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CN106565007A - Ternary compound flooding produced water deoiling agent and preparation method thereof - Google Patents

Ternary compound flooding produced water deoiling agent and preparation method thereof Download PDF

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Publication number
CN106565007A
CN106565007A CN201610983357.5A CN201610983357A CN106565007A CN 106565007 A CN106565007 A CN 106565007A CN 201610983357 A CN201610983357 A CN 201610983357A CN 106565007 A CN106565007 A CN 106565007A
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degreaser
formic acid
formaldehyde
preparation
ternary composite
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CN106565007B (en
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刘亭亭
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Henan Zhengjia Green Energy Co ltd
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Yantai Smithde Electromechanical Equipment Manufacturing Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/68Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water
    • C02F1/682Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water by addition of chemical compounds for dispersing an oily layer on water
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/547Tensides
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07DHETEROCYCLIC COMPOUNDS
    • C07D213/00Heterocyclic compounds containing six-membered rings, not condensed with other rings, with one nitrogen atom as the only ring hetero atom and three or more double bonds between ring members or between ring members and non-ring members
    • C07D213/02Heterocyclic compounds containing six-membered rings, not condensed with other rings, with one nitrogen atom as the only ring hetero atom and three or more double bonds between ring members or between ring members and non-ring members having three double bonds between ring members or between ring members and non-ring members
    • C07D213/04Heterocyclic compounds containing six-membered rings, not condensed with other rings, with one nitrogen atom as the only ring hetero atom and three or more double bonds between ring members or between ring members and non-ring members having three double bonds between ring members or between ring members and non-ring members having no bond between the ring nitrogen atom and a non-ring member or having only hydrogen or carbon atoms directly attached to the ring nitrogen atom
    • C07D213/60Heterocyclic compounds containing six-membered rings, not condensed with other rings, with one nitrogen atom as the only ring hetero atom and three or more double bonds between ring members or between ring members and non-ring members having three double bonds between ring members or between ring members and non-ring members having no bond between the ring nitrogen atom and a non-ring member or having only hydrogen or carbon atoms directly attached to the ring nitrogen atom with hetero atoms or with carbon atoms having three bonds to hetero atoms with at the most one bond to halogen, e.g. ester or nitrile radicals, directly attached to ring carbon atoms
    • C07D213/72Nitrogen atoms
    • C07D213/74Amino or imino radicals substituted by hydrocarbon or substituted hydrocarbon radicals
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K23/00Use of substances as emulsifying, wetting, dispersing, or foam-producing agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/10Nature of the water, waste water, sewage or sludge to be treated from quarries or from mining activities

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Health & Medical Sciences (AREA)
  • Medicinal Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Pyridine Compounds (AREA)

Abstract

The invention belongs to the technical field of oil field sewage treatment, and in particular, relates to a ternary compound flooding produced water deoiling agent; the deoiling agent is a zwitterionic deoiling agent prepared by the steps of carrying out a reaction of 2,5-pyridine diamine with formaldehyde and formic acid to generate an intermediate and then carrying out a reaction of the intermediate with sodium laurate chloride, wherein the molar ratio of 2,5-pyridine diamine to formaldehyde to formic acid to sodium laurate chloride is 1 to (2.5-6) to (2.5-5.5) to (0.8-2.5), preferably (1-3) to 3 to 3 to 1.5. The deoiling agent has the advantages of simple preparation, strong adaptability, low cost, strong salt tolerance and good deoiling effect, the salt tolerance reaches 2.3*10<4> mg/L, and the deoiling rate of ternary compound flooding produced water reaches more than or equal to 97%. Recovered oil produced by separation does not affect subsequent dehydration of crude oil, so the deoiling agent can be widely applied in the deoiling process of the ternary compound flooding produced water.

