸附过程流程图;Fig. 2 is the adsorption process flow chart of an embodiment in the recovery processing method of the present invention;
图3是本发明回收处理方法中的一实施例的失效处理流程图;Fig. 3 is the failure processing flow chart of an embodiment in the recycling processing method of the present invention;
图4是本发明回收处理方法中的一实施例的反冲处理流程图;Fig. 4 is the recoil processing flow chart of an embodiment in the recovery processing method of the present invention;
图5是本发明回收处理方法中的一实施例的解析处理流程图;Fig. 5 is the analysis processing flow chart of one embodiment in the recycling processing method of the present invention;
图6是本发明回收处理方法中的一实施例的再生处理流程图;Fig. 6 is the regeneration processing flow chart of an embodiment in the recycling processing method of the present invention;
图7是本发明回收处理方法中的一实施例的水洗碱处理流程图;Fig. 7 is the water-washing alkali treatment flow chart of an embodiment in the recovery treatment method of the present invention;
图8是本发明回收处理方法中的一实施例的酸循环流程图。Fig. 8 is an acid cycle flow chart of an embodiment of the recovery and treatment method of the present invention.
具体实施方式Detailed ways
下面将结合具体的实施方案对本发明进行进一步的解释,但并不局限本发明。The present invention will be further explained below with reference to specific embodiments, but the present invention is not limited.
下述实施例中,如无特殊说明,所用方法为常规方法,所用试剂都来源于市售商品。In the following examples, unless otherwise specified, the methods used are conventional methods, and the reagents used are all derived from commercial products.
为使本发明实施例的目的、技术方案和优点更加清楚,下面将结合本发明附图对实施例中的技术方案进行清楚、完整地描述,所描述的实施例仅是本发明的一部分实施例而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有作出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。In order to make the purposes, technical solutions and advantages of the embodiments of the present invention clearer, the technical solutions in the embodiments will be clearly and completely described below with reference to the accompanying drawings of the present invention, and the described embodiments are only a part of the embodiments of the present invention not all examples. Based on the embodiments of the present invention, all other embodiments obtained by those of ordinary skill in the art without creative efforts shall fall within the protection scope of the present invention.
实施例1Example 1
参阅图1,图中1、2、3为废水滤液进料阀,4、5、6为废水滤液出料阀,7、8、9为反洗阀,10、11、12为正洗阀,13、14、15为进碱阀门,16、17、18为解析液出料阀门,19、20、21为顶部循环水阀,22、23、24为底部循环水阀,25、26、27为底部酸阀门,28、29、30为顶部酸阀门,31、32、33为底部串料阀,34、35、36为顶部串料阀,37、38、39为串料切换阀门。Referring to Figure 1, in the figure 1, 2, 3 are waste water filtrate feed valves, 4, 5, 6 are waste water filtrate discharge valves, 7, 8, 9 are backwash valves, 10, 11, 12 are positive wash valves, 13, 14, and 15 are the alkali inlet valves, 16, 17, and 18 are the analytical liquid outlet valves, 19, 20, and 21 are the top circulating water valves, 22, 23, and 24 are the bottom circulating water valves, and 25, 26, and 27 are the bottom circulating water valves. Bottom acid valve, 28, 29, 30 are top acid valves, 31, 32, 33 are bottom string valves, 34, 35, 36 are top string valves, 37, 38, 39 are string switching valves.
