CN107417018B - A method of removing oil from wastewater - Google Patents
A method of removing oil from wastewater Download PDFInfo
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- CN107417018B CN107417018B CN201710693317.1A CN201710693317A CN107417018B CN 107417018 B CN107417018 B CN 107417018B CN 201710693317 A CN201710693317 A CN 201710693317A CN 107417018 B CN107417018 B CN 107417018B
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- 239000002351 wastewater Substances 0.000 title claims abstract description 63
- 238000000034 method Methods 0.000 title claims abstract description 18
- 239000003921 oil Substances 0.000 claims abstract description 69
- 238000001179 sorption measurement Methods 0.000 claims abstract description 43
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 31
- 239000000295 fuel oil Substances 0.000 claims abstract description 17
- 230000003197 catalytic effect Effects 0.000 claims abstract description 16
- 238000004062 sedimentation Methods 0.000 claims abstract description 16
- 238000003795 desorption Methods 0.000 claims abstract description 15
- 238000007667 floating Methods 0.000 claims abstract description 14
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical class O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 12
- 238000006555 catalytic reaction Methods 0.000 claims abstract description 11
- 229910052703 rhodium Inorganic materials 0.000 claims abstract description 9
- 239000010948 rhodium Substances 0.000 claims abstract description 9
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims abstract description 9
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical group [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 8
- 238000000746 purification Methods 0.000 claims abstract description 7
- 239000012528 membrane Substances 0.000 claims description 23
- 238000006243 chemical reaction Methods 0.000 claims description 17
- 229910001220 stainless steel Inorganic materials 0.000 claims description 17
- 239000010935 stainless steel Substances 0.000 claims description 17
- 239000010410 layer Substances 0.000 claims description 15
- 239000000126 substance Substances 0.000 claims description 12
- 238000009413 insulation Methods 0.000 claims description 10
- 239000002245 particle Substances 0.000 claims description 8
- 238000005485 electric heating Methods 0.000 claims description 7
- 238000006116 polymerization reaction Methods 0.000 claims description 7
- 239000004964 aerogel Substances 0.000 claims description 6
- 238000005238 degreasing Methods 0.000 claims description 5
- 238000005215 recombination Methods 0.000 claims description 5
- 230000006798 recombination Effects 0.000 claims description 5
- 239000007788 liquid Substances 0.000 claims description 4
- 238000003756 stirring Methods 0.000 claims description 4
- 238000005352 clarification Methods 0.000 claims description 3
- 238000012856 packing Methods 0.000 claims description 3
- 229920000642 polymer Polymers 0.000 claims description 3
- 239000002685 polymerization catalyst Substances 0.000 claims description 3
- 238000001556 precipitation Methods 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims description 3
- 239000011241 protective layer Substances 0.000 claims description 2
- 230000006641 stabilisation Effects 0.000 claims description 2
- 238000011105 stabilization Methods 0.000 claims description 2
- 238000004220 aggregation Methods 0.000 claims 1
- 230000002776 aggregation Effects 0.000 claims 1
- -1 allyl nickel compound modified diatomite Chemical class 0.000 claims 1
- 230000007935 neutral effect Effects 0.000 claims 1
- 235000019198 oils Nutrition 0.000 description 49
- 239000010865 sewage Substances 0.000 description 7
- 239000000945 filler Substances 0.000 description 5
- 244000005700 microbiome Species 0.000 description 5
- 230000000694 effects Effects 0.000 description 4
- 238000005188 flotation Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 239000013618 particulate matter Substances 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 2
- 229910052759 nickel Inorganic materials 0.000 description 2
- PXHVJJICTQNCMI-UHFFFAOYSA-N nickel Substances [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000003786 synthesis reaction Methods 0.000 description 2
- 239000003440 toxic substance Substances 0.000 description 2
