CN109970146A - An oil-water separator for treating oily wastewater and its application in the treatment of crude oil electric desalination wastewater - Google Patents
An oil-water separator for treating oily wastewater and its application in the treatment of crude oil electric desalination wastewater Download PDFInfo
- Publication number
- CN109970146A CN109970146A CN201910291283.2A CN201910291283A CN109970146A CN 109970146 A CN109970146 A CN 109970146A CN 201910291283 A CN201910291283 A CN 201910291283A CN 109970146 A CN109970146 A CN 109970146A
- Authority
- CN
- China
- Prior art keywords
- oil
- water
- parts
- crude
- separating agent
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D17/00—Separation of liquids, not provided for elsewhere, e.g. by thermal diffusion
- B01D17/02—Separation of non-miscible liquids
- B01D17/04—Breaking emulsions
- B01D17/047—Breaking emulsions with separation aids
-
- 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
- C02F1/40—Devices for separating or removing fatty or oily substances or similar floating material
Landscapes
- Chemical & Material Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Thermal Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Physics & Mathematics (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
- Extraction Or Liquid Replacement (AREA)
Abstract
Description
技术领域technical field
本发明属废水处理领域,具体涉及一种处理含油废水的油水分离剂及其在原油电脱盐排水处理中的应用。The invention belongs to the field of wastewater treatment, in particular to an oil-water separation agent for treating oily wastewater and its application in the treatment of crude oil electric desalination drainage.
背景技术Background technique
深度电脱盐是处理原油所含盐份的基本方法,在高压电场和加热条件下,辅以破乳剂、超声波等手段,通过一次或多次注入如2-5%的水将原油中所含盐份洗入水中,之后进行油水分离,同时控制处理后原油的含水量和排水的含油量。通过深度电脱盐工艺,一般可将原油处理至含盐量低于3mg/L、含水量低于0.2%,所排废水的含油量可控制到150mg/L以内。操作正常时,电脱盐所排废水的含油量较低,送往污水处理装置可进行正常的隔油-浮选-生化工艺处理。Deep electrical desalination is the basic method to treat the salt contained in crude oil. Under the condition of high voltage electric field and heating, supplemented by demulsifier, ultrasonic wave and other means, the salt contained in crude oil is removed by one or more injections of water such as 2-5%. Parts are washed into water, and then oil-water separation is carried out, while controlling the water content of the treated crude oil and the oil content of the drainage. Through the deep electric desalination process, the crude oil can generally be treated to the extent that the salt content is lower than 3 mg/L and the water content is lower than 0.2%, and the oil content of the discharged wastewater can be controlled within 150 mg/L. When the operation is normal, the oil content of the wastewater discharged by electric desalination is low, and it can be sent to the sewage treatment device for normal oil separation-flotation-biochemical process treatment.
但由于原油条件的波动和复杂性、电脱盐操控调节手段的有限性和滞后,很多炼油厂的电脱盐装置经常有大量含油量远超150mg/L的废水排出,有时排水含油量甚至可达到10%左右,将此高含油废水掺混到电脱盐注水中返回电脱盐处理通常效果有限,或者会造成电脱盐后原油含盐含水不达标的问题。这种含油量较高的电脱盐废水,送往污水装置处理时会对隔油-浮选-生化工艺造成很大的冲击或者难于处理,经常造成废水堵库。另一方面,这种含油量较高的电脱盐废水在污水装置处理回收的废油,由于富集了其它废水中的复杂成分,通常不便直接作为常减压、催化裂化或焦化的原料利用,有的还难于输送。However, due to the fluctuation and complexity of crude oil conditions, and the limitation and lag of electric desalination control and adjustment methods, the electric desalination devices of many refineries often discharge a large amount of wastewater with oil content far exceeding 150 mg/L, and sometimes the oil content of the drainage can even reach 10. % or so, mixing this high oily wastewater into the electric desalination injection water and returning it to the electric desalination treatment usually has limited effect, or it will cause the problem that the salt and water content of the crude oil after electric desalination does not meet the standard. This kind of electrical desalination wastewater with high oil content will have a great impact on the oil separation-flotation-biochemical process when it is sent to the sewage plant for treatment, or it will be difficult to handle, and often causes the wastewater to block the reservoir. On the other hand, the waste oil recovered from the electrical desalination wastewater with high oil content is usually inconvenient to be used directly as raw materials for atmospheric and vacuum, catalytic cracking or coking due to the enrichment of complex components in other wastewaters. Some are also difficult to transport.