Description

A kind of degreaser of ternary composite flooding water extraction and preparation method thereof
Technical field
The present invention relates to a kind of degreaser for disposing polluted water in oil, and in particular to a kind of ternary composite flooding water extraction Degreaser and preparation method thereof.
Background technology
In recent years China accelerates to have promoted tertiary oil recovery production technique, to maintain and improve crude output.Alkali-surface activity Agent-polymer ternary combination flooding is grown up on the basis of surfactant flooding, caustic flooding and polymer displacement of reservoir oil method A chemical displacement of reservoir oil technology.Relevant research shows that ternary composite driving can significantly improve recovery ratio, front with wide application Scape.
But due to ternary combination flooding extraction sewage water quality it is complicated, the alkali containing a large amount of residuals, surfactant and poly- Compound (such as polyacrylamide PAM), the viscosity for causing sewage becomes big, and sewage oil bead diameter diminishes, and causes sewage emulsifying serious, increases The difficulty of Produced Liquid breakdown of emulsion and purification is added.Meanwhile, the process side of " two grades of sedimentation+cascade filtrations " that oil field generally adopts now Formula can not meet environmental requirement, occur in that equipment disposal ability is reduced, the sedimentation time is long, effluent quality is unqualified etc. and ask Topic.
At present frequently with measure mainly have:1. physical means polymer-contained sewage.At present electrochemical method is main Physical means processing method, wherein electric flocculation technique are more ripe because of its study mechanism, and electrode material is easily obtained, small investment, The features such as being easy to automatization two is gradually widely used in sewage disposal;2. chemical method polymer-contained sewage.Such technology is first Breakdown of emulsion process is first carried out, then the medicament such as further preferably suitable degreaser carries out purification technique.At present conventional medicament mainly has Quaternary, polymer modified clays type, polyacrylamide organic polymer type and modified starch etc., and achieve preferably Flocculation, oil removing action effect.
Patent ZL201410455664.7 " a kind of degreaser for oil field binary combination flooding output sewage " employs third Alkene acyloxyethyl dimethyl amine, alkyl chloride, acrylamide, N, N '-methylene-bisacrylamide, Ammonium persulfate. and sodium sulfite are anti- Should form, the degreaser has consumption few, low cost, the characteristics of oil removal rate is high, oil removal efficiency is high, prepare simple, cost is low Feature, but the degreaser belongs to reverse demulsifier, it is poor for the demulsification of emulsion oil-in-water, meanwhile, the degreaser It is not suitable for the oil removal treatment of the ternary combination flooding extraction sewage of complicated component.
The content of the invention
The present invention provides a kind of degreaser and its system of ternary composite flooding water extraction for the deficiency of currently available technology Preparation Method, the degreaser has process is simple, a with low cost, strong adaptability, and strong with anti-salt property and deoiling effect is good Feature, salt tolerant reaches 2.3 × 104Mg/L, the oil removal rate of ternary composite flooding water extraction is up to more than 97%.
It is an object of the invention to provide a kind of degreaser of ternary composite flooding water extraction, described degreaser is by 2,5- Pyridine diamidogen generates intermediate with formaldehyde, formic acid reaction, then generates amphoteric ion type degreaser with the reaction of chlorine sodium laurate, its Molecular formula is as follows:
The mol ratio of described 2,5- pyridine diamidogen, formaldehyde, formic acid and chlorine sodium laurate is 1: 2.5~6: 2.5~5.5: 0.8~2.5, preferably 1: 3: 3: 1.5.
Further object is that providing a kind of preparation method of the degreaser of ternary composite flooding water extraction, this is removed The preparation method of oil preparation specifically includes following steps:
(1) 2, the 5- pyridines diamidogen and solvent of above-mentioned mol ratio are added in there-necked flask, are loaded onto with water knockout drum Reflux condensing tube, stir speed (S.S.) is 200~300rpm, is warming up to 30~40 DEG C, pours the formic acid of above-mentioned mol ratio into constant pressure drop In liquid funnel, rate of titration is controlled, formic acid is dripped off in 20~30min, after formic acid is dripped off, it is 500 to adjust stir speed (S.S.) ~600rpm, is warming up to 50~55 DEG C, and the formaldehyde of aforementioned proportion is poured in constant pressure funnel, controls rate of titration, makes first Aldehyde is dripped off in 40~60min, after formol titration is finished, is warming up to 80~85 DEG C, and Temperature fall is obtained after 10~24h of reaction Solution A;
(2) it is 12~13 to pH value with the above-mentioned solution A of potassium hydroxide alkalization that mass concentration is 20%, uses n-hexane extraction Upper strata liquid, removes solvent, obtains crude product B;