- 239000010775 animal oil Substances 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000007036 catalytic synthesis reaction Methods 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000002848 electrochemical method Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000005284 excitation Effects 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 239000011152 fibreglass Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- 239000004519 grease Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 238000000053 physical method Methods 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- HBMJWWWQQXIZIP-UHFFFAOYSA-N silicon carbide Chemical group [Si+]#[C-] HBMJWWWQQXIZIP-UHFFFAOYSA-N 0.000 description 1
- 229910010271 silicon carbide Inorganic materials 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 235000015112 vegetable and seed oil Nutrition 0.000 description 1
- 235000019871 vegetable fat Nutrition 0.000 description 1
- 239000008158 vegetable oil Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/24—Treatment of water, waste water, or sewage by flotation
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/288—Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/40—Devices for separating or removing fatty or oily substances or similar floating material
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/4608—Treatment of water, waste water, or sewage by electrochemical methods using electrical discharges
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- C02F1/48—Treatment of water, waste water, or sewage with magnetic or electric fields
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- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
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- C02F2001/007—Processes including a sedimentation step
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- C02F2101/30—Organic compounds
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Abstract
本发明公开了一种废水除油方法,废水依次经过缓存池、粗格栅、微泡气浮油吸附装置、油催化重化解吸反应器、pH值调节池、一次沉淀池、有机铑催化反应槽、生物脱氮池、二次沉淀池、净水池。本方法创造性的利用了π‑烯丙基镍化合物对油分子的催化作用,当废水中的油被改性硅藻土吸附并处于200~250℃的温度下,在π‑烯丙基镍化合物的催化下,油分子中的C‑H键会发生短暂的断裂,并快速再结合为C‑C键或C‑H键,而C‑H键会再次发生断裂,C‑C键则因π‑烯丙基镍化合物的催化作用有限而不会再发生断裂,因此可使碳链较短的油分子逐渐合成为碳链较长的重油分子。
The invention discloses a method for removing oil from wastewater. The wastewater passes through a buffer pool, a coarse grid, a microbubble air floating oil adsorption device, an oil catalytic rechemical desorption reactor, a pH value adjustment tank, a primary sedimentation tank, and an organic rhodium catalytic reaction in sequence. tank, biological denitrification tank, secondary sedimentation tank, water purification tank. The method creatively utilizes the catalytic effect of π-allyl nickel compound on oil molecules. When the oil in the wastewater is adsorbed by modified diatomite and is at a temperature of 200-250 °C, the π-allyl nickel compound Under the catalysis, the C-H bond in the oil molecule will be broken for a short time, and quickly recombine into a C-C bond or a C-H bond, and the C-H bond will be broken again, and the C-C bond will be broken due to π ‑Allyl nickel compounds have a limited catalytic effect and will not break again, so oil molecules with shorter carbon chains can be gradually synthesized into heavy oil molecules with longer carbon chains.
Description
技术领域technical field
本发明涉及一种餐饮废水除油处理方法,属于环境保护中的废水处理领域。The invention relates to a method for degreasing treatment of catering wastewater, belonging to the field of wastewater treatment in environmental protection.
背景技术Background technique
生活污水中,餐饮含油污水是其中的一类主要水体。众多的餐厅、食堂、食品加工企业以及居民日常生活会排放大量的含有污水,其中含有大量的动植物油脂,如果不经处理直接方法,会造成管道的堵塞、水体的浑浊腐败、并滋生治病源。Among domestic sewage, oily sewage from catering is one of the main water bodies. Many restaurants, canteens, food processing enterprises and residents will discharge a large amount of sewage in their daily life, which contains a large amount of animal and vegetable oils and fats. source.
目前,现有的餐饮污水除油方法包括以下四种。At present, the existing catering wastewater degreasing methods include the following four.
(1)物理法主要包括过滤分离法、气浮分离法,但是均仅适用于分离废水中颗粒较大的油品,处理效率为60~80%,出水中含油量约为100~200毫克/升。废水中的细小油珠和乳化油则很难去除。(1) The physical method mainly includes filtration separation method and air flotation separation method, but they are only suitable for separating oil products with larger particles in wastewater, the treatment efficiency is 60-80%, and the oil content in the effluent is about 100-200 mg/ Lift. Small oil droplets and emulsified oils in wastewater are difficult to remove.
(2)化学法处理的优点是设备费用低、处理效果好、操作简单;缺点是需要不断向废水中投放化学药剂,其运行费用高,并会引入二次污染。(2) The advantages of chemical treatment are that the equipment cost is low, the treatment effect is good, and the operation is simple;
(3)物理化学法主要包括气浮法、吸附法、电化学法、超声波分离法等,这些方法一般都具有适应性较强、选择性广的优点。(3) Physical and chemical methods mainly include air flotation method, adsorption method, electrochemical method, ultrasonic separation method, etc. These methods generally have the advantages of strong adaptability and wide selectivity.
