CN1180986C - A method and special device for treating oilfield wastewater by electric-heterogeneous catalytic reaction - Google Patents

A method and special device for treating oilfield wastewater by electric-heterogeneous catalytic reaction Download PDF

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CN1180986C
CN1180986C CNB011389761A CN01138976A CN1180986C CN 1180986 C CN1180986 C CN 1180986C CN B011389761 A CNB011389761 A CN B011389761A CN 01138976 A CN01138976 A CN 01138976A CN 1180986 C CN1180986 C CN 1180986C
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旭 杨
杨旭
孙承林
谢茂松
徐桂芬
王贤高
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Dalian Institute of Chemical Physics of CAS
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Abstract

本发明提供一种工业废水处理途径,即一种用电-多相催化反应处理油田废水的方法,在外加电场存在的条件下,使油田废水中有机污染物在催化剂表面催化氧化,其中所述催化剂由活性组分和载体组成,以Fe、Co、Ni、Mn、Cu、Ti、W或Pb中一种或几种的氧化物为活性组分担载在SiO2、Al2O3、沸石分子筛或活性炭载体上,其中金属组分的重量百分含量为1~10%,其电场中电极间直流电压为12~14V,电流密度为125mA~600mA/平方分米;其中所述催化剂中可添加稀土金属中一种或几种的氧化物作为助剂,该催化剂采用浸渍、烘干、焙烧制成;可有效处理油田开采过程中产生的含油废水以及二硝基苯酚废水,化肥厂废水,切削液废水等;中试结果表明,该技术处理油田废水可直接达标排放,运行费用低廉。

Figure 01138976

The present invention provides a method for treating industrial wastewater, that is, a method for treating oilfield wastewater by using electric-heterogeneous catalytic reaction. Under the condition of an external electric field, the organic pollutants in the oilfield wastewater are catalyzed and oxidized on the surface of the catalyst, wherein the The catalyst is composed of an active component and a carrier, with one or more oxides of Fe, Co, Ni, Mn, Cu, Ti, W or Pb as the active component supported on SiO 2 , Al 2 O 3 , zeolite molecular sieve Or activated carbon carrier, wherein the weight percentage of the metal component is 1-10%, the DC voltage between the electrodes in the electric field is 12-14V, and the current density is 125mA-600mA/square decimeter; wherein the catalyst can be added One or several oxides of rare earth metals are used as additives. The catalyst is made by impregnation, drying and roasting; it can effectively treat oily wastewater and dinitrophenol wastewater generated in the process of oilfield exploitation, wastewater from chemical fertilizer plants, cutting Liquid wastewater, etc.; the pilot test results show that this technology can directly discharge the oilfield wastewater up to the standard, and the operation cost is low.

Figure 01138976

Description

一种用电-多相催化反应处理油田废水的方法及专用装置A method and special device for treating oilfield wastewater by electro-heterogeneous catalytic reaction

技术领域technical field

本发明涉及工业废水处理,具体地说是一种用电-多相催化反应处理油田废水的方法及专用装置。The invention relates to industrial waste water treatment, in particular to a method and a special device for treating oil field waste water by electric-heterogeneous catalytic reaction.

背景技术Background technique

石油开采废水(油田开采过程中产生含油废水)主要来自钻井、采油、洗井、井下作业等不同的工段,这些工段排出的废水中含有石油类、CODCr、挥发酚、硫化物、SS等污染物。这些油田废水属难降解有机废水,难以用生化等常用的方法进行治理;生物降解是最常用的处理废水的过程,但是如二硝基苯酚废水,化肥厂废水,切削液废水等工业废水难以用生物降解的方法进行处理,必须采用新的技术,新的工艺加以处理。Oil extraction wastewater (oily wastewater generated during oilfield exploitation) mainly comes from different sections such as drilling, oil extraction, well washing, and downhole operations. The wastewater discharged from these sections contains petroleum, COD Cr , volatile phenol, sulfide, SS, etc. things. These oilfield wastewaters are refractory organic wastewaters, which are difficult to be treated by common methods such as biochemistry; biodegradation is the most commonly used process for treating wastewater, but industrial wastewater such as dinitrophenol wastewater, fertilizer factory wastewater, and cutting fluid wastewater is difficult to use. Biodegradable methods must be used to deal with new technologies and new processes.

