CN109545419A - One kind is low to be placed with machine waste oil curing method formula and hardener formula - Google Patents

One kind is low to be placed with machine waste oil curing method formula and hardener formula Download PDF

Info

Publication number
CN109545419A
CN109545419A CN201811153997.9A CN201811153997A CN109545419A CN 109545419 A CN109545419 A CN 109545419A CN 201811153997 A CN201811153997 A CN 201811153997A CN 109545419 A CN109545419 A CN 109545419A
Authority
CN
China
Prior art keywords
low
waste oil
machine waste
stearic acid
added
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.)
Pending
Application number
CN201811153997.9A
Other languages
Chinese (zh)
Inventor
冯双喜
仇宏宇
张东梅
耿磊
吴伟
阳诚
李鸿展
文清云
王文龙
安晓丽
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sichuan Environmental Protection Engineering Co Ltd Cnnc
Original Assignee
Sichuan Environmental Protection Engineering Co Ltd Cnnc
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Sichuan Environmental Protection Engineering Co Ltd Cnnc filed Critical Sichuan Environmental Protection Engineering Co Ltd Cnnc
Priority to CN201811153997.9A priority Critical patent/CN109545419A/en
Publication of CN109545419A publication Critical patent/CN109545419A/en
Pending legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/04Treating liquids
    • G21F9/06Processing
    • G21F9/16Processing by fixation in stable solid media
    • G21F9/167Processing by fixation in stable solid media in polymeric matrix, e.g. resins, tars

Landscapes

  • Physics & Mathematics (AREA)
  • Engineering & Computer Science (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

Waste oil disposal technical field is put the invention belongs to low, and in particular to one kind is low to be placed with machine waste oil curing method formula and hardener formula.Technical solution: this method use is reacted in 70-100 DEG C of stearic acid with 5-15mol/L alkaline solution, generates hard hydrochlorate;And thickener cellulose is added, forming product stearic acid sodium is network structure, the interaction force of lipophilic group and oil molecule during being formed using stearic acid sodium inside the package oil suction of generated void space and product and oil suction.The utility model has the advantages that it is rapid to organic waste oil curing reaction, solidified body superior performance is formed, ability to cure is strong, volume reduction ratio is big, and comprehensive decontamination is at low cost, and test dose is less, and it is cheap, it is easy to purchase.