因而,有必要开发一种处理这类高含油废水的技术,尤其是通过简单地混入油水分离剂而实现高效油水分离的方法。Therefore, it is necessary to develop a technology for treating such high oily wastewater, especially a method for realizing high-efficiency oil-water separation by simply mixing an oil-water separating agent.
发明内容SUMMARY OF THE INVENTION
为解决上述技术问题,本发明提供一种处理含油废水的油水分离剂及其在原油电脱盐排水处理中的应用。In order to solve the above technical problems, the present invention provides an oil-water separation agent for treating oily wastewater and its application in the treatment of crude oil electric desalination wastewater.
本发明处理含油废水的油水分离剂,以质量份数计,包含乙二醇二叔丁醚100份、平均分子量800-1300的聚异丁烯30-80份、丙二醇二醋酸酯20-60份、α-吡咯烷酮5-20份。The oil-water separating agent for treating oily wastewater in the present invention comprises, in parts by mass, 100 parts of ethylene glycol di-tert-butyl ether, 30-80 parts of polyisobutylene with an average molecular weight of 800-1300, 20-60 parts of propylene glycol diacetate, α -5-20 parts of pyrrolidone.
其中,所述聚异丁烯为平均分子量800的聚异丁烯和/或平均分子量1300的聚异丁烯,优选将二者混合使用,二者质量份数比例为100:(30-60)时较好;所述丙二醇二醋酸酯为1,2-丙二醇二乙酸酯。Wherein, the polyisobutylene is polyisobutylene with an average molecular weight of 800 and/or polyisobutylene with an average molecular weight of 1300. Preferably, the two are used in combination, and the ratio of the two by mass is preferably 100: (30-60); the Propylene glycol diacetate is 1,2-propylene glycol diacetate.
其中,优选配比为乙二醇二叔丁醚100份、平均分子量800的聚异丁烯40份、平均分子量1300的聚异丁烯20份、丙二醇二醋酸酯40份、α-吡咯烷酮10份。Among them, the preferred proportions are 100 parts of ethylene glycol di-tert-butyl ether, 40 parts of polyisobutylene with an average molecular weight of 800, 20 parts of polyisobutylene with an average molecular weight of 1300, 40 parts of propylene glycol diacetate, and 10 parts of α-pyrrolidone.
本发明的油水分离剂,通过将乙二醇二叔丁醚、聚异丁烯、丙二醇二醋酸酯、α-吡咯烷酮在容器中混配搅匀即可制备,可略加热。所得油水分离剂为稳定的乳液。The oil-water separating agent of the present invention can be prepared by mixing ethylene glycol di-tert-butyl ether, polyisobutylene, propylene glycol diacetate and α-pyrrolidone in a container and stirring evenly, and can be slightly heated. The obtained oil-water separating agent is a stable emulsion.
本发明的油水分离剂,适用于处理水包油型的含油废水,所述的油包括矿物油和生物油脂,其中矿物油包括原油、机油,生物油脂包括植物油脂和动物油脂;其在废水中易于分散、溶解和扩散,对所述油或油脂的破乳、融合能力很强,处理后油或油脂容易形成连续的油相。对含油量低于20%的含油废水,可按1L含油废水添加50-2000mg的量加入,或者按含油量的0.5-5m%加入,在水温20-150℃条件下操作,可获得较高的油水分离效果;其中分离油相所得处理后水中的含油量可控制到150mg/L以下乃至100mg/L以下,所得回收油的含水量可低于0.3m%乃至低于0.2m%。分离油相所得水相可达到清澈透明的水平。对于低温含油废水,其中的油或油脂为凝固态或高粘度的,可以先加入本发明的油水分离剂,将废水分成水相和富油相,富油相加热到油或油脂的熔融状态或低粘度水平再进一步油水分离,最终分离所得水相中的含油量可控制到150mg/L以下乃至100mg/L以下,所得油相的含水量可低于0.3m%乃至低于0.2m%。The oil-water separator of the present invention is suitable for treating oil-in-water type oily wastewater, the oil includes mineral oil and biological oil, wherein the mineral oil includes crude oil and engine oil, and the biological oil includes vegetable oil and animal oil; It is easy to disperse, dissolve and diffuse, has strong demulsification and fusion ability to the oil or grease, and easily forms a continuous oil phase after treatment. For oily wastewater with oil content less than 20%, 50-2000mg of oily wastewater can be added to 1L of oily wastewater, or 0.5-5m% of oil content, operating under the condition of water temperature 20-150℃, can obtain higher oil content. Oil-water separation effect; the oil content in the treated water obtained by separating the oil phase can be controlled to below 150mg/L or even below 100mg/L, and the water content of the recovered oil can be lower than 0.3m% or even lower than 0.2m%. The water phase obtained by separating the oil phase can reach a clear and transparent level. For low-temperature oil-containing wastewater, where the oil or grease is in a solidified state or high viscosity, the oil-water separating agent of the present invention can be added first to separate the wastewater into an aqueous phase and an oil-rich phase, and the oil-rich phase is heated to the molten state of the oil or grease or The low viscosity level is further separated from oil and water, and the oil content in the water phase obtained by the final separation can be controlled to below 150mg/L or even below 100mg/L, and the water content of the obtained oil phase can be lower than 0.3m% or even lower than 0.2m%.