(3) above-mentioned crude product B is poured in four-hole boiling flask, adds dehydrated alcohol, load onto condensing tube, be in stir speed (S.S.) It is under 100~300rpm, the chlorine sodium laurate of aforementioned proportion is soluble in water, then it is slowly added in four-hole boiling flask with funnel, 70~75 DEG C are then heated to, stir speed (S.S.) is 350~400rpm, is alkalized to pH value with the sodium bicarbonate that mass concentration is 25% For 8~9, Temperature fall obtains solution C after 10~14h of reaction;
(4) pH to 2~3 of solution C is adjusted with the HCl of 6mol/L, stands 24~36h, then rotation is steamed under vacuum environment Second alcohol and water is sent, is vacuum dried;Finally washed with ether 3~5 times, obtain the degreaser of the final product present invention.
Described solvent is Hexalin or benzene, and consumption is 10~25 times of 2,5- pyridine diamidogen quality;Described normal hexane Consumption be 2~3 times of 2,5- pyridine diamidogen quality;The consumption of described dehydrated alcohol for 2,5- pyridine diamidogen quality 5~ 10 times;The consumption of described ether is 0.5~1 times of 2,5- pyridine diamidogen quality.
Described reaction equation is as follows:
A kind of degreaser of ternary composite flooding water extraction, it uses technical process as follows:
According to oil-containing situation in ternary compound oil drive output water, the degreaser of the present invention is added in sewage, realized broken Breast and oil-water separation, after reclaiming petroleum substance, are further processed for subsequent technique.The concrete addition of degreaser is as follows:
(1) during oil-containing α >=500mg/L, it is 50~150mg/L to add degreaser to make the mass concentration of degreaser in sewage;
During (2) 500 > oil-containings α >=300mg/L, add degreaser make degreaser in sewage mass concentration be 30~ 50mg/L;
During (3) 300 > oil-containings α >=100mg/L, add degreaser make degreaser in sewage mass concentration be 10~ 30mg/L;
(4) during oil-containing α < 100mg/L, it is 0.1~10mg/L to add degreaser to make the mass concentration of degreaser in sewage.
The degreaser of the ternary composite flooding water extraction that the present invention is provided, it belongs to glycine betaine (amphion) type surface activity Agent, the molecule has cation and anion amphion group, and its cation can attract each other with anion, is easily formed More firm skin covering of the surface, after greasy surfaces are adsorbed onto, can shell in the surfactant in ternary combination flooding extraction sewage From going down, with stronger interfacial activity.Heterocyclic group containing N in the molecule and the hydrophobic group being attached thereto have with greasy dirt There is analog structure, it is easy to greasy dirt absorption, promote the degreaser flocculation dirty with Oil in Sewage Water;Due to both having on molecule Anion and cation, extraneous ion be difficult to it is close with degreaser, so its anti-salt property is stronger;Additionally, going back on molecule Can tangle with polyacrylamide amine molecule so that extensibility of the polyacrylamide in sewage is deteriorated, so as to reduce dirt The viscosity of water, accelerates the speed of oil-water separation.
The present invention has the advantage that compared with prior art and beneficial effect:
(1) extensively, synthesis technique is simple, and strong adaptability can meet environmental conservation for the raw material sources of degreaser of the invention With the needs of oil field development;
(2) degreaser of the invention can reduce the viscosity of sewage, and anti-salt property is good, and salt tolerant is up to 2.3 × 104Mg/L and Inorganic flocculation composition is not contained;
(3) the characteristics of degreaser of the invention has oil removal efficiency high, the oil removal rate of ternary composite flooding water extraction is up to 97% More than, more existing medicament improves more than 50%, meets the requirement of the oil removing pretreatment of ternary composite flooding water extraction.
Specific embodiment
With reference to specific embodiment, and the present invention is described in further detail with reference to data.It should be understood that these embodiments It is of the invention solely for the purpose of illustration, rather than the scope of the present invention is limited by any way.
Embodiment 1:Degreaser H1And preparation method thereof
(1) degreaser H1Composition, component and molecular formula it is as follows:
Degreaser H1Intermediate is generated by 2,5- pyridines diamidogen and formaldehyde, formic acid reaction, is then reacted with chlorine sodium laurate Amphoteric ion type degreaser is generated, wherein, the mol ratio of 2,5- pyridine diamidogen, formaldehyde, formic acid and chlorine sodium laurate is 1: 2.5: 2.5∶0.8.Degreaser H1Molecular formula it is as follows:
(2) degreaser H1Preparation method it is as follows:
1. 2, the 5- pyridines diamidogen and 1091.5g Hexalin of 1mol are added in there-necked flask, are loaded onto with water knockout drum Reflux condensing tube, stir speed (S.S.) is 230rpm, is warming up to 30 DEG C, and the formic acid of 2.5mol is poured in constant pressure funnel, control Rate of titration processed, makes formic acid drip off in 20min, and after formic acid is dripped off, regulation stir speed (S.S.) is 530rpm, is warming up to 50 DEG C, The formaldehyde of 2.5mol is poured in constant pressure funnel, rate of titration is controlled, formaldehyde is dripped off in 40min, treat formol titration After finishing, 82 DEG C are warming up to, Temperature fall obtains solution A after reaction 10h;
2. it is 12 to pH value with the above-mentioned solution A of potassium hydroxide alkalization that mass concentration is 20%, uses n-hexane extraction upper strata Liquid, normal hexane consumption is 218.3g, removes solvent, obtains crude product B;
3. above-mentioned crude product B is poured in four-hole boiling flask, adds 545.8g dehydrated alcohol, load onto condensing tube, in stirring Speed be 100rpm under, the chlorine sodium laurate of 0.8mol is soluble in water, be then slowly added in four-hole boiling flask with funnel, so After be warming up to 72 DEG C, stir speed (S.S.) is 350rpm, with the sodium bicarbonate that mass concentration is 25% alkalize to pH value be 8, react 10h Afterwards Temperature fall obtains solution C;
4. the pH to 2 of solution C is adjusted with the HCl of 6mol/L, stands 24h, then rotation evaporates ethanol under vacuum environment And water, vacuum drying;Finally washed with ether 3 times, the consumption of ether is 54.6g, obtains the degreaser of the final product present invention H1
Embodiment 2:Degreaser H2And preparation method thereof
(1) degreaser H2Composition, component and molecular formula it is as follows:
Degreaser H2Intermediate is generated by 2,5- pyridines diamidogen and formaldehyde, formic acid reaction, is then reacted with chlorine sodium laurate Amphoteric ion type degreaser is generated, wherein, the mol ratio of 2,5- pyridine diamidogen, formaldehyde, formic acid and chlorine sodium laurate is 1: 3: 3: 1.5.Degreaser H1Molecular formula it is as follows:
(2) degreaser H2Preparation method it is as follows:
1. 2, the 5- pyridines diamidogen and 1637.3g benzene of 1mol are added in there-necked flask, load onto returning with water knockout drum Stream condensing tube, stir speed (S.S.) is 200rpm, is warming up to 32 DEG C, and the formic acid of 3mol is poured in constant pressure funnel, control titration Speed, makes formic acid drip off in 28min, and after formic acid is dripped off, regulation stir speed (S.S.) is 500rpm, 52 DEG C is warming up to, by 3mol Formaldehyde pour in constant pressure funnel, control rate of titration, formaldehyde is dripped off in 50min, after formol titration is finished, rise To 80 DEG C, Temperature fall obtains solution A to temperature after reaction 16h;
2. it is 12 to pH value with the above-mentioned solution A of potassium hydroxide alkalization that mass concentration is 20%, uses n-hexane extraction upper strata Liquid, normal hexane consumption is 265.2g, removes solvent, obtains crude product B;
3. above-mentioned crude product B is poured in four-hole boiling flask, adds 756.3g dehydrated alcohol, load onto condensing tube, in stirring Speed be 150rpm under, the chlorine sodium laurate of 1.5mol is soluble in water, be then slowly added in four-hole boiling flask with funnel, so After be warming up to 70 DEG C, stir speed (S.S.) is 360rpm, with the sodium bicarbonate that mass concentration is 25% alkalize to pH value be 9, react 12h Afterwards Temperature fall obtains solution C;
4. the pH to 2 of solution C is adjusted with the HCl of 6mol/L, stands 28h, then rotation evaporates ethanol under vacuum environment And water, vacuum drying;Finally washed with ether 3 times, the consumption of ether is 64.3g, obtains the degreaser of the final product present invention H2
Embodiment 3:Degreaser H3And preparation method thereof
(1) degreaser H3Composition, component and molecular formula it is as follows:
Degreaser H3Intermediate is generated by 2,5- pyridines diamidogen and formaldehyde, formic acid reaction, is then reacted with chlorine sodium laurate Amphoteric ion type degreaser is generated, wherein, the mol ratio of 2,5- pyridine diamidogen, formaldehyde, formic acid and chlorine sodium laurate is 1: 5: 4: 2.Degreaser H3Molecular formula it is as follows:
(2) degreaser H3Preparation method it is as follows:
1. 2, the 5- pyridines diamidogen and 2183g Hexalin of 1mol are added in there-necked flask, are loaded onto with water knockout drum Reflux condensing tube, stir speed (S.S.) is 270rpm, is warming up to 35 DEG C, and the formic acid of 4mol is poured in constant pressure funnel, control drop Constant speed degree, makes formic acid drip off in 24min, and after formic acid is dripped off, regulation stir speed (S.S.) is 580rpm, is warming up to 53 DEG C DEG C, will The formaldehyde of 5mol is poured in constant pressure funnel, controls rate of titration, formaldehyde is dripped off in 45min, treats that formol titration is finished Afterwards, 84 DEG C are warming up to, Temperature fall obtains solution A after reaction 20h;
2. it is 13 to pH value with the above-mentioned solution A of potassium hydroxide alkalization that mass concentration is 20%, uses n-hexane extraction upper strata Liquid, normal hexane consumption is 301.5g, removes solvent, obtains crude product B;