电催化氧化主要利用在电解处理过程中产生的大量·OH自由基,使有机污染物得到降解(宋卫锋等,水处理技术,27(2001.2)90-92)。而电一多相催化氧化(谢茂松等,大连铁道学院学报,19(1998.2)35-37)与电催化氧化不同,外加电压和流经反应器的电流大小在一定的量值范围内对治理废水的效果没有明显的影响;谢茂松等人早期曾提出过一种电—多相催化反应过程(ZL.92106153.6),该技术是把化学催化与电催化过程结合到一起,利用催化剂活性组分和电激活的共同作用,使反应分子活化,可在较温和反应条件下进行单用催化剂不能发生的反应。利用这种技术可以处理啤酒厂的废水(ZL.92106153.6)、化肥厂废水(ZL.00122912)等,并建成了处理化肥废水的工业化装置,处理量为200吨/小时,通过了省市两级环保部门验收。至今运行已两年多,经处理过的废水可以回用,节省了大量的工业用水;电-多相催化氧化是在常温常压下,在电场与催化剂的协同作用下,使大分子有机物转化为小分子或CO2和水,减少有害物质的含量,从而达到废水的排放标准。Electrocatalytic oxidation mainly utilizes a large number of OH free radicals generated in the electrolytic treatment process to degrade organic pollutants (Song Weifeng et al., Water Treatment Technology, 27 (2001.2) 90-92). However, electro-heterogeneous catalytic oxidation (Xie Maosong et al., Journal of Dalian Railway Institute, 19 (1998.2) 35-37) is different from electrocatalytic oxidation. The effect of wastewater has no obvious influence; Xie Maosong and others have proposed an electric-heterogeneous catalytic reaction process (ZL.92106153.6) in the early stage. The combined effect of electroactivation and electroactivation activates the reaction molecules, and can carry out reactions that cannot occur with catalysts alone under milder reaction conditions. This technology can be used to treat brewery wastewater (ZL.92106153.6), chemical fertilizer factory wastewater (ZL.00122912), etc., and has built an industrialized device for treating fertilizer wastewater with a processing capacity of 200 tons per hour. It has passed the provincial and municipal levels Acceptance by the environmental protection department. It has been in operation for more than two years so far, and the treated wastewater can be reused, saving a lot of industrial water; the electro-heterogeneous catalytic oxidation is at normal temperature and pressure, under the synergistic effect of an electric field and a catalyst, to convert macromolecular organic matter For small molecules or CO 2 and water, reduce the content of harmful substances, so as to meet the discharge standards of wastewater.

电-多相催化氧化和其它的水处理技术相比,有许多优点:如反应条件温和,常温常压下进行;对水质没有特殊的要求;运行费用低;所需的设备简单,占地面积小,操作简便;不产生二次污染;特别适合处理一些中等浓度难降解的废水,对某些浓度不高、但毒性大、不适合生化处理的废水,也能收到好的效果。Compared with other water treatment technologies, electro-heterogeneous catalytic oxidation has many advantages: such as mild reaction conditions, carried out under normal temperature and pressure; no special requirements for water quality; low operating costs; simple equipment required, occupying an area of Small, easy to operate; no secondary pollution; especially suitable for treating some medium-concentrated wastewater that is difficult to degrade, and can also receive good results for some wastewater that is not high in concentration but highly toxic and not suitable for biochemical treatment.