本发明的油水分离剂,也是一种高效反破乳剂,尤其适用于原油如高酸劣质原油、重劣质原油添加较多破乳剂条件下电脱盐装置所排含油废水的处理,可将原油电脱盐含油废水很好地分离,分离所得水相中的含油量可控制到150mg/L以下乃至100mg/L以下,所得油相的含水量可低于0.3m%乃至低于0.2m%、含盐量低于3mg/L。所述电脱盐装置所排含油废水中油滴表面所含乳化成分和/或破乳剂成分,往往反而使油滴在水中稳定和难于碰撞融合。所述高酸劣质原油中含较多环烷酸盐,破乳和脱盐困难,重劣质原油脱盐条件苛刻,电脱盐废水的含油量容易超标;含油废水的水包油体系稳定,难于通过常规的沉降、离心方法进行油水分离。The oil-water separating agent of the present invention is also a high-efficiency anti-demulsifier, and is especially suitable for the treatment of crude oil such as high-acid and inferior crude oil, heavy and inferior crude oil with more demulsifiers added to the treatment of oily wastewater discharged from an electric desalination device, and can electrically desalt crude oil. The oily wastewater is well separated, the oil content in the separated water phase can be controlled to below 150mg/L or even below 100mg/L, the water content of the obtained oil phase can be lower than 0.3m% or even lower than 0.2m%, the salt content Below 3mg/L. Emulsifying components and/or demulsifier components contained on the surface of oil droplets in the oil-containing wastewater discharged from the electrical desalination device often make the oil droplets stable in water and difficult to collide and fuse. The high-acid and inferior crude oil contains a lot of naphthenates, which makes it difficult to break demulsification and desalinate. Separation of oil and water by sedimentation and centrifugation.
本发明的油水分离剂用于原油电脱盐所排含油超标废水的处理,可直接利用如130-145℃的废水温度条件和利用废水缓冲储罐作为油水分离罐,基本不增加其它需要较多投资的设备或容器,还能对原油电脱盐装置的运行起到辅助和保障作用。优选采用两个或以上油水分离罐进行重力沉降分离油相和水相。对于积存的低温含原油废水,可以先加入本发明的油水分离剂,将废水分成水相和富油相,富油相加热到如80-150℃进行油水分离,最终分离所得水相中的含油量可控制到150mg/L以下乃至100mg/L以下,所得油相的含水量可低于0.3m%乃至低于0.2m%、含盐量低于3mg/L。The oil-water separation agent of the invention is used for the treatment of the waste water containing oil exceeding the standard discharged from the electric desalination of crude oil, and can directly use the waste water temperature conditions such as 130-145° C. and use the waste water buffer storage tank as the oil-water separation tank, and basically does not increase other needs more investment. The equipment or container can also play an auxiliary and guarantee role in the operation of the crude oil electric desalination unit. Preferably, two or more oil-water separation tanks are used to separate the oil phase and the water phase by gravity settling. For the accumulated low-temperature crude oil-containing wastewater, the oil-water separating agent of the present invention can be added first, and the wastewater is divided into an aqueous phase and an oil-rich phase, and the oil-rich phase is heated to 80-150 ° C for oil-water separation, and finally the oil-containing water in the obtained water phase is separated. The amount of oil can be controlled to below 150mg/L or even below 100mg/L, the water content of the obtained oil phase can be lower than 0.3m% or even lower than 0.2m%, and the salt content is lower than 3mg/L.
