CN107792904A - A kind of technique and device of continuous removal of ammonia and nitrogen light component organic matter and salt - Google Patents

A kind of technique and device of continuous removal of ammonia and nitrogen light component organic matter and salt Download PDF

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Publication number
CN107792904A
CN107792904A CN201711004867.4A CN201711004867A CN107792904A CN 107792904 A CN107792904 A CN 107792904A CN 201711004867 A CN201711004867 A CN 201711004867A CN 107792904 A CN107792904 A CN 107792904A
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China
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level
evaporator
tower reactor
ammonia
rectifying tower
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CN201711004867.4A
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Chinese (zh)
Inventor
张春灵
毛学峰
李晓宁
李小刚
于秀刚
陈修英
刘国勇
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YANTAI GUOBANG CHEMICAL MACHINE TECHNOLOGY Co Ltd
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YANTAI GUOBANG CHEMICAL MACHINE TECHNOLOGY Co Ltd
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Priority to CN201711004867.4A priority Critical patent/CN107792904A/en
Publication of CN107792904A publication Critical patent/CN107792904A/en
Pending legal-status Critical Current

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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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • 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
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • 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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • C02F1/048Purification of waste water by evaporation
    • 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
    • C02F1/38Treatment of water, waste water, or sewage by centrifugal separation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia

Abstract

The invention belongs to technical field of waste water processing, is specifically related to a kind of continuous removal of ammonia and nitrogen light component organic matter and salt technique and system.A kind of waste water ammonia-removal nitrogen desalination process, it is characterised in that comprise the following steps that:Step 1:Rectifying tower reactor is distilled;Step 2:One-level is evaporated;Step 3:Dual evaporation;... step n:N levels are evaporated:Step n+1:Whole level evaporation.Change system used in a kind of waste water ammonia-removal nitrogen desalinating process, including rectifying tower reactor, one-level evaporator, dual evaporation tank and n level evaporators.Beneficial effects of the present invention:1) the light component organic matter in waste water, especially ammoniacal liquor are reclaimed, and purity is high;2) salt in final waste water is eventually converted into solid powder, reduces solid waste discharge;3) take off gently and take off and couple again, reduce plant running energy consumption 40%~70%;4) for waste water after de- light and desalination, obtaining clean water can be used as process water return system to recycle, and reduce the consumption of water.