(4)生物化学(生化)处理法是利用微生物的生化作用,将复杂的有机物分解为简单物质,从而将有毒物质转化为无毒物质,使含油污水得到净化。微生物可将有机物作为营养物质,使其中一部分被吸收转化成为微生物体内的有机成分或增殖成新的微生物,其余部分可被微生物氧化分解成简单的有机或无机物质。(4) Biochemical (biochemical) treatment method uses the biochemical action of microorganisms to decompose complex organic matter into simple substances, thereby converting toxic substances into non-toxic substances, and purifying oily sewage. Microorganisms can use organic matter as nutrients, so that part of them can be absorbed and transformed into organic components in the microorganisms or proliferated into new microorganisms, and the rest can be oxidized and decomposed into simple organic or inorganic substances by microorganisms.
由于上述传统治理方法均存在一定的缺点,因此,有必要摆脱现有的治理技术路线,开辟出处理生活污水除油的新途径,进而开发一种全新形式的生活污水除油处理技术。Since the above traditional treatment methods all have certain shortcomings, it is necessary to get rid of the existing treatment technology route, open up a new way to treat domestic sewage and remove oil, and then develop a new form of domestic sewage degreasing treatment technology.
发明内容SUMMARY OF THE INVENTION
为解决现有技术中存在的不足,本发明提供了一种餐饮废水除油处理方法,餐饮废水通过废水管线进入缓存池,在此进行集中收集和稳定,缓存池的出口通过废水管线连接粗格栅,在此去除餐饮废水中的大直径固体物质,粗格栅的出口通过废水管线连接微气泡油吸附装置,微气泡油吸附装置底部装有9支超微细气泡发生器,装置的液面之上可容纳一张横向放置的π-烯丙基镍化合物改性硅藻土吸附膜,其左侧上部装有进水阀门,右侧底部装有出水阀门,经过粗格栅初步去除大粒径物质的含有油的餐饮废水通过微气泡油吸附装置左侧上部的进水阀门进入装置内部,9支超微细气泡发生器开始工作,产生直径小于50μm的超微细气泡,超微细气泡会夹带废水中的油分子一同上浮,并使其被液面之上的含π-烯丙基镍化合物改性硅藻土吸附膜吸附,该装置右侧壁因与高温的油催化重化解吸反应器相连,因此贴覆有气凝胶毡隔热层,气凝胶毡隔热层顶端装有不锈钢机械臂及转珠轴承;油催化重化解吸反应器采用高强度不锈钢材质,其底部装有5部电热鼓风风机,装置内部安装有一套不锈钢膜架,膜架上可竖直放置5张待高温处理的π-烯丙基镍化合物改性硅藻土吸附膜,其底部右侧设有重油排出口;完全吸附油的含π-烯丙基镍化合物改性硅藻土吸附膜被不锈钢机械臂抓取,并被竖直放置在油催化重化解吸反应器中的不锈钢膜架上,反应器底部的5部电热鼓风风机开始工作,产生200~250℃的高温空气,在π-烯丙基镍化合物的催化下,油分子中的C-H键会发生断裂并快速结合为C-C键,C-C键则不会再发生断裂,因此可使碳链较短的油分子逐渐合成为碳链较长的重油分子,同时,重油分子会在高温下从含π-烯丙基镍化合物改性硅藻土吸附膜中解吸,汇聚后从反应器底部右侧的重油排出口排出,可被集中收集和再利用;微泡气浮油吸附装置的出口通过废水管线连接pH值调节池,在此将废水的pH值调节至近中性,pH值调节池的出口通过废水管线连接一次沉淀池6,在此对废水进行沉淀澄清处理,一次沉淀池的出口通过废水管线连接有机铑催化反应槽,有机铑催化聚合反应槽的外层包裹有槽体绝缘保护层,反应槽的右上部设有进水阀门,左下部设有出水阀门,槽体中央部分安装有二氯四羰基二铑多孔填料,作为聚合反应催化剂,填料层下部连接有颗粒物排放口,左、右两侧壁板正中各安装有一支高压放电电极,在反应槽底部左、右两侧各装有一支搅拌桨叶,废水通过有机铑催化聚合反应槽的进水阀门进入反应槽内部,高压放电电极每间隔0.2s进行一次高压放电,产生一道高压电弧,高压电弧所产生的高能量被废水中残存的油脂吸收,油脂分子中的C-H键受到能量激发处于不稳定状态,并在二氯四羰基二铑的催化作用下发生C-H键断裂并重组,最终生成大分子聚合颗粒物,以悬浮物的形式分散于水中,并通过反应槽右侧的出水阀门排出反应槽,进入二次沉淀池,在此将废水中的剩余不溶物质全部除去,二次沉淀池的出口通过废水管线连接净水池,净水池的出口通过废水管线将处理后的净化出水外排。In order to solve the deficiencies in the prior art, the present invention provides a method for degreasing catering wastewater. The catering wastewater enters a buffer pool through a waste water pipeline, where centralized collection and stabilization are performed, and the outlet of the buffer pool is connected to the coarse grid through a waste water pipeline. The grid is used to remove large-diameter solid substances in the catering wastewater. The outlet of the coarse grid is connected to the micro-bubble oil adsorption device through the wastewater pipeline. The bottom of the micro-bubble oil adsorption device is equipped with 9 ultra-fine bubble generators. It can accommodate a horizontally placed π-allyl nickel compound modified diatomite adsorption membrane. The upper left side is equipped with a water inlet valve, and the right bottom is equipped with a water outlet valve. After the coarse grid, the large particle size is initially removed. The oil-containing food waste water enters the device through the inlet valve on the upper left side of the micro-bubble oil adsorption device, and 9 ultra-fine bubble generators start to work to generate ultra-fine bubbles with a diameter of less than 50 μm. The ultra-fine bubbles will be entrained in the wastewater. The oil molecules floated up together, and were adsorbed by the modified diatomite adsorption film containing π-allyl nickel compound above the liquid surface. Therefore, an aerogel felt insulation