Description

One kind is low to be placed with machine waste oil curing method formula and hardener formula
Technical field
Put waste oil disposal technical field the invention belongs to low, and in particular to it is a kind of it is low be placed with machine waste oil curing method formula and Hardener formula.
Background technique
Radioactivity waste oil includes highly viscous lubricating oil, pumping fluid, machine oil, rail oil etc., and mostly with the shape of miscella Formula is temporary.Containing radionuclides such as tritium, strontium, caesium, cobalts in waste oil, temporary potential danger is very big for a long time.The master of waste oil disposal Want method, generally take with solid-state can incinerating waste material merge carry out burning disposal mode handled.It is useless for no solid The unit of object incinerating and treating device such as creates special incineration system for a small amount of fragmentary radioactivity waste oil and obviously lacks technology Support in terms of economy.Therefore, these units generally select by it is low put waste oil and be transported to the unit of incineration system handle. Since the Spent Radioactive alopecia areata of transport liquid is nearly larger, first waste oil solidification can be transported again, to reduce the transport wind of waste oil Danger.Domestic existing curing agent is mostly such as diatomite vermiculite inorganic solidification agent, although these inorganic absorbent function admirables, In burning disposal, volume reduction ratio is low, and level of residue is big after burning, is unfavorable for waste minimum.External existing curing agent such as N910 is solid Agent cost is too high, less economical.Accordingly, it is desirable to provide a kind of volume reduction ratio is high, the low of good economy performance is placed with machine waste oil solidification side Method formula and hardener formula.
Summary of the invention
It is an object of the invention to the problems low for existing curing agent volume reduction ratio, provide the low machine waste oil that is placed with of one kind and solidify Method formula and hardener formula reduce temporary risk, convenient transportation to the list for having disposing capacity to put waste oil solidification for low Position is disposed.
Technical scheme is as follows:
One kind is low to be placed with machine waste oil curing method, in turn includes the following steps,
Alkaline solution is added in low be placed in machine waste oil in step 1.;
Step 2. by be added alkaline solution it is low be placed with machine waste oil and be placed in 70~100 DEG C of water-bath heat, about 20min;
Then in low be placed in machine waste oil Stearic acid solids are added in step 3., and carry out stir about 2min to being fully cured, Form the stearate solid that product is network structure, generated void space during being formed using stearate solid Wrap up the interaction force of the lipophilic group and oil molecule inside oil suction and product and oil suction.
The alkali compounds is sodium hydroxide or potassium hydroxide.
Concentration 5~15mol/L of sodium hydroxide solution in the step 1, every milliliter low be placed with machine waste oil be added 0.1~ The sodium hydroxide solution of 0.3ml;In the step 3 every milliliter it is low be placed with machine waste oil addition Stearic acid solids quality be 0.2~ 0.6g。
The step 3 is additionally added thickener in low be placed in machine waste oil, so that stearic acid and joined sodium hydroxide solution It is low be placed with machine waste oil mixing it is more uniform.
The thickener is cellulose, and 0.05~0.2g cellulose is added in every milliliter of low is placed in machine waste oil.
Step 2 bath temperature is 90 DEG C.
Every milliliter of low Stearic acid solids quality for being placed with the addition of machine waste oil is 0.4g in the step 3.
The concentration of sodium hydroxide solution being added in the step 1 is 10mol/L, volume 0.2ml.
Low be placed with machine waste oil curing formula the present invention also provides a kind of, it is characterised in that: including sodium hydroxide solution and Stearic acid solids, every milliliter low be placed in machine waste oil be added 0.1~0.3ml concentration be 5~15mol/L sodium hydroxide solution and 0.2~0.6g Stearic acid solids.
The above-mentioned low machine waste oil curing formula that is placed with further includes thickener, and thickener is cellulose, and the quality of cellulose is 0.05~0.2g.
It is above-mentioned it is low be placed with machine waste oil curing formula be every milliliter it is low be placed in machine waste oil be added 0.2ml concentration be 10mol/L Sodium hydroxide solution and 0.4g Stearic acid solids.
The beneficial effects of the present invention are:
Compared with domestic and international existing curing technology, curing agent used in the present invention has following distinguishing feature: (1) to having Machine waste oil curing reaction is rapid, and in organic waste oil mass in the case where 20-50ml scale, the reaction time is less than 2min;(2) it is formed Solidified body superior performance, permeability rate are low less than 1%, viscosity, and the residual volume adhered to after being struck off using tool on the wall is small, heat Stability is good;(3) the curing agent ability to cure formed using curing formula of the invention is strong;(4) reagent that curing formula uses Most of is organic reagent, and volume reduction ratio is big after burning, volume reduction rate > 80%;(5) comprehensive decontamination is at low cost, test dose compared with It is few, it is cheap, it is easy to purchase.
Specific embodiment