Description

A kind of technique and device of continuous removal of ammonia and nitrogen light component organic matter and salt
Technical field
The invention belongs to technical field of waste water processing, a kind of waste water ammonia-removal nitrogen desalination process and used is specifically related to Change system.
Background technology
Industrial wastewater is industrial pollutants common in chemical process, if the life that directly discharge will be to us Environment produces destruction, our health of serious threat.And common one kind alkalescence containing NH4 wastewater from chemical industry, optimization can be passed through Processing reduces its pollution to environment, and processing of traditional handling process to the wastewater from chemical industry of alkalescence containing NH4 be not thorough, processing production Thing is not pure, it is impossible to reaches the purpose for realizing twice laid.
The content of the invention
The present invention makes up the deficiency of conventional art to solve problem mentioned above, there is provided one kind processing is efficient, thorough Bottom, production safety, highly reliable waste water ammonia-removal nitrogen desalination process and change system used.
The present invention is achieved through the following technical solutions:
A kind of technique of continuous removal of ammonia and nitrogen light component organic matter and salt, it is characterised in that comprise the following steps that:
Step 1:Rectifying tower reactor is distilled:By the waste water outside battery limit (BL), heated by preheater, be then sent to rectifying Rectification process is carried out in tower reactor, after ammonia steam introduces condenser condensation process by the tower top of rectifying tower reactor, then is evaporated via tower reactor Tank evaporates, and distinguishing branch by tower reactor reflux pump is pressed into ammonia outlet and rectifying tower reactor top rectifying circular treatment again;Rectifying Aqueous slkali is also added by the external world in the distillation process of tower reactor;The bottom liquid of rectifying tower reactor is pressed into rectifying tower reactor by tower reactor reboiler It is interior, circulate rectification process;
Step 2:One-level is evaporated:The waste water that will be flowed out after rectifying tower reactor rectifying, one-level is pumped into by tower reactor extraction and evaporated Processing is evaporated in tank, steam is entered in rectifying tower reactor by tower reactor reboiler, again rectification process;The bottom liquid of one-level evaporator Entered by one-level evaporator in one-level evaporator, circulating and evaporating processing;
Step 3:Dual evaporation:The waste water flowed out after one-level evaporator is evaporated, two level is pressed into by one-level transfering material pump and steamed Send out and re-evaporation processing is carried out in tank, steam is entered in one-level evaporator by one-level evaporator, again evaporation process;Dual evaporation tank Bottom liquid by secondary evaporimeter enter dual evaporation tank in, circulating and evaporating processing;
……
Step n:N levels are evaporated:The waste water flowed out after n-1 levels evaporator is evaporated, n levels are pressed into by n-1 levels transfering material pump and steamed Send out and re-evaporation processing is carried out in tank, steam is entered in n-1 level evaporators by n-1 levels evaporator, again evaporation process;N levels are evaporated The bottom liquid of tank is entered in n level evaporators by n levels evaporator, circulating and evaporating processing;
Step n+1:Whole level evaporation:The waste water flowed out after n levels evaporator is evaporated, whole level is pressed into by n levels transfering material pump and steamed Send out and re-evaporation processing is carried out in tank, steam is entered in n level evaporators by n levels evaporator, again evaporation process;Whole level evaporator Bottom liquid is entered in whole level evaporator by whole level evaporator, and pressure, circulating and evaporating processing are provided by circulating pump;Whole level evaporator Bottom liquid is introduced in drier and picked out after drying process by solid salt outlet;Another whole level evaporator provides saturated steam by the external world;
The natural number that n in step n and step n+1 described above is 1,2,3.......
It is described by the waste water outside battery limit (BL), be heated to 95 DEG C by preheater.
The tower top temperature of described rectifying tower reactor ensures that overhead extraction ammonia concn is 9~15%, cold at 95~100 DEG C But temperature is 35~40 DEG C after.
The steam pressure of described one-level evaporator outflow be P=0.1MPa, T=122 DEG C of vapor (steam) temperature, what bottom was flowed out Brine waste temperature T≤125 DEG C.
The steam pressure of described dual evaporation tank outflow is P=0.25MPa), T=138.8 DEG C of vapor (steam) temperature, bottom stream Brine waste temperature T≤125 DEG C gone out.
The steam pressure of described three-level evaporator outflow is P=0.4MPa), T=151.7 DEG C of vapor (steam) temperature.