在用电-多相催化反应处理含有机物工业废水过程中,有机物降解实际上是有机物被催化氧化而分解;其反应过程是,一方面于外加电场的激活下,可在水溶液中引发产生以·OH为主的自由基,由于生成的·OH自由基具有很强的氧化性和对有机物反应的无选择性,使得生物难降解的有机物在常温常压下的催化氧化成为可能;另一方面,被处理的有机物可在催化剂表面被选择地进行催化氧化;因此,电-多相催化技术需在电场及催化剂的协同作用下实现有机物的降解,选择适当含活性组分的催化剂和电场条件就可高效率地进行催化氧化分解有机物的反应。In the process of using electro-heterogeneous catalytic reaction to treat industrial wastewater containing organic matter, the degradation of organic matter is actually the decomposition of organic matter by catalytic oxidation; the reaction process is that, on the one hand, under the activation of an external electric field, the following OH-based free radicals, because the generated OH free radicals have strong oxidation and non-selectivity to organic reactions, make it possible to catalyze the oxidation of biodegradable organics at normal temperature and pressure; on the other hand, The organic matter to be treated can be selectively catalyzed and oxidized on the surface of the catalyst; therefore, electro-heterogeneous catalytic technology needs to realize the degradation of organic matter under the synergistic effect of electric field and catalyst. Efficiently carry out the reaction of catalytic oxidation and decomposition of organic matter.

发明内容Contents of the invention

本发明的目的在于提供一种适当的活性组分的催化剂和电场条件的用电-多相催化反应处理油田废水的方法及专用装置。The object of the present invention is to provide a method and a special device for treating oilfield wastewater by electro-heterogeneous catalytic reaction with suitable active component catalyst and electric field conditions.

为实现上述目的,本发明技术方案为:在外加电场存在的条件下,使油田废水中有机污染物在催化剂表面催化氧化,其中所述催化剂由活性组分和载体组成,以Fe、Co、Ni、Mn、Cu、Ti、W或Pb中一种或几种的氧化物为活性组分担载在SiO2、Al2O3、沸石分子筛或活性炭载体上,其中金属组分的重量百分含量为1~10%,余量为载体,其电场中电极间直流电压为12~14V,电流密度为每平方分米125mA~600mA;In order to achieve the above object, the technical solution of the present invention is: under the condition of the presence of an external electric field, the organic pollutants in the oilfield wastewater are catalyzed and oxidized on the surface of the catalyst, wherein the catalyst is composed of an active component and a carrier, and is composed of Fe, Co, Ni One or several oxides of Mn, Cu, Ti, W or Pb are active components loaded on SiO 2 , Al 2 O 3 , zeolite molecular sieves or activated carbon supports, and the weight percentage of metal components is 1-10%, the rest is the carrier, the DC voltage between the electrodes in the electric field is 12-14V, and the current density is 125mA-600mA per square decimeter;

其中:所述催化剂中可添加稀土金属中一种或几种的氧化物作为助剂,重量百分含量为金属组份总重量的1/6~1/5;所述催化剂中金属组分的重量百分含量最好为1~5%;Wherein: one or more oxides of rare earth metals can be added as additives in the catalyst, and the weight percentage is 1/6 to 1/5 of the total weight of the metal component; the metal component in the catalyst The weight percentage is preferably 1 to 5%;

所述催化剂可采用浸渍法制备,用含有金属离子的可溶性氯化物或硝酸盐水溶液,浸渍载体后,静置,烘干,再于300~450℃下进行焙烧2~4小时,即可得成品;The catalyst can be prepared by an impregnation method. The carrier is impregnated with a soluble chloride or nitrate aqueous solution containing metal ions, left to stand, dried, and then roasted at 300-450°C for 2-4 hours to obtain the finished product ;

所述催化剂制备中的可溶性氯化物或硝酸盐水溶液浓度为0.12~2.0mol/l,溶液与载体体积比为0.8~1.5∶1;所述催化剂静置是指于25~30℃条件下置放10~24小时,烘干是在110~130℃温度范围内进行;所述催化剂在以活性炭为载体时,焙烧是在氮气保护下进行;The concentration of the soluble chloride or nitrate aqueous solution in the preparation of the catalyst is 0.12-2.0mol/l, and the volume ratio of the solution to the carrier is 0.8-1.5:1; 10-24 hours, the drying is carried out in the temperature range of 110-130 ° C; when the catalyst is supported by activated carbon, the roasting is carried out under the protection of nitrogen;