本发明一种邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理系统,包括:邻氨基苯酚酸化废水池,用于废水储存和沉降;The invention relates to a recovery and treatment system for o-aminophenol in the o-aminophenol acidification wastewater, comprising: an o-aminophenol acidification wastewater pool, which is used for waste water storage and sedimentation;
废水过滤槽,用于将沉降后的废水过滤达到澄清透明无漂浮油类物质的滤液;The waste water filter tank is used to filter the settled waste water to a clear, transparent filtrate without floating oil;
大孔吸附树脂解析处理装置,用于吸附废水滤液中含有的邻氨基苯酚,吸附饱和后,通过热碱喷淋方式解析处理后获得解析液;所述大孔吸附树脂解析处理装置由一组大孔树脂吸附组件构成,所述大孔树脂吸附组件均包括1#、2#、3#分开独立的均为衬胶树脂柱,每次使用均是两个串联使用,一旦发现串联后面的水质不合格,立即将前面的切换失效,同时将另外两个串联使用,而对失效的依次进行循环水反冲、热碱水解析、解析液收集、酸循环处理;The macroporous adsorption resin analysis treatment device is used to adsorb the o-aminophenol contained in the waste water filtrate. After the adsorption is saturated, the analysis solution is obtained by the hot alkali spray method. The macroporous adsorption resin analysis treatment device consists of a group of large Porous resin adsorption components are composed of macroporous resin adsorption components. The macroporous resin adsorption components include 1#, 2#, and 3# which are separated and independent, all of which are rubber-lined resin columns. Each time they are used, two are used in series. If it is qualified, the previous switch will be invalid immediately, and the other two will be used in series at the same time, and the failed ones will be subjected to circulating water recoil, hot alkali water analysis, analysis liquid collection, and acid circulation treatment in sequence;
具体而言,1#、2#、3#的外部连接管道、控制阀类均是一样的,即1#、2#、3#的顶部均设有进料阀,底部设有出料阀,进料阀均与废水滤液进料管路可连通,出料阀均与出水管路可连通,出水管路与污水收集池连通;1#、2#、3#的顶部和底部均设有串联阀,三个柱体通过串联阀可构成一个串联管路,串联阀均与串联管路可连通;1#、2#、3#的顶部和底部均设有循环水阀,三个柱体通过循环水阀可构成一个循环水管路,循环水阀均与循环水管路可连通;1#、2#、3#的顶部均设有反洗阀,底部均设有正洗阀,三个柱体通过正、反洗阀可构成一个正反洗管路,正、反洗阀均与正反洗管路可连通,正反洗管路与北侧原水池连通;1#、2#、3#的底部均设有解析液出料阀,解析液出料阀与解析液管路连通,解析液管路与解析液收集罐连通;1#、2#、3#的顶部均设有进碱阀,进碱阀均与碱循环管道可连通,碱循环管道一边从稀碱罐出碱液,另一边通过解析液管路返回稀碱罐;1#、2#、3#的顶部均设有进酸阀,底部均设有酸循环阀,三个柱体通过进酸阀、酸循环阀可构成一个酸循环管路,进酸阀和酸循环阀均与酸循环管路可连通;Specifically, the external connection pipes and control valves of 1#, 2#, and 3# are the same, that is, the tops of 1#, 2#, and 3# are provided with feed valves, and the bottoms are provided with discharge valves. The feed valves are all connected to the waste water filtrate feed pipeline, the discharge valves are all connected to the water outlet pipeline, and the water outlet pipeline is connected to the sewage collection tank; the top and bottom of 1#, 2#, and 3# are connected in series The three cylinders can form a series pipeline through the series valve, and the series valves can be connected to the series pipeline; the top and bottom of 1#, 2#, 3# are equipped with circulating water valves, and the three cylinders pass through The circulating water valve can form a circulating water pipeline, and the circulating water valves can be connected with the circulating water pipeline; the tops of 1#, 2#, and 3# are equipped with backwash valves, and the bottoms are equipped with positive wash valves. A forward and backwash pipeline can be formed through the forward and backwash valves. Both the forward and backwash valves can be connected to the forward and backwash pipelines, and the forward and backwash pipelines are connected to the original pool on the north side; 1#, 2#, 3# The bottom of the analytic solution is equipped with an analytical solution discharge valve, the analytical solution discharge valve is connected with the analytical solution pipeline, and the analytical solution pipeline is connected with the analytical solution collection tank; the tops of 1#, 2#, and 3# are all provided with alkali inlet valves , the alkali inlet valve can be connected with the alkali circulation pipeline. The alkali circulation pipeline discharges the alkali liquid from the dilute alkali tank on one side, and returns to the dilute alkali tank through the analytical solution pipeline on the other side; the tops of 1#, 2#, and 3# are equipped with inlet Acid valve, with acid circulation valve at the bottom, three cylinders can form an acid circulation pipeline through the acid inlet valve and acid circulation valve, and the acid inlet valve and acid circulation valve can be connected with the acid circulation pipeline;
解析液收集罐,用于收集大孔树脂吸附解析处理后的解析液,解析液收集罐通过解析液管路、三个树脂柱底部的解析液出料阀分别与1#、2#、3#可连通;The analytical solution collection tank is used to collect the decomposed liquid after adsorption and desorption treatment of macroporous resin. connectable;
污水排放池,用于废水处理后达标排放或进行反复利用,节约水资源,污水排放池通过出水管路、三个树脂柱底部的出料阀分别与1#、2#、3#可连通;The sewage discharge tank is used to discharge the wastewater up to the standard or reuse it repeatedly to save water resources. The sewage discharge tank can be connected to 1#, 2#, and 3# respectively through the water outlet pipeline and the discharge valve at the bottom of the three resin columns;
邻氨基苯酚酸化废水池中的废水经过沉降后进入废水过滤槽内过滤,经过调ph值为5-6时后升温到≥30℃进入大孔吸附树脂解析处理装置,在大孔吸附树脂解析处理装置中完成吸附、失效、水反冲、水洗碱、酸循环处理后获得的解析液进入解析液收集罐中,达到合格排放标准的处理后废水进入污水排放池。The wastewater in the o-aminophenol acidification wastewater tank is settled and then filtered in the wastewater filter tank. After adjusting the pH value to 5-6, it is heated to ≥30 °C and enters the macroporous adsorption resin analysis and treatment device. After the macroporous adsorption resin analysis and treatment The desorption solution obtained after the adsorption, failure, water backflushing, water washing alkali, and acid cycle treatment in the device enters the desorption solution collection tank, and the treated wastewater that meets the qualified discharge standard enters the sewage discharge tank.