The whole level evaporation pot bottom extraction be full of or oversaturated salting liquid is delivered to centrifugation, press filtration work by pump The water of section or drying machine evaporation drying, press filtration or evaporation removes waste water head tank, obtains containing salt solid powder.
A kind of system of continuous removal of ammonia and nitrogen light component organic matter and salt, including rectifying tower reactor, one-level evaporator, two level are steamed Send out tank and n level evaporators, it is characterised in that:The one-level preheater of waste water heat effect is connected on the top of rectifying tower reactor by pipeline With raw material two level preheater, the top of rectifying tower reactor connects condenser by conduit and enters port, condenser exit port connection tower reactor Evaporator, tower reactor evaporator connect the top of rectifying tower reactor by tower reactor backflow catheter pump, and the bottom of rectifying tower reactor passes through tower reactor Reboiler circulates bottom liquid to rectifying tower reactor;Rectifying tower reactor is provided with the interface for accessing extraneous aqueous slkali;
The bottom of rectifying tower reactor produces pump pipeline communication one-level evaporator by tower reactor, and the bottom of one-level evaporator passes through one Level evaporator circulates bottom liquid to one-level evaporator;
By one-level transfering material pump pipeline communication dual evaporation tank, the bottom of dual evaporation tank passes through for the bottom of one-level evaporator Secondary evaporimeter circulates bottom liquid to dual evaporation tank;
By two level transfering material pump pipeline communication n level evaporators, the bottom of n level evaporators passes through n for the bottom of dual evaporation tank Level evaporator circulates bottom liquid to n level evaporators;
The bottom of n level evaporators is connected by n level transfering material pump pipeline communication end level evaporators, the lower pipeline of whole level evaporator Circulating pump is connect, circulating pump pipeline connects whole level evaporator, and whole level evaporator pipeline connects whole level evaporator;The bottom of whole level evaporator Portion's pipeline communication drier;Whole level evaporator pipeline is additionally provided with the extraneous saturated steam interface of access.
The whole level evaporator pipeline connection raw material one-level preheater of described one-level evaporator, secondary evaporimeter ...
Described whole level evaporator pipeline connection raw material two level preheater.
Beneficial effects of the present invention:1) the light component organic matter in waste water, especially ammoniacal liquor are reclaimed, and purity is high;2) most Salt in whole waste water is eventually converted into solid powder, reduces solid waste discharge;3) take off gently and take off and couple again, reduce plant running energy Consumption 40%~70%;4) for waste water after de- light and desalination, obtaining clean water can be used as the circulation of process water return system to make With reducing the consumption of water.
Brief description of the drawings
The present invention is further illustrated below in conjunction with the accompanying drawings.
Fig. 1 is present system structural representation;
In figure, the outlet of 1 steam condensation water, 2 waste water material inlets, 3 temperaturing control pressure valves, 4 raw material one-level preheaters, 5 raw materials two Level preheater, 6 rectifying tower reactors, 7 condensers, 8 tower reactor evaporators, 9 tower reactor reflux pumps, 10 tower reactor reboilers, 11 tower reactors extraction pump, 12 one-level evaporators, 12-1 one-level evaporators, 12-2 one-level transfering material pumps, 13 dual evaporation tanks, 13-1 secondary evaporimeters, 13-2 bis- Level transfering material pump, 14 three-level evaporators, 14-1 three-level evaporators, 14-2 circulating pumps, 15 driers, 16 aqueous slkali imports, 17 ammonias Outlet, 18 saturated steams, the outlet of 19 solid salts, 20 fluid level control valves.
Embodiment
Accompanying drawing is a kind of specific embodiment of the invention.
The technique of continuous the removal of ammonia and nitrogen light component organic matter and salt of the present invention, is comprised the following steps that:
Step 1:Rectifying tower reactor is distilled:By the waste water outside battery limit (BL), heated by preheater, be then sent to rectifying Rectification process is carried out in tower reactor, after ammonia steam introduces condenser condensation process by the tower top of rectifying tower reactor, then is evaporated via tower reactor Tank evaporates, and distinguishing branch by tower reactor reflux pump is pressed into ammonia outlet and rectifying tower reactor top rectifying circular treatment again;Rectifying Aqueous slkali is also added by the external world in the distillation process of tower reactor;The bottom liquid of rectifying tower reactor is pressed into rectifying tower reactor by tower reactor reboiler It is interior, circulate rectification process;