所述催化剂制备方法的专用装置为槽式结构反应器,主要由槽体、顶盖、电极、催化剂组成,反应器采用PVC为材质,在其下部的侧壁上设有进水管,在其上部的侧壁上设有出水管,在其底部设有曝气管,另装有分布板于曝气管上方,在分布板上放置一对或多对带菱形网眼的平行钛电极,面积视反应器容积而定,为电极所包容体积为反应器体积的32~56%,催化剂填充在电极周围。The special device for the catalyst preparation method is a trough structure reactor, which is mainly composed of a tank body, a top cover, an electrode, and a catalyst. The reactor is made of PVC, and a water inlet pipe is provided on the side wall of its lower part. There is an outlet pipe on the side wall, an aeration pipe at the bottom, and a distribution plate above the aeration pipe. One or more pairs of parallel titanium electrodes with diamond mesh are placed on the distribution plate. The area depends on the reaction. Depending on the volume of the reactor, the volume contained in the electrode is 32-56% of the volume of the reactor, and the catalyst is filled around the electrode.

本发明具有如下优点:The present invention has the following advantages:

1.本发明方法可有效处理油田开采过程中产生含油废水、二硝基苯酚废水、化肥厂废水及切削液废水等工业废水;中试结果表明,该技术处理油田废水可直接达到排放标准,特别是使难以生化的含油废水,达到国家一级排放标准,与现有技术中处理CODCr只能降到200mg/L方法相比,本发明CODCr能降到92mg/L。1. The inventive method can effectively process industrial waste water such as oily waste water, dinitrophenol waste water, chemical fertilizer plant waste water and cutting fluid waste water in the process of oil field exploitation; It is to make the oily wastewater which is difficult to biochemically meet the national first-class discharge standard. Compared with the method in the prior art which can only reduce COD Cr to 200 mg/L, the COD Cr of the present invention can be reduced to 92 mg/L.

2.本发明方法操作简便,反应条件温和,在常温常压下进行,特别适合处理一些中等浓度难降解废水,运行费用低廉,设备简单,无二次污染产生。2. The method of the present invention is easy to operate, has mild reaction conditions, and is carried out under normal temperature and pressure. It is especially suitable for treating some medium-concentration refractory wastewater, with low operating costs, simple equipment, and no secondary pollution.

3.本发明方法采用PVC为材质的槽式结构反应器,在反应器中放置一对或多对带菱形网眼的平行钛电极,电极所包容体积为反应器体积的32~56%,处理效果可达最高。3. the inventive method adopts PVC to be the trough structure reactor of material, places one or more pairs of parallel titanium electrodes with diamond-shaped mesh in the reactor, and the contained volume of the electrodes is 32~56% of the reactor volume, and the treatment effect up to max.

附图说明Description of drawings

图1为不同电极宽度对废水处理结果的影响图谱;其中B:L电极宽度/L反应器宽度:32%以下,C:L电极宽度/L反应器宽度:32~56%之间,D:L电极宽度/L反应器宽度:56%以上。(电极宽度指极板宽度,电极间距离与电极高度不变)Figure 1 is a map of the influence of different electrode widths on wastewater treatment results; where B: L electrode width /L reactor width : below 32%, C: L electrode width /L reactor width : between 32% and 56%, D: L electrode width /L reactor width : more than 56%. (Electrode width refers to the width of the pole plate, the distance between electrodes and the height of the electrodes remain unchanged)

图2为电—多相催化反应器示意图。Figure 2 is a schematic diagram of the electro-heterogeneous catalytic reactor.