参阅图2-图8,基于上述一种邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理系统而进行的邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理方法,具体包括如下步骤:Referring to Fig. 2-Fig. 8, the recovery and treatment method of o-aminophenol in the o-aminophenol acidification waste water carried out based on the recovery and treatment system of the o-aminophenol in the above-mentioned a kind of o-aminophenol acidification waste water, specifically comprises the following steps:
S1前期处理:废水经沉降、过滤后(澄清透明无漂浮油类物质),调节PH值至5-6,调节为弱酸性,可去除废水中的碱性杂质,并且在酸性环境中利于大孔吸附树脂柱更好吸附废水滤液中的邻氨基苯酚;S1 Pre-treatment: After the wastewater is settled and filtered (clear and transparent without floating oil), the pH value is adjusted to 5-6, and adjusted to weak acidity, which can remove the alkaline impurities in the wastewater, and is conducive to large pores in an acidic environment The adsorption resin column can better adsorb the o-aminophenol in the wastewater filtrate;
S2吸附处理:打开1#柱上部进料阀,1#柱底部串连阀,打开2#树柱上部串连阀,2#柱底部出料阀,二柱处于串联状态,启动废水泵,调节废水滤液的PH值至5-6,调温≥30℃,弱酸性条件下可去除废水中的碱性杂质,并且在酸性环境中利于大孔吸附树脂柱更好吸附废水滤液中的邻氨基苯酚,流速6立方/h,串联吸附后的合格废水从2#树脂柱底部出料阀,经出水管路进入污水排放池;S2 adsorption treatment: Open the feed valve at the top of the 1# column, the series valve at the bottom of the 1# column, open the series valve at the top of the 2# column, and the discharge valve at the bottom of the 2# column, the second column is in series state, start the waste water pump, adjust The pH value of the wastewater filtrate is 5-6, and the temperature is adjusted to ≥30 °C. The alkaline impurities in the wastewater can be removed under weakly acidic conditions, and the macroporous adsorption resin column can better adsorb the o-aminophenol in the wastewater filtrate in an acidic environment. , the flow rate is 6 cubic meters/h, and the qualified wastewater after series adsorption will enter the sewage discharge tank from the discharge valve at the bottom of the 2# resin column through the water outlet pipeline;
S3失效处理:2#柱底部出水不合格后,关闭1#柱上部进料阀,底部串联料阀,同时关闭2#柱上部串联阀,同时打开2#柱上部进料阀,关闭2#柱底部出料阀,打开2#底部串联阀,串上3#上部串连阀,打开3#底部出料阀,2#3#处于串联状态;S3 failure treatment: After the effluent at the bottom of the 2# column is unqualified, close the upper feed valve of the 1# column, the bottom series feed valve, close the upper series valve of the 2# column, open the upper feed valve of the 2# column, and close the 2# column. Bottom discharge valve, open 2# bottom series valve, connect 3# upper series valve, open 3# bottom discharge valve, 2# and 3# are in series state;
S4反冲处理:失效后的1#柱,打开1#柱上部正反洗阀,同时开启1#柱底部循环水阀,对树脂进行反冲,总用水量5-6立方,水温50-80℃,流速12立方/h,约10-30分钟,出水通过上部正反洗管道进入北侧原水池;S4 backflushing treatment: After the failure of the 1# column, open the positive and backwash valve at the top of the 1# column, and at the same time open the circulating water valve at the bottom of the 1# column to backflush the resin, the total water consumption is 5-6 cubic meters, and the water temperature is 50-80 ℃, the flow rate is 12 cubic meters/h, about 10-30 minutes, the effluent enters the northern raw water tank through the upper forward and reverse washing pipeline;