3. above-mentioned crude product B is poured in four-hole boiling flask, adds 865.2g dehydrated alcohol, load onto condensing tube, in stirring Speed be 250rpm under, the chlorine sodium laurate of 2.0mol is soluble in water, be then slowly added in four-hole boiling flask with funnel, so After be warming up to 73 DEG C, stir speed (S.S.) is 380rpm, with the sodium bicarbonate that mass concentration is 25% alkalize to pH value be 8, react 13h Afterwards Temperature fall obtains solution C;
4. the pH to 3 of solution C is adjusted with the HCl of 6mol/L, stands 32h, then rotation evaporates ethanol under vacuum environment And water, vacuum drying;Finally washed with ether 4 times, the consumption of ether is 85.3g, obtains the degreaser of the final product present invention H3
Embodiment 4:Degreaser H4And preparation method thereof
(1) degreaser H4Composition, component and molecular formula it is as follows:
Degreaser H4Intermediate is generated by 2,5- pyridines diamidogen and formaldehyde, formic acid reaction, is then reacted with chlorine sodium laurate Amphoteric ion type degreaser is generated, wherein, the mol ratio of 2,5- pyridine diamidogen, formaldehyde, formic acid and chlorine sodium laurate is 1: 6: 5.5 ∶2.5.Degreaser H1Molecular formula it is as follows:
(2) degreaser H4Preparation method it is as follows:
1. 2, the 5- pyridines diamidogen and 2728.7g benzene of 1mol are added in there-necked flask, load onto returning with water knockout drum Stream condensing tube, stir speed (S.S.) is 300rpm, is warming up to 40 DEG C, and the formic acid of 5.5mol is poured in constant pressure funnel, control drop Constant speed degree, makes formic acid drip off in 30min, and after formic acid is dripped off, regulation stir speed (S.S.) is 600rpm, is warming up to 55 DEG C, will The formaldehyde of 6mol is poured in constant pressure funnel, controls rate of titration, formaldehyde is dripped off in 60min, treats that formol titration is finished Afterwards, 85 DEG C are warming up to, Temperature fall obtains solution A after reaction 24h;
2. it is 13 to pH value with the above-mentioned solution A of potassium hydroxide alkalization that mass concentration is 20%, uses n-hexane extraction upper strata Liquid, normal hexane consumption is 327.4g, removes solvent, obtains crude product B;
3. above-mentioned crude product B is poured in four-hole boiling flask, adds 1091.5g dehydrated alcohol, load onto condensing tube, in stirring Speed be 300rpm under, the chlorine sodium laurate of 2.5mol is soluble in water, be then slowly added in four-hole boiling flask with funnel, so After be warming up to 75 DEG C, stir speed (S.S.) is 400rpm, with the sodium bicarbonate that mass concentration is 25% alkalize to pH value be 9, react 14h Afterwards Temperature fall obtains solution C;
4. the pH to 3 of solution C is adjusted with the HCl of 6mol/L, stands 36h, then rotation evaporates ethanol under vacuum environment And water, vacuum drying;Finally washed with ether 5 times, the consumption of ether is 109.15g, obtains the oil removing of the final product present invention Agent H4
The degreaser H of embodiment 51Scene application
Multi-purpose station M2Water be ternary composite driving output water, test process scale be 90m3/ d, water oil content 765mg/ L, sewage salinity 22560mg/L, using the degreaser H of the present invention1To multi-purpose station M2Sewage carry out oil removal treatment, degreaser H1Dosage be 6.3kg/d, add degreaser in sewage after degreaser concentration be 70mg/L, oil content is reduced to after process 19.1mg/L, oil content reduces by 97.5%, reaches technological requirement.
The degreaser H of embodiment 62Scene application
Multi-purpose station L2Water be ternary composite driving output water, test process scale be 60m3/ d, water oil content 586mg/ L, sewage salinity 20253mg/L, using the degreaser H of the present invention2To multi-purpose station L2Sewage carry out oil removal treatment, degreaser H2Dosage be 3.3kg/d, add degreaser in sewage after degreaser concentration be 55mg/L, oil content is reduced to after process 8.2mg/L, oil content reduces by 98.6%, reaches technological requirement.
The degreaser H of embodiment 73Scene application
Multi-purpose station L5Water be ternary composite driving output water, test process scale be 50m3/ d, water oil content 823mg/ L, sewage salinity 18256mg/L, using the degreaser H of the present invention3To multi-purpose station L5Sewage carry out oil removal treatment, degreaser H3Dosage be 4.0kg/d, add degreaser in sewage after degreaser concentration be 80mg/L, oil content is reduced to after process 16.5mg/L, oil content reduces by 98.0%, reaches technological requirement.
The degreaser H of embodiment 84Scene application
Multi-purpose station L6Water be ternary composite driving output water, test process scale be 100m3/ d, water oil content 752mg/L, sewage salinity 17650mg/L, using the degreaser H of the present invention4To multi-purpose station L6Sewage carry out oil removal treatment, Degreaser H4Dosage be 7.0kg/d, add degreaser in sewage after degreaser concentration be 70mg/L, oil content after process 20.3mg/L is reduced to, oil content reduces by 97.3%, reaches technological requirement.