layer is attached, and the top of the aerogel felt insulation layer is equipped with a stainless steel mechanical arm and a ball bearing; the oil catalytic desorption reactor is made of high-strength stainless steel, and its bottom is equipped with 5 electric heaters Blower, a set of stainless steel membrane frame is installed inside the device. On the membrane frame, 5 sheets of π-allyl nickel compound modified diatomite adsorption membrane to be treated at high temperature can be placed vertically. There is a heavy oil discharge port on the right side of the bottom. ; The π-allyl nickel compound-modified diatomite adsorption membrane that completely adsorbs oil is grabbed by a stainless steel manipulator and placed vertically on the stainless steel membrane frame in the oil catalytic desorption reactor. The bottom of the reactor is The 5 electric heating blowers of the machine start to work, generating high temperature air at 200~250℃. Under the catalysis of π-allyl nickel compound, the C-H bond in the oil molecule will be broken and quickly combined into a C-C bond, and the C-C bond will be It will not break again, so the oil molecules with shorter carbon chains can be gradually synthesized into heavy oil molecules with longer carbon chains, and at the same time, the heavy oil molecules will be adsorbed from the modified diatomite containing π-allyl nickel compounds at high temperature It is desorbed in the membrane, collected and discharged from the heavy oil outlet on the right side of the bottom of the reactor, which can be collected and reused centrally; the outlet of the microbubble air floating oil adsorption device is connected to the pH value adjustment tank through the waste water pipeline, where the pH value of the waste water is adjusted. The pH value is adjusted to near neutrality, the outlet of the pH adjustment tank is connected to the primary sedimentation tank 6 through the waste water pipeline, and the wastewater is subjected to precipitation and clarification treatment. The outer layer of the tank is wrapped with an insulating protective layer of the tank body, the upper right part of the reaction tank is provided with a water inlet valve, the lower left part is provided with a water outlet valve, and the central part of the tank body is installed with dichlorotetracarbonyl dirhodium porous filler, which is used as a polymerization catalyst. A particle discharge port is connected to the lower part of the packing layer, a high-voltage discharge electrode is installed in the middle of the left and right side wall plates, and a stirring blade is installed on the left and right sides of the bottom of the reaction tank. The wastewater passes through the organic rhodium catalyzed polymerization reaction tank The water inlet valve enters the inside of the reaction tank, The high-voltage discharge electrode conducts a high-voltage discharge every 0.2s to generate a high-voltage arc. The high energy generated by the high-voltage arc is absorbed by the oil remaining in the wastewater, and the C-H bond in the oil molecule is excited by the energy. Under the catalysis of dirhodium tetracarbonyl, the C-H bond is broken and recombined, and finally macromolecular polymer particles are formed, which are dispersed in water in the form of suspension, and discharged from the reaction tank through the water outlet valve on the right side of the reaction tank, and enter the secondary sedimentation tank. Here, all the remaining insoluble substances in the wastewater are removed, the outlet of the secondary sedimentation tank is connected to the purification tank through the waste water pipeline, and the outlet of the purification tank discharges the treated purified effluent through the waste water pipeline.