Step 2:One-level is evaporated:The waste water that will be flowed out after rectifying tower reactor rectifying, one-level is pumped into by tower reactor extraction and evaporated Processing is evaporated in tank, steam is entered in rectifying tower reactor by tower reactor reboiler, again rectification process;The bottom liquid of one-level evaporator Entered by one-level evaporator in one-level evaporator, circulating and evaporating processing;
Step 3:Dual evaporation:The waste water flowed out after one-level evaporator is evaporated, two level is pressed into by one-level transfering material pump and steamed Send out and re-evaporation processing is carried out in tank, steam is entered in one-level evaporator by one-level evaporator, again evaporation process;Dual evaporation tank Bottom liquid by secondary evaporimeter enter dual evaporation tank in, circulating and evaporating processing;
Step 4:Whole level evaporation:The waste water flowed out after dual evaporation tank is evaporated, whole level is pressed into by two level transfering material pump and steamed Send out and re-evaporation processing is carried out in tank, steam is entered in dual evaporation tank by secondary evaporimeter, again evaporation process;Whole level evaporator Bottom liquid entered by whole level evaporator in whole level evaporator, provide pressure by circulating pump, circulating and evaporating processing;Whole level evaporator Bottom liquid introduce in drier and picked out after drying process by solid salt outlet;Another whole level evaporator provides saturation water by the external world and steamed Gas;
It is described by the waste water outside battery limit (BL), be heated to 95 DEG C by preheater.
The tower top temperature of described rectifying tower reactor ensures that overhead extraction ammonia concn is 9~15%, cold at 95~100 DEG C But temperature is 35~40 DEG C after.
The steam pressure of described one-level evaporator outflow be P=0.1MPa, T=122 DEG C of vapor (steam) temperature, what bottom was flowed out Brine waste temperature T≤125 DEG C.
The steam pressure of described dual evaporation tank outflow is P=0.25MPa), T=138.8 DEG C of vapor (steam) temperature, bottom stream Brine waste temperature T≤125 DEG C gone out.
The steam pressure of described three-level evaporator outflow is P=0.4MPa), T=151.7 DEG C of vapor (steam) temperature.
The whole level evaporation pot bottom extraction be full of or oversaturated salting liquid is delivered to centrifugation, press filtration work by pump The water of section or drying machine evaporation drying, press filtration or evaporation removes waste water head tank, obtains containing salt solid powder.
A kind of system of continuous removal of ammonia and nitrogen light component organic matter and salt, including rectifying tower reactor, one-level evaporator, two level are steamed Tank and whole level evaporator are sent out, the top of rectifying tower reactor connects the one-level preheater and raw material two level of waste water heat effect by pipeline Preheater, the top of rectifying tower reactor connect condenser by conduit and enter port, condenser exit port connection tower reactor evaporator, tower reactor Evaporator connects the top of rectifying tower reactor by tower reactor backflow catheter pump, and bottom is circulated in the bottom of rectifying tower reactor by tower reactor reboiler Liquid is to rectifying tower reactor;Rectifying tower reactor is provided with the interface for accessing extraneous aqueous slkali;
The bottom of rectifying tower reactor produces pump pipeline communication one-level evaporator by tower reactor, and the bottom of one-level evaporator passes through one Level evaporator circulates bottom liquid to one-level evaporator;
By one-level transfering material pump pipeline communication dual evaporation tank, the bottom of dual evaporation tank passes through for the bottom of one-level evaporator Secondary evaporimeter circulates bottom liquid to dual evaporation tank;
The bottom of dual evaporation tank passes through two level transfering material pump pipeline communication end level evaporator, the lower pipeline of whole level evaporator Circulating pump is connected, circulating pump pipeline connects whole level evaporator, and whole level evaporator pipeline connects whole level evaporator;Whole level evaporator Bottom pipe connects drier;Whole level evaporator pipeline is additionally provided with the extraneous saturated steam interface of access.Described one-level The whole level evaporator pipeline connection raw material one-level preheater of evaporator, secondary evaporimeter ....Described whole level evaporator pipeline connection Raw material two level preheater.
The general principle and principal character and advantages of the present invention of the present invention has been shown and described above.Above-described embodiment and Merely illustrating the principles of the invention described in specification, without departing from the spirit and scope of the present invention, the present invention is also Various changes and modifications are had, these changes and improvements all fall within the protetion scope of the claimed invention.It is claimed Scope is by appended claims and its equivalent thereof.