Invention is further described in detail combined with specific embodiments below.
Embodiment 1
Present embodiments provide it is a kind of it is low be placed with machine waste oil curing method, using in 70-100 DEG C of stearic acid and 5-15mol/ The reaction of L sodium hydroxide solution, generates odium stearate;And thickener cellulose is added, forming product odium stearate is network structure, Lipophilic group and oil molecule during being formed using odium stearate inside the package oil suction of generated void space and product Interaction force and oil suction;Then product is cooled to room temperature.
The present embodiment additionally provides this low formula for being placed with machine waste oil curing agent, claims according to the required dosage for solidifying machine oil Measure the dosage of curing agent are as follows: 0.1~0.3ml sodium hydroxide solution (sodium hydroxide solution is added in every milliliter of low is placed in machine waste oil 5~15mol/L of concentration), 0.2~0.6g Stearic acid solids and 0.05~0.2g cellulose.
Wherein, every milliliter of machine oil is calculated by 1g, and wherein used oil mass fraction is 43.86~72.99%, sodium hydroxide matter Amount score is 1.46~7.89%, water quality score is 7.30~13.6%, cellulose mass fraction is 3.65~8.77%, hard Resin acid mass fraction is 14.6~26.32%.
Embodiment 2
The present embodiment on the basis of embodiment 1, commonly uses machine oil respectively, fetches the used oil from certain factory, from laboratory TBP/OK and scintillation solution from laboratory tested respectively as machine oil to be processed, successively carry out following steps:
Step 1. configures the sodium hydroxide solution of 10mol/L first, with about 90ml water by 40g sodium hydroxide solution, to It is transferred to constant volume in 100ml volumetric flask after liquid is cooling, 1g cellulose is then weighed and 4g stearic acid is stand-by.
20ml machine oil to be processed is added in step 2. in 100ml beaker, is wherein being added the configured 10mol/L's of 2ml Sodium hydroxide solution is placed in 90 DEG C of water-bath and is heated about 20min.
1g cellulose and 4g stearic acid is added in step 3., and carries out stir about 2min to being fully cured, and beaker is taken out cold But.
By experiment, it can be seen that the curing formula, which can dodge scintillation solution to 30% TBP/OK and liquid, completes solidification, and it is solid Change effect is fine, and gained cured body strength is higher, without free fluid after cooling, and almost without wall sticking phenomenon.
Embodiment 3
The present embodiment is fetched from the low of certain factory on the basis of embodiment 1 and embodiment 2 and is placed with machine waste oil, to extensive The low machine waste oil that is placed with solidified, successively carry out following steps:
Step 1. take it is low be placed with machine waste oil 1L, wherein be added the configured 10mol/L of 100ml sodium hydroxide solution;
Step 2. is placed in 90 DEG C of water-bath and is heated about 30min;
50g cellulose and 200g stearic acid is added in step 3., and carries out stir about 2min and be fully cured to waste oil, by beaker Take out cooling.
Solidified body performance test: permeability rate, volatility, solidified body thermal stability is carried out to solidified body.
1. thermal stability test: take a certain amount of solidified body to be heated on temperature controllable type electrothermal baffle, 100 DEG C, 150 DEG C, 180 DEG C, 210 DEG C are heated 15 minutes respectively, and solidified body is without significant change (up to 210 DEG C of electric hot plate heating).
2. permeability rate is tested: four groups of solidified bodies carry out the experiment of permeability rate.
It weighs respectively after taking three filter paper constant weights.A certain amount of solidified body is added on filter paper, and is weighed, and places 30 It weighs again after it.
Solidified body quality weighing result
Serial number Filter paper weight (g) Filter paper adds solidified body (g) Solidified body net weight (g)
1 4.344 30.578 26.234
2 4.328 29.244 24.916
3 4.342 27.922 23.580
4 4.399 28.472 24.133
Solidified body quality weighing result is weighed after 30 days
Serial number Filter paper weight (g) Filter paper adds solidified body (g) Solidified body net weight (g)
1 4.428 28.687 24.259
2 4.396 22.669 18.273
3 4.462 25.764 21.302
4 4.447 26.871 22.424
Solidified body performance
Serial number Permeability weight (g) Permeability rate (%)
1 0.084 0.35
2 0.068 0.37
3 0.120 0.56
4 0.108 0.48
Volume reduction ratio experiment
Serial number Solidify body weight (g) After directly burning remaining (g) Volume reduction ratio (%)
1 20.125 1.414 92.97
2 20.545 1.354 93.41
3 29.845 1.423 95.23
4 20.424 1.401 93.14
Performance parameter is as follows:
1. solidified body is without significant change when heating to solidified body for 100-210 DEG C.
2. measuring to solidified body permeability rate, solidified body permeability rate is 0.35%-0.56% after 30 days, and maximum value is 0.56%.
3. solidified body volume reduction ratio is 92.97%-95.23%.
Embodiment 4
The present embodiment on the basis of embodiment 1, fetches 4, the 20ml used oil sample from certain factory, 4ml is added wherein The sodium hydroxide solution of configured 10mol/L is heated to 70,80,90,100 DEG C in water-bath respectively, and it is fine that 2g is then added Dimension element and 8g stearic acid, and carry out stir about 2min and be fully cured to waste oil, beaker is taken out and is cooled down.Then for obtained production Object carries out solidity test.