具体实施方式Detailed ways

实施例1Example 1

M/SiO2催化剂的制备:Preparation of M/ SiO2 catalyst:

取0.18mol/L的Fe(NO3)3溶液100ml,将100克40~60目SiO2颗粒倒入浸渍液中搅拌,放置10小时,于110℃下烘干2小时,再于400℃下焙烧3小时,自然冷却到室温制成催化剂A。催化剂A中金属组分的重量为:Fe:1%,其余为载体SiO2Take 100ml of 0.18mol/L Fe(NO 3 ) 3 solution, pour 100 grams of 40-60 mesh SiO 2 particles into the impregnating solution and stir, let stand for 10 hours, dry at 110°C for 2 hours, and then dry at 400°C Calcined for 3 hours, naturally cooled to room temperature to make catalyst A. The weight of metal components in catalyst A is: Fe: 1%, the rest is carrier SiO 2 .

实施例2Example 2

M/Al2O3和M/沸石催化剂的制备:Preparation of M/ Al2O3 and M/zeolite catalysts:

以Al2O3或分子筛沸石取代实施例1中的SiO2颗粒,其余与实施例1相同,制备成含Fe:1%的M/Al2O3催化剂B或含Fe:1%的M/沸石型催化剂C。Replace the SiO particles in Example 1 with Al 2 O 3 or molecular sieve zeolite, and the others are the same as in Example 1 to prepare M/Al 2 O 3 catalyst B containing Fe: 1% or M/Al containing Fe: 1%. Zeolite catalyst C.

实施例3Example 3

M/活性炭催化剂的制备:Preparation of M/activated carbon catalyst:

①以中孔活性炭取代实施例1中的SiO2粉,并在氮气氛下进行焙烧,其余与实施例1相同,制备成含Fe:1%的M/活性炭型催化剂D1。① Replace the SiO2 powder in Example 1 with mesoporous activated carbon, and roast it under a nitrogen atmosphere. The rest are the same as Example 1, and prepare M/activated carbon catalyst D1 containing Fe: 1%.

②以中孔活性炭取代实施例1中的SiO2粉,并在实施例1中的浸渍溶液中添加0.18mol/L的硝酸镧溶液10ml,并在N2气氛下焙烧,其余条件和步骤同实施例1。制备成La0.2%-Fel%的M/活性炭型催化剂D2。2. replace the SiO powder in Example 1 with mesoporous activated carbon, and add 10ml of lanthanum nitrate solution of 0.18mol/L in the impregnation solution in Example 1, and roast under N atmosphere, and all the other conditions and steps are implemented with the same example 1. The M/activated carbon type catalyst D2 prepared as La0.2%-Fel%.

实施例4Example 4

对于油田废水的电—多相催化静态实验:Static experiment of electro-heterogeneous catalysis for oil field wastewater:

所用原水CODCr:503mg/l,BOD5:18mg/l,BOD5/CODCr:0.036,PH:7,浅黄色。The raw water COD Cr : 503mg/l, BOD 5 : 18mg/l, BOD 5 /COD Cr : 0.036, PH: 7, light yellow.

在以PVC为材质的电—多相催化槽式结构反应器由槽体(2)、顶盖(3)、电极(4)、催化剂(5)组成,在其下部侧壁上设有进水管(1),在其上部侧壁上设有出水管(6),在其底部设有曝气管(8),另装有分布板(7)于曝气管(8)上方,在分布板(7)上竖直放置3对带菱形网眼的平行钛电极(4),其面积为电极所包容体积为反应器体积的56%,催化剂(5)填充在电极(4)周围;将400ml原水加入装有电极的反应器中,静态反应。经过不同的处理时间,取样分析,结果见表1。(CODCr采用水质化学需氧量的测定重铬酸盐法(GB 11914-89)进行分析)The electro-heterogeneous catalytic tank structure reactor made of PVC is composed of a tank body (2), a top cover (3), an electrode (4), and a catalyst (5), and a water inlet pipe is provided on its lower side wall (1), an outlet pipe (6) is provided on its upper side wall, an aeration pipe (8) is provided at its bottom, and a distribution plate (7) is installed above the aeration pipe (8). (7) vertically place 3 pairs of parallel titanium electrodes (4) with diamond-shaped meshes, its area is that the contained volume of the electrodes is 56% of the reactor volume, and the catalyst (5) is filled around the electrodes (4); 400ml of raw water Added to the reactor equipped with electrodes, static reaction. After different processing times, samples were taken and analyzed, and the results are shown in Table 1. (COD Cr is analyzed by the dichromate method (GB 11914-89) for the determination of chemical oxygen demand in water quality)