Claims (10)

1. the technique of a kind of continuous removal of ammonia and nitrogen light component organic matter and salt, it is characterised in that comprise the following steps that:
Step 1:Rectifying tower reactor is distilled:By the waste water outside battery limit (BL), heated by preheater, be then sent to rectifying tower reactor Interior carry out rectification process, after ammonia steam introduces condenser condensation process by the tower top of rectifying tower reactor, then via the steaming of tower reactor evaporator Hair, branch is distinguished by tower reactor reflux pump and is pressed into ammonia outlet and rectifying tower reactor top rectifying circular treatment again;Rectifying tower reactor Distillation process in also pass through and extraneous add aqueous slkali;The bottom liquid of rectifying tower reactor is pressed into rectifying tower reactor by tower reactor reboiler, Circulate rectification process;
Step 2:One-level is evaporated:The waste water that will be flowed out after rectifying tower reactor rectifying, it is pumped into by tower reactor extraction in one-level evaporator Processing is evaporated, steam is entered in rectifying tower reactor by tower reactor reboiler, again rectification process;The bottom liquid of one-level evaporator passes through One-level evaporator enters in one-level evaporator, circulating and evaporating processing;
Step 3:Dual evaporation:The waste water flowed out after one-level evaporator is evaporated, dual evaporation tank is pressed into by one-level transfering material pump Interior progress re-evaporation processing, steam are entered in one-level evaporator by one-level evaporator, again evaporation process;The bottom of dual evaporation tank Liquid is entered in dual evaporation tank by secondary evaporimeter, circulating and evaporating processing;
……
Step n:N levels are evaporated:The waste water flowed out after n-1 levels evaporator is evaporated, n level evaporators are pressed into by n-1 levels transfering material pump Interior progress re-evaporation processing, steam are entered in n-1 level evaporators by n-1 levels evaporator, again evaporation process;N level evaporators Bottom liquid is entered in n level evaporators by n levels evaporator, circulating and evaporating processing;
Step n+1:Whole level evaporation:The waste water flowed out after n levels evaporator is evaporated, whole level evaporator is pressed into by n levels transfering material pump Interior progress re-evaporation processing, steam are entered in n level evaporators by n levels evaporator, again evaporation process;The bottom liquid of whole level evaporator Entered by whole level evaporator in whole level evaporator, pressure, circulating and evaporating processing are provided by circulating pump;The bottom liquid of whole level evaporator Introduce in drier and picked out after drying process by solid salt outlet;Another whole level evaporator provides saturated steam by the external world;
The natural number that n in step n and step n+1 described above is 1,2,3.......
2. the technique of a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 1 and salt, it is characterised in that:Institute State by the waste water outside battery limit (BL), be heated to 95 DEG C by preheater.
3. the technique of a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 1 and salt, it is characterised in that:Institute The tower top temperature for the rectifying tower reactor stated ensures that overhead extraction ammonia concn is 9~15%, and temperature is after cooling at 95~100 DEG C 35~40 DEG C.
4. the technique of a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 1 and salt, it is characterised in that:Institute The steam pressure for the one-level evaporator outflow stated be P=0.1MPa, T=122 DEG C of vapor (steam) temperature, the brine waste temperature that bottom is flowed out Spend T≤125 DEG C.
5. the technique of a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 1 and salt, it is characterised in that:Institute The steam pressure for the dual evaporation tank outflow stated is P=0.25MPa), T=138.8 DEG C of vapor (steam) temperature, the saliferous of bottom outflow gives up Coolant-temperature gage T≤125 DEG C.
6. the technique of a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 1 and salt, it is characterised in that:Institute The steam pressure for the three-level evaporator outflow stated is P=0.4MPa), T=151.7 DEG C of vapor (steam) temperature.
7. the technique of a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 1 and salt, it is characterised in that:Institute State the evaporation pot bottom extraction of whole level be full of or oversaturated salting liquid is delivered to centrifugation, press filtration workshop section or drying machine by pump The water of evaporation drying, press filtration or evaporation removes waste water head tank, obtains containing salt solid powder.
8. a kind of continuous removal of ammonia and nitrogen light component organic matter and salt system, including rectifying tower reactor, one-level evaporator, dual evaporation tank With n level evaporators, it is characterised in that:The top of rectifying tower reactor connects the one-level preheater and original of waste water heat effect by pipeline Expect two level preheater, the top of rectifying tower reactor connects condenser by conduit and enters port, the connection tower reactor evaporation of condenser exit port Tank, tower reactor evaporator connect the top of rectifying tower reactor by tower reactor backflow catheter pump, and the bottom of rectifying tower reactor is boiled again by tower reactor Device circulates bottom liquid to rectifying tower reactor;Rectifying tower reactor is provided with the interface for accessing extraneous aqueous slkali;
The bottom of rectifying tower reactor produces pump pipeline communication one-level evaporator by tower reactor, and the bottom of one-level evaporator is steamed by one-level Send out device and circulate bottom liquid to one-level evaporator;
By one-level transfering material pump pipeline communication dual evaporation tank, the bottom of dual evaporation tank passes through two level for the bottom of one-level evaporator Evaporator circulates bottom liquid to dual evaporation tank;
By two level transfering material pump pipeline communication n level evaporators, the bottom of n level evaporators is steamed by n levels for the bottom of dual evaporation tank Send out device and circulate bottom liquid to n level evaporators;
The bottom of n level evaporators is followed by n level transfering material pump pipeline communication end level evaporators, the lower pipeline connection of whole level evaporator Ring pump, circulating pump pipeline connect whole level evaporator, and whole level evaporator pipeline connects whole level evaporator;The lower tube of whole level evaporator Road connects drier;Whole level evaporator pipeline is additionally provided with the extraneous saturated steam interface of access.
9. a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 8 and salt system, it is characterised in that:It is described One-level evaporator, secondary evaporimeter ... whole level evaporator pipeline connection raw material one-level preheater.
10. a kind of continuous removal of ammonia and nitrogen light component organic matter according to claim 8 and salt system, it is characterised in that:Institute The whole level evaporator pipeline connection raw material two level preheater stated.
CN201711004867.4A 2017-10-25 2017-10-25 A kind of technique and device of continuous removal of ammonia and nitrogen light component organic matter and salt Pending CN107792904A (en)