Experimental phenomena: 70-80 DEG C of condensation is slightly slow, and wall is glued without fluidity in surface;90-100 DEG C condensation rapidly, surface without Fluidity, viscosity are smaller.The solidified body permeability rate and burning volume reduction ratio that above-mentioned experiment obtains meet the requirements.
Embodiment 5
On the basis of embodiment 1,6ml is added wherein and configures the present embodiment for the used oil from certain factory 20ml4 10mol/L sodium hydroxide solution, be placed in 90 DEG C of water-bath and heated about 20min, be added 3g cellulose and 12g it is hard Resin acid, and carry out stir about 2min and be fully cured to waste oil, beaker is taken out and is cooled down.10.0g solidified body is taken to be solidified respectively Body performance is measured:
Serial number Permeability weight Permeability rate It is remaining after directly burning Volume reduction ratio
1 0.014g 0.14% 1.62g 83.80%
2 0.014g 0.14% 1.59g 84.10%
3 0.013g 0.13% 1.57g 84.30%
4 0.013g 0.13% 1.57g 84.30%
Embodiment 6
The present embodiment on the basis of embodiment 1, fetches 3, the 20ml used oil sample from certain factory, 2ml is added wherein The sodium hydroxide solution of configured 5mol/L is heated to 90 DEG C of addition 1g celluloses and 4g stearic acid in water-bath, goes forward side by side Row stirring to waste oil is fully cured, and beaker is taken out and is cooled down.Solidified body curing time is 5 minutes.Beaker is taken out and is cooled down.Respectively It takes 10.0g solidified body to carry out solidified body performance to be measured:
Serial number Permeability weight Permeability rate It is remaining after directly burning Volume reduction ratio
1 0.023g 0.23% 0.84g 91.60%
2 0.026g 0.26% 0.82g 91.80%
3 0.024g 0.24% 0.85g 91.5%
Embodiment 7
The present embodiment on the basis of embodiment 1, fetches 3, the 20ml used oil sample from certain factory, 2ml is added wherein The sodium hydroxide solution of configured 10mol/L is heated to 90 DEG C of addition 1g celluloses and 4g stearic acid in water-bath, goes forward side by side Row stirring to waste oil is fully cured, and beaker is taken out and is cooled down.Solidified body curing time is 2 minutes.Beaker is taken out and is cooled down.Respectively It takes 10.0g solidified body to carry out solidified body performance to be measured:
Serial number Permeability weight Permeability rate It is remaining after directly burning Volume reduction ratio
1 0.018g 0.18% 0.92g 90.80%
2 0.017g 0.17% 0.94g 90.60%
3 0.018g 0.18% 0.94g 90.60%
Embodiment 8
The present embodiment on the basis of embodiment 1, fetches 3, the 20ml used oil sample from certain factory, 4ml is added wherein The sodium hydroxide solution of configured 15mol/L is heated to 90 DEG C of addition 2g celluloses and 8g stearic acid in water-bath, goes forward side by side Row stirring to waste oil is fully cured, and beaker is taken out and is cooled down.Solidified body curing time is 2 minutes.Beaker is taken out and is cooled down.Respectively It takes 10.0g solidified body to carry out solidified body performance to be measured:
Serial number Permeability weight Permeability rate It is remaining after directly burning Volume reduction ratio
1 0.018g 0.18% 1.21g 87.90%
2 0.017g 0.17% 1.23g 87.70%
3 0.018g 0.18% 1.24g 87.60%
The present invention, which is reacted using bases with stearic acid, to be formed the principle progress of stearate and organic low puts the cured side of waste oil Method.This formula provides alkaline condition using sodium hydroxide, it is possible to use methyl can be used in the bases reagent such as potassium hydroxide, thickener The derivatives such as cellulose, ethyl cellulose, hydroxymethyl-propyl cellulose.
Compared with domestic and international existing curing technology, curing agent used in the present invention has following distinguishing feature: (1) originally Invention is rapid to organic waste oil curing reaction, is less than 2min in the 20-50ml scale reaction time in organic waste oil mass.(2) solidify Body superior performance: solidified body permeability rate is low less than 1%, solidified body viscosity, and on the wall residual is adhered to after striking off using tool Surplus is small, and thermal stability is good, and at 200 DEG C, solidified body performance stablizes the big portion of curing agent used in (3) curing agent ability to cure strong (4) It is divided into organic reagent, burning volume reduction rate is big, and the comprehensive decontamination of volume reduction rate > 80% (5) is at low cost, and test dose is less, and price is just Preferably, it is easy to purchase.
The selection of the hardener formula absorbent of the present embodiment is mainly organic absorbent;In view of organic liquid waste polarity It is small, the organics absorbents such as long chain fatty acids soap, cellulose, polyacrylic acid lipid are carried out the study found that single absorbent pair The solidified body permeability rate of the weaker waste oil of polarity is higher, it is difficult to reach requirement.A variety of cooperation solidification effects are obviously improved and solid A small amount of inorganic additive is added during changing to be reduced the phenomenon that solidified body glues wall and permeability rate is effectively reduced.Comprehensively consider solidification effect Fruit, operation terseness and cost, select suitable absorbent to be combined.
Obviously, various changes and modifications can be made to the invention without departing from essence of the invention by those skilled in the art Mind and range.It is if these modifications and variations are within the scope of the claims of the present invention and its equivalent technology, then of the invention It is also intended to include these modifications and variations.