S5解析再生处理:打开1#树脂柱顶部进碱阀,同时打开1#树脂柱底部正反洗阀,启动进碱泵,加热至80度的4%总用碱量6立方(2BV),流速3-4.5立方/H(1-1.5BV),总共时间大于2小时,出水通过正反洗管道进入北侧原水池,出水偏碱后即PH为10-12时通过1#树脂柱底部解析液出料阀进入解析液收集罐;(出水情况通过1#树脂柱放料阀放料后通过PH试纸测量而定,所述放料阀为采样或者检修放净物料使用);S5 Analytical regeneration treatment: Open the alkali inlet valve at the top of the 1# resin column, and at the same time open the forward and backwash valve at the bottom of the 1# resin column, start the alkali inlet pump, heat to 80
S6水洗碱处理:热碱进完后,关闭1#柱顶部进碱阀,关闭1#树脂柱底部正反洗阀,打开1#树脂柱顶部循环水阀,打开1#树脂柱底部解析液出料阀,水洗总用水量约6立方,流速3立方/H,前1小时3立方通过解析液管道进入1#解析液收集罐,打开稀碱罐顶部进料阀,关闭1#解析液收集罐进料阀,后1小时3立方通过解析液管道进入稀碱罐;S6 water washing alkali treatment: After the hot alkali is finished, close the alkali inlet valve at the top of the 1# column, close the forward and reverse washing valve at the bottom of the 1# resin column, open the circulating water valve at the top of the 1# resin column, and open the bottom of the 1# resin column. Feed valve, the total water consumption for washing is about 6 cubic meters, and the flow rate is 3 cubic meters per H. In the first 1 hour, 3 cubic meters enters the 1# analytical solution collection tank through the analytical solution pipeline, open the feed valve at the top of the dilute alkali tank, and close the 1# analytical solution collection tank. Feed valve, after 1
S7酸循环处理:打开1#树脂柱底部酸循环阀,打开1#树脂柱顶部进酸阀,将一定量稀盐酸打入稀酸罐,开启稀酸泵,通过稀酸管道打入树脂柱,循环一定时间,保证树脂柱内PH在3左右,循环结束。S7 acid circulation treatment: open the acid circulation valve at the bottom of the 1# resin column, open the acid inlet valve at the top of the 1# resin column, pump a certain amount of dilute hydrochloric acid into the dilute acid tank, open the dilute acid pump, and drive it into the resin column through the dilute acid pipeline, Cycle for a certain period of time to ensure that the pH in the resin column is about 3, and the cycle ends.
进一步的,1#、2#、3#为分开独立树脂柱,每次使用均是两个串联使用,一旦发现串联后面的水质不合格,立即将前面的切换失效,同时将另外两个串联使用,而对失效的依次进行循环水反冲、热碱水解析、解析液收集、酸循环处理。Further, 1#, 2#, and 3# are separate and independent resin columns, and two are used in series each time. Once the water quality behind the series is found to be unqualified, the previous switch will be invalid immediately, and the other two will be used in series at the same time. , and for the failed ones, circulating water backflushing, hot alkali water analysis, analysis liquid collection, and acid circulation treatment are performed in sequence.
具体的,调节废水滤液的进水温度可为30℃-80℃,温度≥30℃可以防止邻氨基苯酚结晶析出堵塞管道。Specifically, adjusting the inlet water temperature of the waste water filtrate can be 30°C-80°C, and the temperature ≥ 30°C can prevent o-aminophenol from crystallizing out and blocking the pipeline.
具体的,解析液收集罐内解析液可直接返回生产车间使用,不需要回收成品,即循环套用处理,大大降低了运营成本,也简化了回收处理设备,提高了企业经济效益。Specifically, the analytical liquid in the analytical liquid collection tank can be directly returned to the production workshop for use, without the need to recycle the finished product, that is, the recycling treatment, which greatly reduces the operating cost, simplifies the recycling and processing equipment, and improves the economic benefits of the enterprise.
