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CN105174552A - Oil removal treatment method for high-concentration sewage in coal chemical industry - Google Patents

Oil removal treatment method for high-concentration sewage in coal chemical industry Download PDF

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CN105174552A
CN105174552A CN201510654489.9A CN201510654489A CN105174552A CN 105174552 A CN105174552 A CN 105174552A CN 201510654489 A CN201510654489 A CN 201510654489A CN 105174552 A CN105174552 A CN 105174552A
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sewage
treatment method
oil removal
removal treatment
emulsion
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洪磊
徐炎华
陆曦
刘志英
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Nanjing Tech University
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Abstract

本发明涉及一种煤化工高浓度污水的除油处理方法;其具体步骤如下:先将煤化工高浓污水进入除油破乳单元投加破乳剂和助凝剂,使废水中的油类物质破乳达到去除效果;然后将除油破乳后的废水进入吸附单元,通过吸附剂进一步去除废水中的固体悬浮颗粒和油类物质。废水经本项发明水中的油类物质和固体悬浮颗粒的去除率分别高达97%、95%以上,COD去除率高达到40%以上。本发明处理工艺简单、效果好、处理费用低等特点,具有广阔的应用前景。The invention relates to a method for degreasing treatment of high-concentration sewage in the coal chemical industry; the specific steps are as follows: firstly, the high-concentration sewage in the coal chemical industry enters the deoiling and demulsification unit and adds a demulsifier and a coagulant aid to make the oily substances in the waste water Demulsification achieves the removal effect; then the wastewater after oil removal and demulsification enters the adsorption unit, and the solid suspended particles and oily substances in the wastewater are further removed by the adsorbent. The removal rates of oily substances and solid suspended particles in waste water through the invention are as high as 97% and 95% respectively, and the COD removal rate is as high as 40%. The invention has the characteristics of simple treatment process, good effect, low treatment cost and the like, and has broad application prospects.

Description

一种煤化工高浓污水的除油处理方法A method for degreasing treatment of high-concentration sewage in coal chemical industry

技术领域technical field

本发明涉及一种水处理方法;尤其涉及一种适用于煤化工高浓污水的除油处理方法。The invention relates to a water treatment method, in particular to an oil removal treatment method suitable for high-concentration sewage in coal chemical industry.

背景技术Background technique

发展煤化工是我国的能源需求,但是随着现代煤化工的发展,其“水污染”和“缺水”日趋严重,以严重威胁企业的可持续发展,迫切需要实现“近零排放”。然而,煤化工高浓污水由于水中含有大量的油类物质和固体悬浮颗粒,导致在酚氨回收过程中导致热交换器堵塞、降低酚氨回收系统稳定性,在后续生化过程中抑制微生物代谢、降低生化效率。所以,要想提高中水回用率,关键要除油除浊。目前,处理含油废水方法较多,如化学法(盐析法,凝聚法)、电化学法;、膜分离法、气浮法;生物法等。这些方法都有各自缺点:设备占地面积大、投资高、药剂投加量大、预处理复杂。国内外对煤化工污水的处理技术工程上应用较多的有重力法、气浮法、膜技术等,没有针对煤化工高浓污水水量大、水中油、悬浮物含量的特点,导致整体除油、除尘成本高、效率低。目前应用比较多的投加破乳剂来除油,但是现有的常规破乳剂由于没有针对煤化工高浓污水水中油、固体悬浮颗粒的特性,导致其适用性差、效率低下,并且存在二次污染、投加量大等问题。The development of coal chemical industry is my country's energy demand, but with the development of modern coal chemical industry, its "water pollution" and "water shortage" are becoming more and more serious, which seriously threatens the sustainable development of enterprises, and it is urgent to realize "near-zero emissions". However, the high-concentration sewage of coal chemical industry contains a large amount of oily substances and solid suspended particles in the water, which leads to blockage of heat exchangers during the recovery process of phenolic ammonia, reduces the stability of the phenolic ammonia recovery system, and inhibits microbial metabolism in the subsequent biochemical process. Reduce biochemical efficiency. Therefore, in order to improve the reuse rate of reclaimed water, the key is to remove oil and turbidity. At present, there are many methods for treating oily wastewater, such as chemical method (salting out method, coagulation method), electrochemical method; membrane separation method, air flotation method; biological method, etc. These methods have their own disadvantages: the equipment occupies a large area, high investment, large dosage of chemicals, and complicated pretreatment. Gravity method, air flotation method, membrane technology, etc. are widely used in domestic and foreign coal chemical wastewater treatment technology projects, which do not address the characteristics of large water volume, oil and suspended solids content in high-concentration coal chemical wastewater, resulting in overall degreasing , Dust removal cost is high and efficiency is low. At present, more demulsifiers are used to remove oil, but the existing conventional demulsifiers have poor applicability, low efficiency, and secondary pollution because they do not have the characteristics of oil and solid suspended particles in high-concentration coal chemical sewage water. , Dosing large amount and other issues.