表1.电—多相催化法对油田废水静态处理结果 处理时间(h)   电压-电流 反应后CODCr(mg/l)     1   12V-400mA     253     2     195     3     149     4     120 Table 1. Static treatment results of oilfield wastewater by electro-heterogeneous catalysis Processing time (h) Voltage and current COD Cr after reaction (mg/l) 1 12V-400mA 253 2 195 3 149 4 120

由表1.实验结果看,用电—多相催化法处理油田废水,效果较好,处理后的废水可以达到国家二级排放标准。From the experimental results in Table 1, it can be seen that the treatment of oilfield wastewater by electro-heterogeneous catalysis has a good effect, and the treated wastewater can meet the national secondary discharge standard.

实施例5Example 5

对于油田废水的电—多相催化连续实验(I):Continuous experiment of electro-heterogeneous catalysis for oilfield wastewater (I):

在以PVC为材质的电—多相催化反应器中,平行放置两块带菱形网眼的钛电极,装填100ml按实施例1制备的催化剂A,用蠕动泵连续进样,在一定的外加电流条件下,采用不同的空速,进行处理。每个水样取完全平衡后数值。In an electric-heterogeneous catalytic reactor made of PVC, two titanium electrodes with diamond-shaped meshes are placed in parallel, and 100ml of catalyst A prepared in Example 1 is filled, and a peristaltic pump is used for continuous sample injection. Next, different airspeeds are used for processing. Each water sample takes the value after complete equilibrium.

反应温度25℃,常压,原水CODCr:506mg/,PH:6-7,浅米黄色,出水几乎无色,反应结果列于表2。The reaction temperature is 25°C, normal pressure, raw water COD Cr : 506mg/, PH: 6-7, light beige, and the effluent is almost colorless. The reaction results are listed in Table 2.

          表2.催化剂A对油田废水的处理结果 空速(V∶V催化剂)     2.2     2.5     2.9     3.3     4.0 反应后CODCr(mg/l)     65     78     97     115     137 Table 2. Catalyst A treatment results for oilfield wastewater Space velocity (V water : V catalyst ) 2.2 2.5 2.9 3.3 4.0 COD Cr after reaction (mg/l) 65 78 97 115 137

实施例6Example 6

对于油田废水的电—多相催化连续实验(II):Continuous experiment of electro-heterogeneous catalysis for oilfield wastewater (II):

原水CODCr:504mg/l。采用实施例2制备的催化剂B,其余条件与实施例5同,反应结果列于表3。Raw water COD Cr : 504mg/l. Adopt the catalyst B prepared by embodiment 2, all the other conditions are the same as embodiment 5, and the reaction results are listed in table 3.

表3.催化剂B处理油田废水的结果   空速(V∶V催化剂)   2.2   2.5   2.9   3.3   4.0   反应后CODCr(mg/l)   50   65   84   102   117 Table 3. Results of Catalyst B Treating Oilfield Wastewater Space velocity (V water : V catalyst ) 2.2 2.5 2.9 3.3 4.0 COD Cr after reaction (mg/l) 50 65 84 102 117

实施例7Example 7

对于油田废水的电—多相催化连续实验(III):Continuous experiment of electro-heterogeneous catalysis for oilfield wastewater (III):

原水CODCr:503mg/l。采用实施例3制备的催化剂C,其余条件与实施例5同,反应结果列于表4。Raw water COD Cr : 503mg/l. Catalyst C prepared in Example 3 was adopted, and all the other conditions were the same as in Example 5. The reaction results are listed in Table 4.