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CN108341447A (en) * 2018-04-04 2018-07-31 烟台国邦化工机械科技有限公司 A kind of waste liquid continuously takes off light desalination process and system
CN108467076A (en) * 2018-06-01 2018-08-31 烟台国邦化工机械科技有限公司 Based on the process and device for strengthening resolving resourceization processing waste water containing low-boiling-point substance

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CN106746110A (en) * 2016-12-02 2017-05-31 广州市心德实业有限公司 A kind of device and processing method for processing high ammonia nitrogen and high salt waste water
CN207451656U (en) * 2017-10-25 2018-06-05 烟台国邦化工机械科技有限公司 A kind of continuous removal of ammonia and nitrogen light component organic matter and salt system

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CN103539299A (en) * 2012-07-10 2014-01-29 南京大学 Process for recycling wastewater containing low boiling-point organism such as formaldehyde and high-concentration inorganic salt
CN103224260A (en) * 2013-04-12 2013-07-31 苏州中色德源环保科技有限公司 Wastewater treatment and recovery method
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CN105481036A (en) * 2015-11-06 2016-04-13 王文领 Energy-saving type negative-pressure deamination method of coked residual ammonia water
CN105418447A (en) * 2015-12-17 2016-03-23 烟台国邦化工机械科技有限公司 DMAC (dimethylacetamide) rectification device and technique
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108341447A (en) * 2018-04-04 2018-07-31 烟台国邦化工机械科技有限公司 A kind of waste liquid continuously takes off light desalination process and system
CN108467076A (en) * 2018-06-01 2018-08-31 烟台国邦化工机械科技有限公司 Based on the process and device for strengthening resolving resourceization processing waste water containing low-boiling-point substance

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