Claims (8)

1. a kind of degreaser of ternary composite flooding water extraction, it is characterised in that described degreaser be by 2,5- pyridines diamidogen with Formaldehyde, formic acid reaction generate intermediate, then generate amphoteric ion type degreaser with the reaction of chlorine sodium laurate, and its molecular formula is such as Under:
2. the degreaser of ternary composite flooding water extraction according to claim 1, it is characterised in that described 2,5- pyridines two The mol ratio of amine, formaldehyde, formic acid and chlorine sodium laurate is 1: 2.5~6: 2.5~5.5: 0.8~2.5.
3. the degreaser of ternary composite flooding water extraction according to claim 1 and 2, it is characterised in that described 2,5- pyrroles The mol ratio of pyridine diamidogen, formaldehyde, formic acid and chlorine sodium laurate is 1: 3: 3: 1.5.
4. a kind of preparation method of the degreaser of ternary composite flooding water extraction, it is characterised in that the preparation method is specifically included Following steps:
(1) 2, the 5- pyridines diamidogen and solvent of above-mentioned mol ratio are added in there-necked flask, load onto the backflow with water knockout drum Condensing tube, stir speed (S.S.) is 200~300rpm, is warming up to 30~40 DEG C, pours the formic acid of above-mentioned mol ratio into constant pressure addition leakage In bucket, control rate of titration, formic acid is dripped off in 20~30min, after formic acid is dripped off, adjust stir speed (S.S.) be 500~ 600rpm, is warming up to 50~55 DEG C, and the formaldehyde of aforementioned proportion is poured in constant pressure funnel, controls rate of titration, makes formaldehyde Drip off in 40~60min, after formol titration is finished, be warming up to 80~85 DEG C, Temperature fall obtains molten after 10~24h of reaction Liquid A;
(2) it is 12~13 to pH value with the above-mentioned solution A of potassium hydroxide alkalization that mass concentration is 20%, uses n-hexane extraction upper strata Liquid, removes solvent, obtains crude product B;
(3) above-mentioned crude product B is poured in four-hole boiling flask, adds dehydrated alcohol, load onto condensing tube, be 100 in stir speed (S.S.) It is under~300rpm, the chlorine sodium laurate of aforementioned proportion is soluble in water, then it is slowly added in four-hole boiling flask with funnel, then 70~75 DEG C are warming up to, stir speed (S.S.) is 350~400rpm, it is 8 to be alkalized to pH value with the sodium bicarbonate that mass concentration is 25% ~9, Temperature fall obtains solution C after 10~14h of reaction;
(4) pH to 2~3 of solution C is adjusted with the HCl of 6mol/L, stands 24~36h, then rotation is evaporated under vacuum environment Second alcohol and water, vacuum drying;Finally washed with ether 3~5 times, obtain the degreaser of the final product present invention.
5. the preparation method of the degreaser of ternary composite flooding water extraction according to claim 4, it is characterised in that described Solvent is Hexalin or benzene, and consumption is 10~25 times of 2,5- pyridine diamidogen quality.
6. the preparation method of the degreaser of the ternary composite flooding water extraction according to claim 4 or 5, it is characterised in that institute The consumption of the normal hexane stated is 2~3 times of 2,5- pyridine diamidogen quality.
7. the preparation method of the degreaser of ternary composite flooding water extraction according to claim 6, it is characterised in that described The consumption of dehydrated alcohol is 5~10 times of 2,5- pyridine diamidogen quality.
8. the preparation method of the degreaser of ternary composite flooding water extraction according to claim 7, it is characterised in that described The consumption of ether is 0.5~1 times of 2,5- pyridine diamidogen quality.
CN201610983357.5A 2016-11-09 2016-11-09 A kind of degreaser of ternary composite flooding water extraction and preparation method thereof Active CN106565007B (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110182895A (en) * 2019-05-23 2019-08-30 中国石油化工股份有限公司 A kind of degreaser and preparation method thereof for polymer-containing sewage in oil field processing