实施例2:Example 2:
所述大孔吸附树脂解析处理装置由两组大孔树脂吸附组件构成,每组大孔树脂吸附组件均包括三个大孔树脂吸附柱,三个大孔树脂吸附柱采用两个吸附柱串连进行吸附,而另一个吸附柱解析的处理工艺;具体而言,所述大孔吸附树脂解析处理装置由6个大孔吸附树脂柱构成,分别为四个1200*3000mm尺寸的和两个1600*3000mm尺寸的,其中,三个1200*3000树脂柱为一组大孔树脂吸附组件,另一个1200*3000树脂柱和两个1600*3000树脂柱为另一组大孔树脂吸附组件,所述1200*3000尺寸的树脂柱计划装填3方树脂,1600*3000尺寸的树脂柱装填4方树脂,所述大孔吸附树脂柱均为衬胶树脂柱。The macroporous adsorption resin analysis treatment device is composed of two groups of macroporous resin adsorption components, each group of macroporous resin adsorption components includes three macroporous resin adsorption columns, and the three macroporous resin adsorption columns are connected in series by two adsorption columns The treatment process of adsorption and desorption of another adsorption column; specifically, the macroporous adsorption resin desorption treatment device is composed of 6 macroporous adsorption resin columns, four 1200*3000mm in size and two 1600* 3000mm size, among which, three 1200*3000 resin columns are a set of macroporous resin adsorption components, another 1200*3000 resin column and two 1600*3000 resin columns are another set of macroporous resin adsorption components, the 1200 *The 3000 size resin column is planned to be filled with 3 squares of resin, and the 1600*3000 size resin column is planned to be filled with 4 squares of resin. The macroporous adsorption resin columns are all rubber-lined resin columns.
实施例3Example 3
邻氨基苯酚酸化废水中的邻氨基苯酚的回收处理方法,具体包括如下步骤:首先将车间邻氨基苯酚污水15立方邻氨基苯酚含量经过沉降槽沉降以及过滤槽过滤后,去除底部污泥以及漂浮的油污等杂质;其次,经过滤槽过滤的废水滤液调ph值5-6后经过废水泵由进料阀进入1#树脂柱,同时串联通过2#树脂柱,1#,2#树脂柱均为1200*3000衬胶树脂柱,每个树脂柱内装填ADS600聚苯乙烯树脂3立,吸附效率约为6立/小时;再其次,循环水返洗步骤2中已经失效的1#树脂柱,大约30分钟后可以去除残留在孔道内的废水滤液,水洗液通过顶部的正反洗管路通入北侧原水池;再其次,使用4%的氢氧化钠溶液6立方在80℃的条件下对S3处理后的树脂柱进行解析获得解析液,将解析液收集入解析液收集罐,再通过泵打回车间循环套用,所述解析液收集罐液体中的邻氨基苯酚含量为0.75%,约含有纯邻氨基苯酚45kg。The recovery and treatment method of o-aminophenol in the o-aminophenol acidification wastewater specifically includes the following steps: first, after the content of 15 cubic meters of o-aminophenol in the o-aminophenol sewage of the workshop is settled in a sedimentation tank and filtered in a filter tank, the bottom sludge and floating sludge are removed. Oil stains and other impurities; secondly, the waste water filtrate filtered by the filter tank is adjusted to pH 5-6 and then enters the 1# resin column through the waste water pump through the feed valve, and passes through the 2# resin column in series at the same time, the 1# and 2# resin columns are both 1200*3000 rubber-lined resin columns, each resin column is filled with ADS600 polystyrene resin for 3 liters, and the adsorption efficiency is about 6 liters/hour; secondly, the 1# resin column that has failed in the circulating water backwash step 2, about After 30 minutes, the waste water filtrate remaining in the pores can be removed, and the washing liquid is passed to the north side raw water tank through the front and back washing pipelines at the top; secondly, use 6 cubic meters of 4% sodium hydroxide solution at 80 ℃. The resin column treated in S3 is decomposed to obtain desorption liquid, which is collected into a desorption liquid collection tank, and then pumped back to the workshop for recycling by a pump. The o-aminophenol content in the desorption liquid collection tank liquid is 0.75%, about Pure o-aminophenol 45kg.