其微泡气浮油吸附装置的有效容积为155m3,超微细气泡发生器能够产生直径小于50μm的超微细气泡,正常工作电压为20V,工作寿命一般为5000h。The effective volume of the microbubble air flotation oil adsorption device is 155m 3 , the ultra-fine bubble generator can generate ultra-fine bubbles with a diameter of less than 50 μm, the normal working voltage is 20V, and the working life is generally 5000h.
其油催化重化解吸反应器的容积为330m3,其电热鼓风风机可产生200~250℃的热空气,正常工作电压为380V。Its oil catalytic desorption reactor has a volume of 330m 3 , its electric heating blower can generate hot air at 200~250℃, and its normal working voltage is 380V.
π-烯丙基镍化合物改性硅藻土吸附膜的面积为10.2m2,π-烯丙基镍化合物的含量为16.6g/m2,π-烯丙基镍化合物的纯度为95.2%。The area of the π-allyl nickel compound modified diatomite adsorption membrane was 10.2 m 2 , the content of the π-allyl nickel compound was 16.6 g/m 2 , and the purity of the π-allyl nickel compound was 95.2%.
本发明的优点在于:The advantages of the present invention are:
(1)本发明摆脱了现有的餐饮废水油净化处理模式,创造性的采用了物理手段与化学方法相结合的技术路线,充分利用改性硅藻土的吸附作用和π-烯丙基镍化合物的催化合成作用,使餐饮废水中的油被吸附富集,并发生合成反应,生成可利用的重油,其油的去除效率达到99.8%。(1) The present invention gets rid of the existing catering wastewater oil purification treatment mode, creatively adopts a technical route combining physical means and chemical methods, and makes full use of the adsorption effect of modified diatomite and π-allyl nickel compounds. The catalytic synthesis effect of the catalyst makes the oil in the catering wastewater be adsorbed and enriched, and a synthesis reaction occurs to generate a usable heavy oil, and the oil removal efficiency reaches 99.8%.
(2)本发明利用热空气作为加热源,并采取了将π-烯丙基镍化合物分散于改性硅藻土中的方式,使合成反应进行的更加完全,提高了反应效率,提升了整个系统的处理能力。(2) The present invention uses hot air as a heating source, and adopts the method of dispersing the π-allyl nickel compound in the modified diatomite, so that the synthesis reaction is more complete, the reaction efficiency is improved, and the whole process is improved. The processing power of the system.
(3)本发明中所使用的改性硅藻土吸附膜经热解吸过程后得以再生,可被重新用于吸附废水中的油,实现了物料的重复利用,大大降低了运行成本。(3) The modified diatomite adsorption membrane used in the present invention is regenerated after the thermal desorption process, and can be reused to absorb oil in wastewater, realizing the reuse of materials and greatly reducing the operating cost.
(4)本发明原理简单易行,设计施工成本较低,并且处理效果较好,运行维护成本很低,有利于大范围推广应用。(4) The principle of the present invention is simple and easy to implement, the design and construction cost is low, the treatment effect is good, and the operation and maintenance cost is low, which is conducive to wide-scale popularization and application.
附图说明Description of drawings
图1是本发明的设备示意图。FIG. 1 is a schematic diagram of the apparatus of the present invention.