           表4.催化剂C处理油田废水的结果   空速(V∶V催化剂)   2.2   2.5   2.9   3.3   4.0   反应后CODCr(mg/l)   48   60   70   77   93 Table 4. Results of Catalyst C Treating Oilfield Wastewater Space velocity (V water : V catalyst ) 2.2 2.5 2.9 3.3 4.0 COD Cr after reaction (mg/l) 48 60 70 77 93

实施例8Example 8

对于油田废水的电—多相连续实验(IV):For the electric-multiphase continuous experiment of oilfield wastewater (IV):

原水CODCr:506mg/L,采用实施例3②中制备的催化剂D2,其余条件与实施例5同,处理结果列于表5。Raw water COD Cr : 506mg/L, adopts the catalyst D2 prepared in embodiment 3②, all the other conditions are the same as embodiment 5, and the treatment results are listed in table 5.

          表5.催化剂D2处理油田废水的结果    空速(V∶V催化剂)   2.2   2.5   2.9   3.3   4.0   反应后CODCr(mg/l)   32   40   56   69   80 Table 5. Results of Catalyst D2 Treating Oilfield Wastewater Space velocity (V water : V catalyst ) 2.2 2.5 2.9 3.3 4.0 COD Cr after reaction (mg/l) 32 40 56 69 80

实施例9Example 9

电极宽度对处理效果的影响:Influence of electrode width on treatment effect:

在同一个电—多相催化反应器中,使用等量的催化剂,改变电极宽度,其余条件与实施例7同,反应结果列于表6。In the same electro-heterogeneous catalytic reactor, the same amount of catalyst was used, the electrode width was changed, and the other conditions were the same as in Example 7. The reaction results are listed in Table 6.

表6.不同电极宽度对废水处理效率的影响Table 6. Effect of different electrode widths on wastewater treatment efficiency

               L电极宽度/L反应器宽度:32%以下 空速(V∶V催化剂)     2.9     3.3     3.7     4.0 反应后CODCr(mg/l)     72     83     104     120 L electrode width /L reactor width : below 32% Space velocity (V water : V catalyst ) 2.9 3.3 3.7 4.0 COD Cr after reaction (mg/l) 72 83 104 120

            L电极宽度/L反应器宽度:32~56%之间 空速(V∶V催化剂)     2.9     3.3     3.7     4.0 反应后CODCr(mg/l)     62     75     82     93 L electrode width /L reactor width : between 32% and 56% Space velocity (V water : V catalyst ) 2.9 3.3 3.7 4.0 COD Cr after reaction (mg/l) 62 75 82 93

            L电极宽度/L反应器宽度:56%以上 空速(V∶V催化剂)     2.9     3.3     3.7     4.0 反应后CODCr(mg/l)     80     89     99     112 L electrode width /L reactor width : more than 56% Space velocity (V water : V catalyst ) 2.9 3.3 3.7 4.0 COD Cr after reaction (mg/l) 80 89 99 112

不同电极宽度对废水处理结果的影响图谱见图1,由图1.可知,当电极宽度为反应器宽度的32~56%时,处理效率最高。The influence spectrum of different electrode widths on the wastewater treatment results is shown in Figure 1. It can be seen from Figure 1 that when the electrode width is 32-56% of the reactor width, the treatment efficiency is the highest.

实施例10Example 10

对于油田废水的电—多相催化中试实验:For the electro-heterogeneous catalysis pilot test of oilfield wastewater:

基于实验室较好的反应结果,在油田现场进行中试。中试采用槽式反应器,使用催化剂C,电极采用带菱形网眼的钛电极,多组电极,电极间距20cm,在反应槽中加400立升催化剂。用潜水泵把池中水抽出,经过转子流量计计量后进入反应槽。含油废水的CODCr为200mg/L,进水量为800升/小时。反应后出水PH:6-7,颜色很浅,稳定运行12天。中试结果见表7。Based on the good reaction results in the laboratory, a pilot test was carried out in the oil field. The pilot test adopts a tank reactor, uses catalyst C, and uses titanium electrodes with rhombic mesh as the electrodes. There are multiple sets of electrodes with an electrode spacing of 20 cm, and 400 liters of catalyst are added to the reaction tank. Use a submersible pump to pump out the water in the pool, and enter the reaction tank after being measured by the rotameter. The COD Cr of oily waste water is 200mg/L, and the inflow is 800 liters/hour. After the reaction, the pH of the effluent is 6-7, the color is very light, and it runs stably for 12 days. The results of the pilot test are shown in Table 7.