本发明的油水分离剂,可在注入废水后通过管道混合器即静态混合器,或机械搅拌等方式与废水混匀,再重力沉降分层或通过离心法进行油水分离,其中分离剂成分基本上进入油相,随回收油进一步利用,且基本不影响回收油的进一步加工。比如在处理原油电脱盐废水时所回收的油相,可泵入电脱盐后原油去常减压装置正常加工,在质量较差时也可送至催化裂化装置或焦化装置进行加工。本发明的油水分离剂不含无机物,没有灰分,通常仅占所回收原油量的0.5-5%,不影响常减压装置、催化裂化装置或焦化装置的操作和效果。The oil-water separating agent of the present invention can be mixed with the wastewater by a pipeline mixer, namely a static mixer, or mechanical stirring after being injected into the wastewater, and then gravity sedimentation and stratification or centrifugation can be used for oil-water separation, wherein the components of the separating agent are basically It enters the oil phase and is further utilized with the recovered oil, and does not substantially affect the further processing of the recovered oil. For example, the oil phase recovered from the treatment of crude oil electrical desalination wastewater can be pumped into the crude oil after electrical desalination to go to atmospheric and vacuum units for normal processing, and can also be sent to catalytic cracking units or coking units for processing when the quality is poor. The oil-water separating agent of the present invention contains no inorganic matter and no ash, usually only accounts for 0.5-5% of the recovered crude oil, and does not affect the operation and effect of atmospheric and vacuum units, catalytic cracking units or coking units.
具体实施方式Detailed ways
以下通过实施例、对比例对本发明进行具体说明,但不构成对本发明的限制。The present invention will be specifically described below through examples and comparative examples, but it does not constitute a limitation to the present invention.
实施例1-10、对比例1-9Embodiment 1-10, comparative example 1-9
按表1的配比,分别制备实施例1-10、对比例1-9的油水分离剂;混配方法是在500ml烧杯中先加入配料量的乙二醇二叔丁醚、丙二醇二醋酸酯、α-吡咯烷酮,电动搅拌中加入平均分子量800的聚异丁烯,搅匀后再加平均分子量1300的聚异丁烯,继续搅拌至均匀,之后分别装入试剂瓶保存。According to the proportions in Table 1, the oil-water separating agents of Examples 1-10 and Comparative Examples 1-9 were prepared respectively; the compounding method was to first add the ethylene glycol di-tert-butyl ether and propylene glycol diacetate of the ingredients in a 500ml beaker. , α-pyrrolidone, add polyisobutylene with an average molecular weight of 800 in the electric stirring, add polyisobutylene with an average molecular weight of 1300 after stirring, continue to stir until uniform, and then put them into reagent bottles for storage.
表1油水分离剂的配比,单位gTable 1 Proportion of oil-water separator, unit g
应用例1Application example 1
取某高酸劣质原油电脱盐装置所排含油废水,含油量8.1g/L,其在室温或90℃放置5h不分层,不形成连续油相;在1000ml烧杯中加入该含油废水1000ml,加热到80℃并加入实施例1的油水分离剂230μl约200mg(按含油量的2.5m%加入),搅匀后置于80℃保温箱中放置2h,记录放置1h、2h时的油水分离情况,检测放置2h后水相的含油量。Take the oily wastewater discharged from a high-acid and inferior crude oil electric desalination device, the oil content is 8.1g/L, and it will not stratify at room temperature or 90℃ for 5 hours, and will not form a continuous oil phase; add 1000ml of the oily wastewater into a 1000ml beaker, heat it to 80°C and add 230 μl of the oil-water separator of Example 1, about 200mg (according to 2.5m% of the oil content), stir well, place it in an 80°C incubator for 2 hours, and record the oil-water separation at 1 hour and 2 hours. Detect the oil content of the water phase after standing for 2 hours.
按相同的方法,依次在18个1000ml烧杯中加入该含油废水1000ml,分别加热到80℃并依次加入实施例2-10、对比例1-9的油水分离剂230μl 约200mg(按含油量的2.5m%加入,每个烧杯中只加一种油水分离剂),搅匀后置于80℃保温箱中放置2h,记录放置1h、2h时的油水分离情况,检测放置2h后水相的含油量。另在一个1000ml烧杯中加入该含油废水1000ml,加热到80℃直接置于80℃保温箱中放置2h作为空白对照。According to the same method, 1000ml of the oily waste water was added to 18 1000ml beakers in turn, heated to 80°C, and 230μl of the oil-water separation agent of Example 2-10 and Comparative Example 1-9 were added in turn, about 200mg (according to 2.5% of the oil content). Add m%, only one oil-water separator is added to each beaker), stir evenly, place it in an 80°C incubator for 2h, record the oil-water separation at 1h and 2h, and detect the oil content of the water phase after 2h . In addition, 1000ml of the oily wastewater was added to a 1000ml beaker, heated to 80°C and directly placed in an 80°C incubator for 2 hours as a blank control.
测试情况列于表2中,其中水相的含油量为距杯底20-30%液深处所取水样的含油量。The test conditions are listed in Table 2, where the oil content of the water phase is the oil content of the water sample taken from the depth of 20-30% of the liquid at the bottom of the cup.