中国专利申请CN104826578A披露了一种粉煤灰改性吸附剂及其制备与处理含油污水的方法,所述方法通过特定组分改性、特定工艺参数和操作步骤,从而使得最终得到的吸附剂来处理含油污水,用在低浓度油含量废水有一定的效果,但如果在应对处理成分复杂、稳定的煤化工高浓污水上表现出加药量大、处理效果不达标等不足之处。专利CN103435132B披露了一种活性炭纤维处理含油废水及其再生方法和装置,活性炭纤维电化学处理含油废水及其原位再生技术进行除油,装置繁琐,不易于实现工业化应用。Chinese patent application CN104826578A discloses a fly ash modified adsorbent and a method for preparing and treating oily sewage. The method uses specific component modification, specific process parameters and operating steps to make the final adsorbent The treatment of oily sewage has a certain effect when used in low-concentration oil-content wastewater, but if it is used to deal with complex and stable coal chemical high-concentration sewage, it shows shortcomings such as large dosage and substandard treatment effect. Patent CN103435132B discloses a method and device for treating oily wastewater with activated carbon fiber and its regeneration method and device. The electrochemical treatment of oily wastewater with activated carbon fiber and its in-situ regeneration technology for oil removal are cumbersome and difficult to realize industrial application.

发明内容Contents of the invention

本发明的目的是为了改进现有技术的不足而提供一种煤化工高浓污水的除油处理方法。The object of the present invention is to provide an oil removal treatment method for high-concentration sewage in coal chemical industry in order to improve the deficiencies of the prior art.

本发明的技术方案为:一种煤化工高浓污水的除油处理方法,其特征在于工艺流程如下:高浓污水进水→除油破乳单元→吸附单元→过滤池→出水;其具体步骤如下:The technical solution of the present invention is: a method for degreasing treatment of high-concentration sewage in coal chemical industry, which is characterized in that the process flow is as follows: high-concentration sewage inflow→oil removal and demulsification unit→adsorption unit→filter tank→water outlet; its specific steps as follows:

①除油破乳单元:污水进入除油破乳处理单元,向除油池中投加破乳剂和助剂,控制温度反应,从而去除水中的油类物质。其中所述的破乳剂为聚醚破乳剂或者是硫酸和聚醚破乳剂的混合破乳剂;① Oil removal and demulsification unit: Sewage enters the oil removal and demulsification treatment unit, and demulsifiers and additives are added to the degreasing tank to control the temperature reaction, thereby removing oily substances in the water. Wherein said demulsifier is a polyether demulsifier or a mixed demulsifier of sulfuric acid and polyether demulsifier;

②吸附单元:除油破乳单元出水进入到吸附单元,加入吸附剂进行处理;去除水中的固体悬浮颗粒和进一步除油。②Adsorption unit: The effluent from the oil removal and demulsification unit enters the adsorption unit, and is treated by adding an adsorbent; the solid suspended particles in the water are removed and the oil is further removed.

③过滤池:对吸附单元出水进行过滤,截留吸附剂。③Filter pool: filter the effluent from the adsorption unit to retain the adsorbent.

优选上述步骤①中所述的聚醚破乳剂为丙二醇嵌段醚、异构十醇聚醚或十二十四醇聚醚等。Preferably, the polyether demulsifier described in the above step ① is propylene glycol block ether, isomeric decanth or lauryl polyethers, etc.

当上述的破乳剂为聚醚破乳剂时,破乳剂的投加质量与污水的体积比为200~500mg/L。When the above-mentioned demulsifier is a polyether demulsifier, the volume ratio of the added mass of the demulsifier to the sewage is 200-500 mg/L.