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0429996A2 (en) * 1989-11-21 1991-06-05 The B.F. Goodrich Company Process for methylating a hindered nitrogen atom in an inert non aqueous-solvent
WO2002036540A2 (en) * 2000-11-02 2002-05-10 Torrent Pharmaceuticals Ltd PROCESS FOR PREPARATION OF β-PHENETHYLAMINE DERIVATIVE
CN1911828A (en) * 2005-08-10 2007-02-14 福州大学 Modified lignin oil removing flocculant and its preparation method
CN102071110A (en) * 2011-01-06 2011-05-25 建德市白沙化工有限公司 Formula and preparation method of oil removal agent
CN102689941A (en) * 2012-05-29 2012-09-26 中国海洋石油总公司 Method for treating sewage in polymer flooding oilfield

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0429996A2 (en) * 1989-11-21 1991-06-05 The B.F. Goodrich Company Process for methylating a hindered nitrogen atom in an inert non aqueous-solvent
WO2002036540A2 (en) * 2000-11-02 2002-05-10 Torrent Pharmaceuticals Ltd PROCESS FOR PREPARATION OF β-PHENETHYLAMINE DERIVATIVE
CN1911828A (en) * 2005-08-10 2007-02-14 福州大学 Modified lignin oil removing flocculant and its preparation method
CN102071110A (en) * 2011-01-06 2011-05-25 建德市白沙化工有限公司 Formula and preparation method of oil removal agent
CN102689941A (en) * 2012-05-29 2012-09-26 中国海洋石油总公司 Method for treating sewage in polymer flooding oilfield

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110182895A (en) * 2019-05-23 2019-08-30 中国石油化工股份有限公司 A kind of degreaser and preparation method thereof for polymer-containing sewage in oil field processing
CN110182895B (en) * 2019-05-23 2021-06-18 中国石油化工股份有限公司 Oil removing agent for polymer-containing sewage treatment in oil field and preparation method thereof

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