将实施例1-10油水分离剂处理废水所收集的连续油相各取5ml,混匀,测含水量0.18m%,测含盐量低于3mg/L。Take 5ml of the continuous oil phase collected from the waste water treated by the oil-water separator in Examples 1-10, mix well, measure the water content to be 0.18m%, and measure the salt content to be lower than 3mg/L.
表2 各油水分离剂对含油量8.1g/L原油电脱盐废水的80℃处理效果情况,加入量200mg/LTable 2 The treatment effect of each oil-water separator on 8.1g/L crude oil electric desalination wastewater at 80℃, the addition amount is 200mg/L
。 .
应用例2Application example 2
取某高酸劣质原油电脱盐装置所排含油废水,含油量46g/L,其在室温或90℃密闭放置3h不分层,不形成连续油相;在1000ml烧杯中,按应用例1的方法,依次在19个1000ml烧杯中加入该含油废水1000ml,分别加热到90℃并依次加入实施例1-10、对比例1-9的油水分离剂570μl 约500mg(按含油量的1.1%加入,每个烧杯中只加一种油水分离剂),搅匀后置于90℃保温箱中放置2h,记录放置1h、2h时的油水分离情况,检测放置2h后水相的含油量。另在一个1000ml烧杯中加入该含油废水1000ml,加热到90℃直接置于90℃保温箱中放置2h作为空白对照。Take the oily waste water discharged from a high-acid and inferior crude oil electric desalination unit, with an oil content of 46g/L, which is kept in a closed place at room temperature or 90°C for 3 hours without stratification and without forming a continuous oil phase; in a 1000ml beaker, according to the method of application example 1 , add 1000ml of the oily waste water in 19 1000ml beakers in turn, heat to 90°C and add 570μl of oil-water separators of Examples 1-10 and 1-9 in turn, about 500mg (add at 1.1% of the oil content, each Add only one oil-water separating agent to each beaker), stir evenly, place it in a 90°C incubator for 2 hours, record the oil-water separation at 1 hour and 2 hours, and detect the oil content of the water phase after placing for 2 hours. In addition, 1000ml of the oily wastewater was added to a 1000ml beaker, heated to 90°C and directly placed in a 90°C incubator for 2h as a blank control.
测试情况列于表3中,其中水相的含油量为距杯底20-30%液深处所取水样的含油量。The test conditions are listed in Table 3, where the oil content of the water phase is the oil content of the water sample taken from the depth of 20-30% of the liquid from the bottom of the cup.
将实施例1-10油水分离剂处理废水所收集的连续油相各取10ml,混匀,测含水量0.23m%,含盐量低于3mg/L。Take 10ml of the continuous oil phase collected from the waste water treated by the oil-water separator in Examples 1-10, mix well, measure the water content of 0.23m%, and the salt content of less than 3mg/L.
表3 各油水分离剂对含油量46g/L原油电脱盐废水的90℃处理效果情况,加入量500mg/LTable 3 The treatment effect of each oil-water separator on 46g/L crude oil electric desalination wastewater at 90℃, the addition amount is 500mg/L
。 .
应用例3Application example 3
取某重劣质原油电脱盐装置所排含油废水,含油量150g/L,其在室温或90℃密闭放置3h不分层、不形成连续油相;在1000ml烧杯中加入该含油废水1000ml,加热到90℃并加入实施例1的油水分离剂1700μl 约1500mg,搅匀后置于90℃保温箱中放置3h,记录放置2h、3h时的油水分离情况,检测放置3h后水相的含油量。Take the oily wastewater discharged from a heavy and inferior crude oil electric desalination device, the oil content is 150g/L, it is sealed at room temperature or 90 ℃ for 3 hours without stratification and no continuous oil phase is formed; add 1000ml of the oily wastewater into a 1000ml beaker, and heat it to 90 ℃ and add 1700 μl of oil-water separator of Example 1 about 1500 mg, stir evenly, place it in a 90 ℃ incubator for 3 hours, record the oil-water separation at 2 hours and 3 hours, and detect the oil content of the water phase after placing for 3 hours.
按相同的方法,依次在18个1000ml烧杯中加入该含油废水1000ml,分别加热到90℃并依次加入实施例2-10、对比例1-9的油水分离剂1700μl 约1500mg(按含油量的1.0%加入,每个烧杯中只加一种油水分离剂),搅匀后置于90℃保温箱中放置3h,记录放置2h、3h时的油水分离情况,检测放置3h后水相的含油量。According to the same method, 1000ml of the oily waste water was added to 18 1000ml beakers in turn, heated to 90°C, and 1700μl of oil-water separation agent of Example 2-10 and Comparative Example 1-9 were added in sequence. About 1500mg (according to 1.0 % addition, only one oil-water separator is added to each beaker), stir evenly and place in a 90°C incubator for 3 hours, record the oil-water separation at 2 hours and 3 hours, and detect the oil content of the water phase after being placed for 3 hours.