取三份样品采用本发明的回收处理方法后,分别检测COD指标和色度指标,具体数据如下:After taking three samples and adopting the recovery treatment method of the present invention, COD index and chromaticity index are detected respectively, and the specific data are as follows:
(表1)(Table 1)
由(表1)可知废水中COD的平均去除率达到99.20%,色度的去除率为99.17%;It can be seen from (Table 1) that the average removal rate of COD in wastewater reaches 99.20%, and the removal rate of chroma is 99.17%;
由(表1)可知废水中每升产品的平均回收率高达8.19g。It can be known from (Table 1) that the average recovery rate per liter of product in the wastewater is as high as 8.19g.
尽管已经示出和描述了本发明的实施例,对于本领域的普通技术人员而言,可以理解在不脱离本发明的原理和精神的情况下可以对这些实施例进行多种变化、修改、替换和变型,本发明的范围由所附权利要求及其等同物限定。Although embodiments of the present invention have been shown and described, it will be understood by those skilled in the art that various changes, modifications, and substitutions can be made in these embodiments without departing from the principle and spirit of the invention and modifications, the scope of the present invention is defined by the appended claims and their equivalents.
Claims (10)
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Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB1331948A (en) * | 1969-10-11 | 1973-09-26 | Inst De Proiectari Pentru Ind | Regeneration of ion exchange resins |
CN1265376A (en) * | 2000-03-13 | 2000-09-06 | 南京大学 | Treatment of 2,3-acid producing waste water and resource recovering and utilizing method |
CN101066824A (en) * | 2007-06-14 | 2007-11-07 | 南开大学 | Treatment and recycling method of 1-amino-8-naphthol-3,6-disulfonic acid production wastewater |
CN102910757A (en) * | 2012-09-27 | 2013-02-06 | 新泰昊原化工有限责任公司 | Treatment technique of waste water generated in production of o-nitrophenol |
CN103319019A (en) * | 2013-06-14 | 2013-09-25 | 陕西蓝深特种树脂有限公司 | Aspartame production mother solution recycling and treating method and system |
CN104355455A (en) * | 2014-11-20 | 2015-02-18 | 郑州航空工业管理学院 | Ortho-aminophenol wastewater treatment method |
CN105417774A (en) * | 2015-11-24 | 2016-03-23 | 湖北鸿鑫化工有限公司 | Recycling method of 2-(4-methyl phenyl)-benzoxazole synthetic process wastewater |
CN107117749A (en) * | 2017-05-17 | 2017-09-01 | 浙江奇彩环境科技股份有限公司 | A kind of para-aminophenol produces the recycling processing method of waste water |
CN108793493A (en) * | 2018-06-22 | 2018-11-13 | 西安蓝深环保科技有限公司 | O-aminophenol recovery and treatment method in a kind of strong brine |
-
2021
- 2021-12-31 CN CN202111669522.7A patent/CN114291916A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB1331948A (en) * | 1969-10-11 | 1973-09-26 | Inst De Proiectari Pentru Ind | Regeneration of ion exchange resins |
CN1265376A (en) * | 2000-03-13 | 2000-09-06 | 南京大学 | Treatment of 2,3-acid producing waste water and resource recovering and utilizing method |
CN101066824A (en) * | 2007-06-14 | 2007-11-07 | 南开大学 | Treatment and recycling method of 1-amino-8-naphthol-3,6-disulfonic acid production wastewater |
CN102910757A (en) * | 2012-09-27 | 2013-02-06 | 新泰昊原化工有限责任公司 | Treatment technique of waste water generated in production of o-nitrophenol |
CN103319019A (en) * | 2013-06-14 | 2013-09-25 | 陕西蓝深特种树脂有限公司 | Aspartame production mother solution recycling and treating method and system |
CN104355455A (en) * | 2014-11-20 | 2015-02-18 | 郑州航空工业管理学院 | Ortho-aminophenol wastewater treatment method |
CN105417774A (en) * | 2015-11-24 | 2016-03-23 | 湖北鸿鑫化工有限公司 | Recycling method of 2-(4-methyl phenyl)-benzoxazole synthetic process wastewater |
CN107117749A (en) * | 2017-05-17 | 2017-09-01 | 浙江奇彩环境科技股份有限公司 | A kind of para-aminophenol produces the recycling processing method of waste water |
CN108793493A (en) * | 2018-06-22 | 2018-11-13 | 西安蓝深环保科技有限公司 | O-aminophenol recovery and treatment method in a kind of strong brine |
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