当上述的破乳剂为混合破乳剂时,破乳剂中硫酸的投加质量与污水的体积比为8~12g/L。其中所述的混合破乳剂中硫酸和聚醚破乳剂的质量比为2~5:1。When the above-mentioned demulsifier is a mixed demulsifier, the volume ratio of the added mass of sulfuric acid in the demulsifier to the sewage is 8-12g/L. The mass ratio of sulfuric acid and polyether demulsifier in the mixed demulsifier is 2-5:1.

优选除油破乳单元中控制温度为25~40℃;反应时间为0.5~5h。Preferably, the controlled temperature in the oil removal and demulsification unit is 25-40° C.; the reaction time is 0.5-5 hours.

优选步骤①中所述的助剂为阴离子聚丙烯胺、阳离子聚丙烯胺或硅藻土的一种或两种;助剂的投加质量与污水的体积比为5~10mg/L。Preferably, the auxiliary agent described in step ① is one or both of anionic polyacrylamine, cationic polyacrylamine or diatomite; the volume ratio of the additive mass to sewage is 5-10 mg/L.

优选步骤②中所述的吸附剂为活性炭与粉煤灰的混合物;活性炭与粉煤灰的质量比为1:(1~4);活性炭投加质量与污水的体积比为2.5~7.5g/L。加入吸附剂后处理时间一般为3~5h。The adsorbent described in the preferred step ② is a mixture of activated carbon and fly ash; the mass ratio of activated carbon to fly ash is 1: (1~4); the volume ratio of activated carbon dosing quality to sewage is 2.5~7.5g/ L. The treatment time after adding the adsorbent is generally 3 to 5 hours.

有益效果:Beneficial effect:

(1)本发明所述的煤化工高浓污水的除油处理方法,整体工艺破乳剂用量少、效果好、处理速度快等优点。(1) The method for degreasing treatment of high-concentration coal chemical sewage according to the present invention has the advantages of less demulsifier consumption, good effect and fast treatment speed in the overall process.

(2)经本发明工艺处理,可使水中的油类物质和固体悬浮颗粒聚集,其去除率可以分别达到97%、95%以上,COD的去除率可达到40%以上。(2) After the process of the present invention, the oily substances and solid suspended particles in the water can be aggregated, and the removal rate can reach more than 97% and 95% respectively, and the removal rate of COD can reach more than 40%.

(3)本发明中所投加的破乳剂为硫酸和聚醚类破乳剂的有机复配,有效降低了除油过程中破乳剂的投加量,显著提高了除油效率,无二次污染等问题。(3) The demulsifier added in the present invention is an organic compound of sulfuric acid and polyether demulsifier, which effectively reduces the dosage of demulsifier in the degreasing process, significantly improves the degreasing efficiency, and has no secondary pollution And other issues.

具体实施方式Detailed ways

下面通过具体实施案例对本发明的技术方案再作进一步的说明。以下例子中破乳剂、助剂和吸附剂的投加质量均以步骤①中所要处理的煤化工高浓污水的体积为基准。The technical solutions of the present invention will be further described below through specific implementation examples. In the following examples, the dosing quality of demulsifiers, additives and adsorbents is based on the volume of high-concentration coal chemical sewage to be treated in step ①.

实施例1Example 1

一种煤化工高浓污水的除油处理方法,包括如下步骤:A method for degreasing treatment of high-concentration coal chemical sewage, comprising the following steps:

①污水进入除油破乳处理单元,向除油池中投加破乳剂丙二醇段嵌醚,投加量为200mg/L,温度为25℃,反应时间为1h。所投加的助剂为阴离子聚丙烯胺,投加量为5mg/L。① Sewage enters the degreasing and demulsifying treatment unit, and the demulsifying agent propylene glycol segmented ether is added to the degreasing pool. The dosage is 200mg/L, the temperature is 25°C, and the reaction time is 1h. The additive added is anionic polyacrylamine, and the dosage is 5mg/L.