Claims (10)

1. one kind is low to be placed with machine waste oil curing method, it is characterised in that: it in turn includes the following steps,
Step 1. is in the low solution for being placed with and alkali compounds being added in machine waste oil and configures;
Step 2. by it is above-mentioned it is low be placed with machine waste oil and be placed in 70-100 DEG C of water-bath heat;
Then Stearic acid solids are added in above-mentioned low be placed in machine waste oil in step 3., and be stirred to being fully cured, and are formed and are produced Object is the hard hydrochlorate solid of network structure, and generated void space package is inhaled during being formed using hard hydrochlorate solid Oil and product inside lipophilic group and oil molecule interaction force and oil suction.
2. one kind as described in claim 1 is low to be placed with machine waste oil curing method, it is characterised in that: the alkali compounds configuration Solution be sodium hydroxide solution or potassium hydroxide solution.
3. one kind as claimed in claim 2 is low to be placed with machine waste oil curing method, it is characterised in that: the sodium hydroxide solution Concentration is 5-15mol/L, every milliliter of low sodium hydroxide solution for being placed with machine waste oil and 0.1~0.3ml being added;It is every in the step 3 The low Stearic acid solids quality for being placed with the addition of machine waste oil of milliliter is 0.2~0.6g.
4. one kind as described in claim 1-3 low is placed with machine waste oil curing method, it is characterised in that: the step 3 is put low It is additionally added thickener in organic waste oil, is placed with the mixing of machine waste oil more for making stearic acid and joined the low of sodium hydroxide solution Uniformly.
5. one kind as described in claim 1-3 low is placed with machine waste oil curing method, it is characterised in that: the step 2 water-bath temperature Degree is 90 DEG C.
6. one kind as described in claim 1-3 low is placed with machine waste oil curing method, it is characterised in that: every milli in the step 3 Rising the low Stearic acid solids quality for being placed with the addition of machine waste oil is 0.4g.
7. one kind as described in claim 1-3 low is placed with machine waste oil curing method, it is characterised in that: be added in the step 1 Concentration of sodium hydroxide solution be 10mol/L, volume 0.2ml.
8. low machine waste oil curing formula is placed with a kind of, it is characterised in that: including sodium hydroxide solution and Stearic acid solids, every milliliter It is low to be placed in machine waste oil that 0.1~0.3ml concentration is added is that 5~15mol/L sodium hydroxide solution and 0.2~0.6g stearic acid are solid Body.
9. one kind as claimed in claim 8 is low to be placed with machine waste oil curing formula, it is characterised in that: it further include thickener, every milli It rises low be placed in machine waste oil and 0.05~0.2g cellulose is added as thickener.
10. a kind of as claimed in claim 8 or 9 low be placed with machine waste oil curing formula, it is characterised in that: every milliliter low to be placed with machine 2 × 10 are added in waste oil-3Mol sodium hydroxide and 0.4g Stearic acid solids.
CN201811153997.9A 2018-09-30 2018-09-30 One kind is low to be placed with machine waste oil curing method formula and hardener formula Pending CN109545419A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811153997.9A CN109545419A (en) 2018-09-30 2018-09-30 One kind is low to be placed with machine waste oil curing method formula and hardener formula