测试情况列于表4中,其中水相的含油量为距杯底20-30%液深处所取水样的含油量。另在一个1000ml烧杯中加入该含油废水1000ml,加热到90℃直接置于90℃保温箱中放置3h作为空白对照。The test conditions are listed in Table 4, where the oil content of the water phase is the oil content of the water sample taken from the depth of 20-30% of the liquid at the bottom of the cup. In addition, 1000ml of the oily wastewater was added to a 1000ml beaker, heated to 90°C and directly placed in a 90°C incubator for 3h as a blank control.
将实施例1-10油水分离剂处理废水所收集的连续油相各取50ml测含水量都低于0.3m%,测含盐量都低于3mg/L。Take 50ml of the continuous oil phase collected from the waste water treated by the oil-water separating agent in Examples 1-10, and measure the water content below 0.3m%, and measure the salt content below 3mg/L.
表4 各油水分离剂对含油量150g/L原油电脱盐废水的90℃处理效果情况,加入量1500mg/LTable 4 The treatment effect of each oil-water separator on 150g/L crude oil electric desalination wastewater at 90℃, the addition amount is 1500mg/L
。 .
应用例4Application example 4
在六个1000ml烧杯中分别加入应用例1-3所用三种含油废水各1000ml,每种含油废水各二杯,分别加热到80℃并加入实施例5的油水分离剂,搅匀后置于100L耐压反应釜的杯架中,油水分离剂加入量如表5所列;另在三个1000ml烧杯中分别加入该三种含油废水各1000ml,加热到80℃直接置于耐压反应釜的杯架中作为空白对照。所述九个烧杯外形尺寸相同,在耐压反应釜杯架中的烧杯底面处于相同的水平高度。放完烧杯后反应釜内注入80℃热水至与烧杯内液面齐平,关闭反应釜封盖,充高纯氮气至0.6MPa再泄压,重复充放高纯氮气六次置换空气后再充高纯氮气至0.6MPa,之后送电将反应釜内热水升温至140℃,恒温1h后断电开冷却水将反应釜内热水降温至80℃后泄压,打开反应釜封盖,取出九个烧杯。操作过程中,从第一个烧杯中废水开始加油水分离剂到反应釜内热水升温到140℃的时间为0.4h,从开冷却水到热水降温至80℃、泄压、开封盖、九个烧杯全部取出的时间为0.3h。In six 1000ml beakers, add 1000ml of each of the three types of oily waste water used in Application Examples 1-3, and two cups of each oily waste water, respectively, heat to 80°C and add the oil-water separator of Example 5, stir evenly and place in 100L In the cup holder of the pressure-resistant reaction kettle, the amount of oil-water separating agent added is listed in Table 5; in addition, 1000 ml of each of the three types of oily wastewater was added to the three 1000-ml beakers, heated to 80 °C, and placed directly in the cup of the pressure-resistant reaction kettle. rack as a blank control. The outer dimensions of the nine beakers are the same, and the bottom surfaces of the beakers in the pressure-resistant reactor cup holder are at the same level. After placing the beaker, inject 80°C hot water into the reaction kettle until it is flush with the liquid level in the beaker, close the lid of the reaction kettle, fill with high-purity nitrogen to 0.6MPa, then release the pressure, and repeat the charge and discharge of high-purity nitrogen six times to replace the air. Charge high-purity nitrogen to 0.6MPa, then power on to heat up the hot water in the reactor to 140°C, keep the temperature for 1 hour, turn off the power, turn on the cooling water, cool the hot water in the reactor to 80°C, release the pressure, open the lid of the reactor, Remove nine beakers. During the operation, the time from the waste water in the first beaker adding the water separating agent to the heating of the hot water in the reactor to 140°C is 0.4h, from the opening of the cooling water to the cooling of the hot water to 80°C, pressure relief, opening the lid, The time for all the nine beakers to be taken out was 0.3h.
检查各烧杯内的油水分离情况,并对各油相、水相进行检测,结果列于表5。Check the oil-water separation in each beaker, and test each oil phase and water phase. The results are listed in Table 5.
表5 各油水分离剂对含油量8.1g/L、46g/L、150g/L原油电脱盐废水的140℃处理效果情况Table 5 Treatment effect of each oil-water separator on 8.1g/L, 46g/L and 150g/L crude oil electric desalination wastewater at 140℃
。 .