图中:1-缓存池、2-粗格栅、3-微泡气浮油吸附装置、4-油催化重化解吸反应器、5-pH值调节池、6-一次沉淀池、7-有机铑催化反应槽、8-二次沉淀池、9-净水池;In the picture: 1-buffer pool, 2-coarse grid, 3-microbubble air-floating oil adsorption device, 4-oil catalytic heavy chemical desorption reactor, 5-pH value adjustment tank, 6-primary sedimentation tank, 7-organic Rhodium catalytic reaction tank, 8-secondary sedimentation tank, 9-purification tank;
图2是微泡气浮油吸附装置和油催化重化解吸反应器的示意图。Figure 2 is a schematic diagram of a microbubble air-floating oil adsorption device and an oil catalytic recombination desorption reactor.
32-超微细气泡发生器、33-超微细气泡、34-不锈钢机械臂、35-转珠轴承、36-进水阀门、37-出水阀门;41-气凝胶毡隔热层、42-π-烯丙基镍化合物改性硅藻土吸附膜、43-不锈钢膜架、44-电热鼓风风机、45-重油排出口。32-Ultra-fine bubble generator, 33-Ultra-fine bubbles, 34-Stainless steel robotic arm, 35-Rotary ball bearing, 36-Water inlet valve, 37-Water outlet valve; 41-Aerogel felt insulation layer, 42-π -Allyl nickel compound modified diatomite adsorption membrane, 43-stainless steel membrane frame, 44-electric heating blower, 45-heavy oil discharge port.
图3是高压放电有机铑催化聚合反应槽的示意图。Figure 3 is a schematic diagram of a high voltage discharge organorhodium catalyzed polymerization reaction tank.
71-高压放电电极、72-二氯四羰基二铑多孔填料、73-槽体绝缘保护层、74-进水阀门、75-出水阀门、76-搅拌桨叶、77-颗粒物排放口。71- High voltage discharge electrode, 72- Dichlorotetracarbonyl dirhodium porous filler, 73- Tank insulation protection layer, 74- Water inlet valve, 75- Water outlet valve, 76- Stirring blade, 77- Particle discharge port.
具体实施方式Detailed ways
如图1所示的餐饮废水除油处理方法,含油的餐饮废水通过废水管线进入缓存池1,在此进行集中收集和初步稳定调节,缓存池1的出口通过废水管线连接粗格栅2,在此去除餐饮废水中的大直径固体物质,粗格栅2的出口通过废水管线连接微泡气浮油吸附装置3,微泡气浮油吸附装置3中的含π-烯丙基镍化合物改性硅藻土吸附膜42在完全吸附油后会被不锈钢机械臂34抓取,并被送入油催化重化解吸反应器4,油催化重化解吸反应器4中生成的重油从重油排出口45排出并被回收再利用,同时,微泡气浮油吸附装置3的出口通过废水管线连接pH值调节池5,在此将废水的pH值调节至近中性,pH值调节池6的出口通过废水管线连接一次沉淀池6,在此对废水进行沉淀澄清处理,一次沉淀池6的出口通过废水管线连接有机铑催化反应槽7,在此通过高压放电催化作用将污水中的剩余油脂聚合成不溶于水的颗粒物通过废水管线连接二次沉淀池8,在此将废水中的剩余不溶物质全部除去,二次沉淀池8的出口通过废水管线连接净水池9,净水池9的出口通过废水管线将处理后的净化出水外排;其中,微泡气浮油吸附装置3采用高强度玻璃钢材质,有效容积为155m3,其底部装有9支超微细气泡发生器32,能够产生直径小于50μm的超微细气泡33,装置的液面之上可容纳一张横向放置的π-烯丙基镍化合物改性硅藻土吸附膜42,该吸附膜面积为10.2m2,π-烯丙基镍化合物的含量为16.6g/m2,π-烯丙基镍化合物的纯度为95.2%,其左侧上部装有进水阀门36,右侧底部装有出水阀门37,该装置右侧壁因与高温的油催化重化解吸反应器4相连,故贴覆有气凝胶毡隔热层41