②除油破乳单元出水进入到吸附单元通过吸附剂去除水中的固体悬浮颗粒和进一步除油,吸附剂为活性炭与粉煤灰的混合物,活性炭与粉煤灰的混合比为1:1,活性炭与粉煤灰的投加量分别为2.5g/L、2.5g/L;吸附时间3小时。②The effluent from the oil removal and demulsification unit enters the adsorption unit to remove solid suspended particles in the water and further remove oil through the adsorbent. The adsorbent is a mixture of activated carbon and fly ash. The mixing ratio of activated carbon and fly ash is 1:1. The dosage of fly ash is 2.5g/L and 2.5g/L respectively; the adsorption time is 3 hours.

③对吸附单元出水进行过滤,截留吸附剂。③Filter the effluent from the adsorption unit to retain the adsorbent.

表1除油效果Table 1 degreasing effect

实施例2Example 2

一种煤化工高浓污水的除油处理方法,包括如下步骤:A method for degreasing treatment of high-concentration coal chemical sewage, comprising the following steps:

①污水进入除油破乳处理单元,向除油池中投加破乳剂异构十醇聚醚,投加量为400mg/L,温度为35℃,反应时间为2.5h。所投加的助剂为阳离子聚丙烯胺,投加量为7.5mg/L。① The sewage enters the oil removal and demulsification treatment unit, and the demulsifier isomeric decanol polyether is added to the oil removal tank, the dosage is 400mg/L, the temperature is 35°C, and the reaction time is 2.5h. The additive added is cationic polyacrylamine, and the dosage is 7.5mg/L.

②除油破乳单元出水进入到吸附单元通过吸附剂去除水中的固体悬浮颗粒和进一步除油,吸附剂为为活性炭与粉煤灰的混合物,活性炭与粉煤灰的混合比为1:2.5,活性炭与粉煤灰的投加量分别为3g/L、7.5g/L;吸附时间4小时。②The effluent from the oil removal and demulsification unit enters the adsorption unit to remove solid suspended particles in the water and further remove oil. The adsorbent is a mixture of activated carbon and fly ash, and the mixing ratio of activated carbon and fly ash is 1:2.5. The dosages of activated carbon and fly ash are 3g/L and 7.5g/L respectively; the adsorption time is 4 hours.

③对吸附单元出水进行过滤,截留吸附剂。③Filter the effluent from the adsorption unit to retain the adsorbent.

表2除油效果Table 2 degreasing effect

实施例3Example 3

一种煤化工高浓污水的除油处理方法,包括如下步骤:A method for degreasing treatment of high-concentration coal chemical sewage, comprising the following steps:

①污水经均质调节后进入除油破乳处理单元,向除油池中投加破乳剂硫酸与十二十四醇聚醚的混合物,混合比为3:1,其硫酸投加量为9g/L,温度为40℃,反应时间为5h。所投加的助剂为硅藻土,投加量为10mg/L。① After homogeneous adjustment, the sewage enters the degreasing and demulsifying treatment unit, and the mixture of demulsifying agent sulfuric acid and lauryl polyether is added to the degreasing tank, the mixing ratio is 3:1, and the dosage of sulfuric acid is 9g /L, the temperature is 40°C, and the reaction time is 5h. The additive added is diatomaceous earth, and the dosage is 10mg/L.

②除油破乳单元出水进入到吸附单元通过吸附剂去除水中的固体悬浮颗粒和进一步除油,吸附剂为为活性炭与粉煤灰的混合物,活性炭与粉煤灰的混合比为1:4,活性炭与粉煤灰的投加量分别为5g/L、20g/L;吸附时间3小时。②The effluent from the oil removal and demulsification unit enters the adsorption unit to remove solid suspended particles in the water and further remove oil. The adsorbent is a mixture of activated carbon and fly ash, and the mixing ratio of activated carbon and fly ash is 1:4. The dosages of activated carbon and fly ash are 5g/L and 20g/L respectively; the adsorption time is 3 hours.

③对吸附单元出水进行过滤,截留吸附剂。③Filter the effluent from the adsorption unit to retain the adsorbent.

表3除油效果Table 3 degreasing effect

实施例4Example 4

一种煤化工高浓污水的除油处理方法,包括如下步骤:A method for degreasing treatment of high-concentration coal chemical sewage, comprising the following steps:

①污水进入除油破乳处理单元,向除油池中投加破乳剂硫酸与十二十四醇聚醚的混合物,混合比为4.5:1,其硫酸投加量为11g/L,温度为40℃,反应时间为3h。所投加的助剂为阳离子聚丙烯酰胺,投加量为10mg/L。① Sewage enters the degreasing and demulsifying treatment unit, and a mixture of demulsifying agent sulfuric acid and tetradecyl polyether is added to the degreasing tank, the mixing ratio is 4.5:1, the dosage of sulfuric acid is 11g/L, and the temperature is 40°C, the reaction time is 3h. The additive added is cationic polyacrylamide, and the dosage is 10mg/L.