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811153997.9A CN109545419A (en) 2018-09-30 2018-09-30 One kind is low to be placed with machine waste oil curing method formula and hardener formula

Publications (1)

Publication Number Publication Date
CN109545419A true CN109545419A (en) 2019-03-29

Family

ID=65841300

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811153997.9A Pending CN109545419A (en) 2018-09-30 2018-09-30 One kind is low to be placed with machine waste oil curing method formula and hardener formula

Country Status (1)

Country Link
CN (1) CN109545419A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111799009A (en) * 2020-07-31 2020-10-20 中核四川环保工程有限责任公司 Method for solidifying radioactive waste scintillation liquid

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05203796A (en) * 1992-01-23 1993-08-10 Hitachi Ltd Cement solidification of incombustible miscelleneous solid wastes and device thereof
JPH0634793A (en) * 1992-07-21 1994-02-10 Japan Atom Energy Res Inst Method of processing radioactive waste oil into low level flammable solid waste
JPH07150129A (en) * 1993-11-26 1995-06-13 Honen Corp Method for solidifying oil
JPH10123291A (en) * 1996-10-22 1998-05-15 Hitachi Ltd Method for solidifying organic solution and method for treating aqueous solution
CN104464867A (en) * 2014-12-03 2015-03-25 中国工程物理研究院材料研究所 Preparation method of high-strength cement solidifying body for radioactive used oil
JP2016136133A (en) * 2015-01-15 2016-07-28 三洋化成工業株式会社 Radioactive waste liquid solidification agent and method for producing radioactive waste liquid solidification agent
JP2017125132A (en) * 2016-01-14 2017-07-20 三洋化成工業株式会社 Waste liquid solidifying agent
CN107910091A (en) * 2017-11-16 2018-04-13 北京化工大学 A kind of compounding method of radioactivity waste oil