表7.电—多相催化法处理油田废水中试结果 空速(V∶V催化剂) 反应后CODCr(mg/l) 运行费用*(元/吨) 2.1 92 1.0 Table 7. Pilot test results of electro-heterogeneous catalytic treatment of oilfield wastewater Space velocity (V water : V catalyst ) COD Cr after reaction (mg/l) Operating cost * (yuan/ton) 2.1 92 1.0

*运行费用只包括电耗 * Operating cost includes electricity consumption only

表8.电—多相催化法处理油田废水中试稳定性结果   运行天数     1   2   3   4   5   6   7   8   9   10   11   12   处理后CODCr(mg/L)     50   90   92   98   85   87   90   90   92   89   92   88 Table 8. The stability results of the pilot test for the treatment of oilfield wastewater by electro-heterogeneous catalysis days of operation 1 2 3 4 5 6 7 8 9 10 11 12 After treatment COD Cr (mg/L) 50 90 92 98 85 87 90 90 92 89 92 88

*V水∶V水::催化剂=2.1,电压:14V,电流密度:125mA/平方分米 * V water water : V water:: catalyst = 2.1, voltage: 14V, current density: 125mA/square decimeter

由表7、8的实验结果看,采用电—多相催化氧化技术处理低CODCr的含油废水,可以达到国家一级排放标准,在油田具有广泛的应用前景。From the experimental results in Tables 7 and 8, it can be seen that the electro-heterogeneous catalytic oxidation technology is used to treat oily wastewater with low COD Cr , which can meet the national first-level discharge standards and has broad application prospects in oil fields.

Claims (7)

1. an electricity consumption-heterogeneous catalytic reaction is handled the method for oil field waste, it is characterized in that: under the condition that extra electric field exists, make in the oil field waste organic pollutant at the catalyst surface catalyzed oxidation, wherein said catalyzer is made up of active ingredient and carrier, is that active ingredient is supported on SiO with one or more oxide compound among Fe, Co, Ni, Mn, Cu, Ti, W or the Pb 2, Al 2O 3, on zeolite molecular sieve or the absorbent charcoal carrier, wherein the weight percentage of metal component is 1~10%, in its electric field between electrode volts DS be 12~14V, current density is every square decimeter of 125mA~600mA; Electrode width is 32~56% of a reactor width.
2. method according to claim 1 is characterized in that: the oxide compound that can add in the rare earth metal one or more in the wherein said catalyzer is as auxiliary agent, and weight percentage is 1/6~1/5 of a metal component gross weight.
3. method according to claim 1 and 2 is characterized in that: the weight percentage of metal component is 1~5% in the described catalyzer.
4. method according to claim 1 and 2, it is characterized in that: wherein said catalyzer can adopt immersion process for preparing, with soluble chloride that contains metal ion or nitrate aqueous solution, behind the impregnated carrier, leave standstill, roasting 2~4 hours is carried out in oven dry again under 300~450 ℃, can obtain finished catalyst.
5. method according to claim 4 is characterized in that: soluble chloride or nitrate aqueous solution concentration are 0.12~2.0mol/l in the wherein said catalyzer, and solution is 0.8~1.5: 1 with the carrier bulk ratio.
6. method according to claim 4 is characterized in that: wherein said catalyzer leaves standstill and is meant under 25~30 ℃ of conditions and put 10~24 hours, and oven dry is to carry out in 110~130 ℃ of temperature ranges.
7. method according to claim 4 is characterized in that: wherein said catalyzer is when being carrier with the gac, and roasting is to carry out under nitrogen protection.
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