,气凝胶毡隔热层41顶端装有不锈钢机械臂34及转珠轴承35;其中,油催化重化解吸反应器4采用高强度不锈钢材质,容积为330m3,其底部装有5部电热鼓风风机44,能够产生200~250℃的热空气,装置内部安装有一套不锈钢膜架43,膜架上可竖直放置5张待高温处理的π-烯丙基镍化合物改性硅藻土吸附膜42,其底部右侧设有重油排出口45;经过粗格栅2初步去除大粒径物质的含有油的餐饮废水通过微泡气浮油吸附装置3左侧上部的进水阀门36进入装置内部,9支超微细气泡发生器32开始工作,产生直径小于50μm的超微细气泡33,超微细气泡33会夹带废水中的油分子一同上浮,并使其被液面之上的含π-烯丙基镍化合物改性硅藻土吸附膜42吸附,完全吸附油的含π-烯丙基镍化合物改性硅藻土吸附膜42被不锈钢机械臂34抓取,并被竖直放置在油催化重化解吸反应器4中的不锈钢膜架43上,反应器底部的5部电热鼓风风机44开始工作,产生200~250℃的高温空气,在π-烯丙基镍化合物的催化下,油分子中的C-H键会发生短暂的断裂,并快速再结合为C-C键或C-H键,而C-H键会再次发生断裂,C-C键则因π-烯丙基镍化合物的催化作用有限而不会再发生断裂,因此可使碳链较短的油分子逐渐合成为碳链较长的重油分子。同时,重油分子会在高温下从含π-烯丙基镍化合物改性硅藻土吸附膜42中解吸,汇聚后从反应器底部右侧的重油排出口45排出,可被集中收集和再利用。高压放电有机铑催化聚合反应槽7的外层包裹有槽体绝缘保护层73,内部为碳化硅陶瓷结构,反应槽的有效容积为133m3,反应槽的右上部设有进水阀门74,左下部设有出水阀门75,槽体中央部分安装有二氯四羰基二铑多孔填料72,作为聚合反应催化剂,填料的孔径为5.2mm,比表面积为6.5cm2/g,填料层下部连接有颗粒物排放口77,左、右两侧壁板正中各安装有一支高压放电电极71,在反应槽底部左、右两侧各装有一支搅拌桨叶76,污水通过高压放电有机铑催化聚合反应槽7的进水阀门74进入反应槽内部,高压放电电极71每间隔0.1s进行一次高压放电,放电电压范围为8500~15000V,会在反应槽中产生一道横贯槽体左右的高压电弧,高压电弧所产生的高能量被废水中的油脂物质吸收,油脂分子中的C-H键受到能量激发处于不稳定状态,并在二氯四羰基二铑的表面催化作用下发生C-H键断裂并重组,最终生成大分子聚合颗粒物,以悬浮物的形式分散于水中,并通过反应槽右侧的出水阀门排出反应槽,进入三次沉淀池8。As shown in Fig. 1, the oil-containing catering wastewater enters the buffer pool 1 through the waste water pipeline, where centralized collection and preliminary stable adjustment are carried out. The outlet of the buffer pool 1 is connected to the
微泡气浮油吸附装置3,其有效容积为275m3,超微细气泡发生器32能够产生直径小于50μm的超微细气泡33,正常工作电压为20V,工作寿命一般为5000h。油催化重化解吸反应器4的容积为330m3,其中可容纳5张竖直放置的待高温处理的π-烯丙基镍化合物改性硅藻土吸附膜42,其电热鼓风风机44可产生200~250℃的热空气,工作电压为380V。π-烯丙基镍化合物改性硅藻土吸附膜42的面积为10.2m2,π-烯丙基镍化合物的含量为16.6g/m2,π-烯丙基镍化合物的纯度为95.2%。The microbubble air flotation oil adsorption device 3 has an effective volume of 275m 3 , the
通过本系统处理后的餐饮废水,其油去除效率可达99.8%。The oil removal efficiency of the catering wastewater treated by this system can reach 99.8%.
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Denomination of invention: A method for removing oil from wastewater Granted publication date: 20200721 Pledgee: Wuzhou Small and Micro Enterprises Financing Guarantee Co.,Ltd. Pledgor: Guangxi Huayuan Environmental Protection Technology Co.,Ltd. Registration number: Y2024980048220 |
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