应用例5Application example 5
在六个1000ml烧杯中分别加入应用例1-3所用三种室温含油废水各1000ml,每种含油废水各二杯,不加热,各加入实施例5的油水分离剂,搅匀,油水分离剂加入量如表6所列;另在三个1000ml烧杯中分别加入该三种含油废水各1000ml,不加热、不加油水分离剂作为空白对照。室温放置1h后检查各烧杯内的油水分离情况,其中未加油水分离剂的无可见变化;加入油水分离剂的上层形成富油相,富油相以下形成透明水相,将各杯中的富油相取出,分别置于小容量烧杯中加热到90℃并置于90℃保温箱放置1h后形成连续油相,油相上无沫,油相水相界面清晰,水相透明,分别对各油相、室温水相及90℃水相的合并水相进行检测,结果列于表6。In six 1000ml beakers, add 1000ml of each of the three kinds of oily wastewater at room temperature used in Application Examples 1-3, and two cups of each oily wastewater, without heating, add the oil-water separator of Example 5, stir well, and add the oil-water separator. The amount is listed in Table 6; in addition, 1000ml of each of the three types of oily waste water was added to three 1000ml beakers, respectively, without heating, without adding oil, and the water separator was used as a blank control. After standing at room temperature for 1 hour, check the oil-water separation in each beaker, and there is no visible change in the water-separating agent without adding oil; the oil-rich phase is formed in the upper layer of the oil-water separation agent, and the transparent water phase is formed below the oil-rich phase. The oil phase was taken out, placed in a small-capacity beaker and heated to 90°C and placed in a 90°C incubator for 1 hour to form a continuous oil phase. There was no foam on the oil phase, the oil-water phase interface was clear, and the water phase was transparent. The combined water phase of the oil phase, the room temperature water phase and the 90° C. water phase was tested, and the results are listed in Table 6.
表6 各油水分离剂对含油量150g/L原油电脱盐废水的常温+90℃处理效果情况Table 6 The treatment effect of each oil-water separator on the crude oil electric desalination wastewater with an oil content of 150g/L at room temperature +90℃
。 .
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910291283.2A CN109970146B (en) | 2019-04-11 | 2019-04-11 | An oil-water separator for treating oily wastewater and its application in the treatment of crude oil electric desalination wastewater |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910291283.2A CN109970146B (en) | 2019-04-11 | 2019-04-11 | An oil-water separator for treating oily wastewater and its application in the treatment of crude oil electric desalination wastewater |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN109970146A true CN109970146A (en) | 2019-07-05 |
| CN109970146B CN109970146B (en) | 2021-07-30 |
Family
ID=67084245
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201910291283.2A Active CN109970146B (en) | 2019-04-11 | 2019-04-11 | An oil-water separator for treating oily wastewater and its application in the treatment of crude oil electric desalination wastewater |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN109970146B (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110467941A (en) * | 2019-08-20 | 2019-11-19 | 山东京博石油化工有限公司 | A kind of processing method and system of crude oil electric desalting draining |
| WO2024232930A1 (en) * | 2023-05-08 | 2024-11-14 | Halliburton Energy Services, Inc. | Supramolecular host guest product concentrators for production fluids |
| US12274956B2 (en) | 2021-11-08 | 2025-04-15 | Halliburton Energy Services, Inc. | Supramolecular host guest product concentrators for production fluids |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP1953207A1 (en) * | 2005-02-09 | 2008-08-06 | Basf Se | Use of hyperbranched polyesters as demulsifiers for cracking crude oil emulsions |
| WO2009100012A1 (en) * | 2008-02-07 | 2009-08-13 | Amcol International Corporation | Underwater processing of fluid streams |
| CN102140365A (en) * | 2010-01-28 | 2011-08-03 | 中国石油化工集团公司 | Acid-containing crude oil demulsifying agent and preparation method thereof |
| CN102627380A (en) * | 2012-04-19 | 2012-08-08 | 重庆融极环保工程有限公司 | Efficient acidic oil sludge decomposing agent, and preparation method and application thereof |
| CN103951009A (en) * | 2014-02-17 | 2014-07-30 | 宜兴汉光高新石化有限公司 | Coking demulsifier and preparation method thereof |
-
2019
- 2019-04-11 CN CN201910291283.2A patent/CN109970146B/en active Active
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP1953207A1 (en) * | 2005-02-09 | 2008-08-06 | Basf Se | Use of hyperbranched polyesters as demulsifiers for cracking crude oil emulsions |
| WO2009100012A1 (en) * | 2008-02-07 | 2009-08-13 | Amcol International Corporation | Underwater processing of fluid streams |