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05203796A (en) * 1992-01-23 1993-08-10 Hitachi Ltd Cement solidification of incombustible miscelleneous solid wastes and device thereof
JPH0634793A (en) * 1992-07-21 1994-02-10 Japan Atom Energy Res Inst Method of processing radioactive waste oil into low level flammable solid waste
JPH07150129A (en) * 1993-11-26 1995-06-13 Honen Corp Method for solidifying oil
JPH10123291A (en) * 1996-10-22 1998-05-15 Hitachi Ltd Method for solidifying organic solution and method for treating aqueous solution
CN104464867A (en) * 2014-12-03 2015-03-25 中国工程物理研究院材料研究所 Preparation method of high-strength cement solidifying body for radioactive used oil
JP2016136133A (en) * 2015-01-15 2016-07-28 三洋化成工業株式会社 Radioactive waste liquid solidification agent and method for producing radioactive waste liquid solidification agent
JP2017125132A (en) * 2016-01-14 2017-07-20 三洋化成工業株式会社 Waste liquid solidifying agent
CN107910091A (en) * 2017-11-16 2018-04-13 北京化工大学 A kind of compounding method of radioactivity waste oil

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111799009A (en) * 2020-07-31 2020-10-20 中核四川环保工程有限责任公司 Method for solidifying radioactive waste scintillation liquid
CN111799009B (en) * 2020-07-31 2024-04-19 中核四川环保工程有限责任公司 Method for solidifying radioactive waste scintillation liquid

Similar Documents

Publication Publication Date Title
Liu et al. Liquid–liquid equilibrium for systems of (fatty acid ethyl esters+ ethanol+ soybean oil and fatty acid ethyl esters+ ethanol+ glycerol)
CN109545419A (en) One kind is low to be placed with machine waste oil curing method formula and hardener formula
Leadbeater et al. Laboratory experiments using microwave heating
CN106188498A (en) A kind of bisphenol-type epoxyacrylate, its preparation method and photosensitive resin
CN208359478U (en) Environment-friendly type powder 3D printer
CN107910091B (en) A kind of compounding method of radioactivity waste oil
CN104010987A (en) Packaging of radioactive waste by cementing
Ji et al. Solventless ketalization of glycerol to solketal with acetone over the ionic liquid [P (C4H9) 3C14H29][TsO]
Hostetler et al. An improved synthesis of substituted [11C] toluenes via Suzuki coupling with [11C] methyl iodide
WO2008108079A1 (en) Analytical sample drying method and drying apparatus
Ramkumar et al. Exploring the solvation behavior of guanidinium based carboxylate ionic liquids in DMSO and DMF through apparent molar properties
CN109659059A (en) Handle device, system, method and the application of radioactive waste
CN103121715B (en) Preparation method of negative thermal expansion material ZrV2O7
CN101838521A (en) Preparation method of aliphatic dibasic acid/bentonite composite phase change energy storage material
CN205981854U (en) Formula soil organic matter detection device is cleared up to graphite
CN207198073U (en) It is a kind of to be used to estimate the device for fast detecting sentenced and meet content shared by water exothermic chemical product
Fretz et al. Birch Reductive Alkylation of Methyl m-(Hydroxymethyl) benzoate Derivatives and the Behavior of o-and p-(Hydroxymethyl) benzoates under Reductive Alkylation Conditions
JPS61500455A (en) Method for solidifying aqueous radioactive waste using an insoluble compound of magnesium oxide
CN102608156A (en) Device and method for measuring fouling resistance and heat conductivity
Bonomo et al. Acid-base chemistry of the metal-bonded porphyrinogen tetraanion: A novel methodology for the metal-assisted deuteration, alkylation, and functionalization of the porphyrinogen skeleton
CN207685065U (en) The retracting device of the solvent of the source containing MO
Yaakob et al. Esterification of palmitic acid with methanol in the presence of macroporous ion exchange resin as catalyst
CN107502025B (en) A kind of microcapsules temperature sensing material and the preparation method and application thereof
CN111799009A (en) Method for solidifying radioactive waste scintillation liquid
CN102798693B (en) Bromine residual detection method for dexamethasone epoxide

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20190329

RJ01 Rejection of invention patent application after publication