②除油破乳单元出水进入到吸附单元通过吸附剂去除水中的固体悬浮颗粒和进一步除油,吸附剂为为活性炭与粉煤灰的混合物,活性炭与粉煤灰的混合比为1:3,活性炭与粉煤灰的投加量分别为7.5g/L、22.5g/L;吸附时间4.5小时。②The effluent from the oil removal and demulsification unit enters the adsorption unit to remove solid suspended particles in the water and further remove oil. The adsorbent is a mixture of activated carbon and fly ash, and the mixing ratio of activated carbon and fly ash is 1:3. The dosages of activated carbon and fly ash are 7.5g/L and 22.5g/L respectively; the adsorption time is 4.5 hours.

③对吸附单元出水进行过滤,截留吸附剂。③Filter the effluent from the adsorption unit to retain the adsorbent.

表3除油效果Table 3 degreasing effect

Claims (8)

1. an oil removal treatment method for Coal Chemical Industry height strong sewage, is characterized in that technical process is as follows: high strong sewage water inlet → oil removing breakdown of emulsion unit → absorbing unit → filtering basin → water outlet; Its concrete steps are as follows:
1. oil removing breakdown of emulsion unit: sewage enters oil removing breakdown of emulsion processing unit, adds emulsion splitter and auxiliary agent in grease removal tank, control temperature reacts; Wherein said emulsion splitter is the mixing emulsion splitter of polyether demulsification agent or sulfuric acid and polyether demulsification agent;
2. absorbing unit: the water outlet of oil removing breakdown of emulsion unit enters into absorbing unit, adds sorbent material and processes;
3. filtering basin: absorbing unit water outlet is filtered, retains sorbent material.
2. oil removal treatment method according to claim 1, is characterized in that the polyether demulsification agent described in step is 1. propylene glycol block ether, isomery ten alcohol polyethers or ten tetracosanol polyethers.
3. oil removal treatment method according to claim 1, when it is characterized in that the emulsion splitter described in step is 1. polyether demulsification agent, the volume ratio adding quality and sewage of emulsion splitter is 200 ~ 500mg/L.
4. oil removal treatment method according to claim 1, is characterized in that the mass ratio of sulfuric acid and polyether demulsification agent in the mixing emulsion splitter described in step is 1. 2 ~ 5:1.
5. oil removal treatment method according to claim 1, it is characterized in that step 1. in emulsion splitter for mixing emulsion splitter time, in emulsion splitter, the volume ratio adding quality and sewage of sulfuric acid is 8 ~ 12g/L.
6. oil removal treatment method according to claim 1, is characterized in that the temperature described in step is 1. 25 ~ 40 DEG C; Reaction times is 0.5 ~ 5h.
7. oil removal treatment method according to claim 1, it is characterized in that the auxiliary agent described in step be 1. anion pp amine, cation polypropylene amine or diatomaceous one or both; The volume ratio adding quality and sewage of auxiliary agent is 5 ~ 10mg/L.
8. oil removal treatment method according to claim 1, is characterized in that the sorbent material described in step is 2. the mixture of gac and flyash; The mass ratio of gac and flyash is 1:(1 ~ 4); The volume ratio that gac adds quality and sewage is 2.5 ~ 7.5g/L.
CN201510654489.9A 2015-10-12 2015-10-12 Oil removal treatment method for high-concentration sewage in coal chemical industry Pending CN105174552A (en)

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CN105668846A (en) * 2016-01-15 2016-06-15 中国石油大学(华东) Fine processing technology of coal chemical aromatics-containing wastewater
CN112047550A (en) * 2020-08-28 2020-12-08 环球润博能源科技(北京)有限公司 System and method for treating wastewater containing complex organic pollutants and ammonia nitrogen
CN113429019A (en) * 2021-06-24 2021-09-24 广东省科学院资源利用与稀土开发研究所 Method for purifying and removing oil from industrial waste water containing rare earth

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Application publication date: 20151223