| CN102140365A (en) * | 2010-01-28 | 2011-08-03 | 中国石油化工集团公司 | Acid-containing crude oil demulsifying agent and preparation method thereof |
| CN102627380A (en) * | 2012-04-19 | 2012-08-08 | 重庆融极环保工程有限公司 | Efficient acidic oil sludge decomposing agent, and preparation method and application thereof |
| CN103951009A (en) * | 2014-02-17 | 2014-07-30 | 宜兴汉光高新石化有限公司 | Coking demulsifier and preparation method thereof |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110467941A (en) * | 2019-08-20 | 2019-11-19 | 山东京博石油化工有限公司 | A kind of processing method and system of crude oil electric desalting draining |
| US12274956B2 (en) | 2021-11-08 | 2025-04-15 | Halliburton Energy Services, Inc. | Supramolecular host guest product concentrators for production fluids |
| WO2024232930A1 (en) * | 2023-05-08 | 2024-11-14 | Halliburton Energy Services, Inc. | Supramolecular host guest product concentrators for production fluids |
Also Published As
| Publication number | Publication date |
|---|---|
| CN109970146B (en) | 2021-07-30 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US6056882A (en) | Process of breaking a sludge emulsion with a ball mill followed by separation | |
| CN109970146A (en) | An oil-water separator for treating oily wastewater and its application in the treatment of crude oil electric desalination wastewater | |
| Duan et al. | Solid separation from the heavy oil sludge produced from Liaohe Oilfield | |
| CN103154202A (en) | Improvement of desalination equipment in refinery | |
| EP2470620A1 (en) | Systems, methods and compositions for the separation and recovery of hydrocarbons from particulate matter | |
| CN101121898A (en) | A rapid demulsification method | |
| CN102257104A (en) | Demulsifying of hydrocarbon feeds | |
| AU2013358575A1 (en) | Treatment of crude oil, sludges and emulsions | |
| US8197667B2 (en) | Method to recover crude oil from sludge or emulsion | |
| KR102586688B1 (en) | Use of peroxy acids/hydrogen peroxide to remove metal components from petroleum and hydrocarbon streams for downstream applications | |
| NO20161542A1 (en) | PROCESS FOR REMOVAL OF WATER (BOTH BOUND and UNBOUND) FROM PETROLEUM SLUDGES AND EMULSIONS WITH A VIEW TO RETRIEVE ORIGINAL HYDROCARBONS PRESENT THEREIN | |
| JP2008513551A (en) | Neutralization of high total acid number (TAN) crude oil emulsions | |
| Tang et al. | A low-temperature ionic liquid demulsifier derived from recycled PET waste plastics | |
| CA2761201C (en) | Analogue ionic liquids for the separation and recovery of hydrocarbons from particulate matter | |
| CN104496132B (en) | Oil field oil sludge New Process for Treatment | |
| Qu et al. | Synthesis and demulsification mechanism of an ionic liquid with four hydrophobic branches and four ionic centers | |
| KR20170022602A (en) | Method for removing metals from hydrocarbon oil | |
| EP1165723A1 (en) | Metal phase transfer additive composition and method | |
| JP2005314500A (en) | Method for producing gasoline base material with high octane number | |
| CN1235843C (en) | Method for eliminating and reclaiming acid component from oil products | |
| CN115785997B (en) | A method for producing marine fuel oil or oil blending materials by using waste oil from cabin cleaning | |
| US11752447B2 (en) | Methods for separating water and contaminants from valuable or harmful process liquids | |
| RU2491323C1 (en) | De-emulsifier for destruction of water-oil emulsions | |
| CN107601619A (en) | A kind of preparation technology of water process demulsifier | |
| CN110240227B (en) | Deoiling treatment process for crude oil electric desalting and draining |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| TR01 | Transfer of patent right | ||
| TR01 | Transfer of patent right |
Effective date of registration: 20250529 Address after: 253500 Shandong Province, Dezhou City, Lingcheng District, Ande Street, middle section of Beihuan Road, north side of the road (within the premises of Dezhou Gongjie Construction Engineering Co., Ltd.) Patentee after: Zhongmin New Energy Technology (Shandong) Co.,Ltd. Country or region after: China Address before: 255400 Shandong Province, Zibo City, Linqi District, No. 818 Jia, Linqi Avenue, West Building of Zhongrui Mansion, Room 810 Patentee before: SHANDONG JUXING NEW MATERIAL TECHNOLOGY Co.,Ltd. Country or region before: China |