CN116637606A - Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process - Google Patents

Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process Download PDF

Info

Publication number
CN116637606A
CN116637606A CN202310568568.2A CN202310568568A CN116637606A CN 116637606 A CN116637606 A CN 116637606A CN 202310568568 A CN202310568568 A CN 202310568568A CN 116637606 A CN116637606 A CN 116637606A
Authority
CN
China
Prior art keywords
adsorption bed
toluene
resin
sulfur
lower outlet
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN202310568568.2A
Other languages
Chinese (zh)
Other versions
CN116637606B (en
Inventor
马继鹏
刘生海
艾小兵
郝勇
刘建明
王江鹏
王强
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.)
Shaanxi Yanchang Zhongmei Yulin Energy And Chemical Co ltd
Original Assignee
Shaanxi Yanchang Zhongmei Yulin Energy And Chemical Co ltd
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 Shaanxi Yanchang Zhongmei Yulin Energy And Chemical Co ltd filed Critical Shaanxi Yanchang Zhongmei Yulin Energy And Chemical Co ltd
Priority to CN202310568568.2A priority Critical patent/CN116637606B/en
Publication of CN116637606A publication Critical patent/CN116637606A/en
Application granted granted Critical
Publication of CN116637606B publication Critical patent/CN116637606B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/345Regenerating or reactivating using a particular desorbing compound or mixture
    • B01J20/3475Regenerating or reactivating using a particular desorbing compound or mixture in the liquid phase
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/26Synthetic macromolecular compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/3425Regenerating or reactivating of sorbents or filter aids comprising organic materials
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/345Regenerating or reactivating using a particular desorbing compound or mixture
    • B01J20/3458Regenerating or reactivating using a particular desorbing compound or mixture in the gas phase
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/345Regenerating or reactivating using a particular desorbing compound or mixture
    • B01J20/3458Regenerating or reactivating using a particular desorbing compound or mixture in the gas phase
    • B01J20/3466Regenerating or reactivating using a particular desorbing compound or mixture in the gas phase with steam
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • 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
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The application discloses a regeneration method of a resin adsorption bed layer in a sulfur-ammonia-containing sewage treatment process, which comprises the following steps: s1, opening an upper inlet and a lower outlet, injecting water from the upper inlet, and then collecting liquid flowing out from the lower outlet; s2, stopping water injection, injecting toluene from an upper inlet, standing for soaking after the toluene fully infiltrates the resin particles, continuously injecting toluene from the upper inlet, collecting liquid flowing out from a lower outlet until the liquid flowing out from the lower outlet is transparent, and stopping injecting toluene; s3, injecting nitrogen from an upper inlet, and collecting liquid flowing out from a lower outlet; stopping injecting nitrogen after no liquid flows out from the lower outlet, blowing superheated steam from the upper inlet, cooling and collecting the liquid flowing out from the lower outlet; s4, stopping injecting superheated steam, injecting water from an outlet at the lower part, stopping injecting water when the inside of the shell of the resin adsorption bed layer is full of liquid, and standing until the resin particles are uniformly dispersed.

Description

Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process
Technical Field
The application relates to the technical field of adsorption resin recycling, in particular to a method for recycling a resin adsorption bed layer in a sulfur-ammonia-containing sewage treatment process.
Background
The sulfur-ammonia-containing sewage can be generated in the heavy oil catalytic pyrolysis process, and the current commonly used sulfur-ammonia-containing sewage treatment process comprises the following steps: firstly, skimming the floating oil in the sulfur-ammonia-containing sewage, and then adsorbing organic matters in the sulfur-ammonia-containing sewage through a resin adsorption bed layer, so that the sulfur-ammonia-containing sewage can be subjected to the next process treatment.
In the working process of the resin adsorption bed, impurities adsorbed by the internal resin can be gradually accumulated to block holes on the surface and in the resin, so that the adsorption purification capacity of the resin adsorption bed is gradually deteriorated; when the oil content in the liquid flowing out from the outlet at the lower part of the resin adsorption bed layer is too high, the resin inside the resin adsorption bed layer is required to be regenerated to restore the original adsorption capacity.
At present, in the adsorption treatment process of the sulfur-containing ammonia sewage by the heavy oil catalytic pyrolysis process, the main problem is that after the resin is regenerated once or for a plurality of times, impurities in holes of the resin still cannot be effectively removed and the original adsorption quantity of the resin cannot be recovered due to incomplete regeneration, so that the service cycle and service life of the resin are very limited, and the practical application effect of a resin adsorption bed in the sulfur-containing ammonia sewage treatment process is affected.
Disclosure of Invention
The embodiment of the application solves the problems of limited service cycle and service life and influence on the practical application effect caused by incomplete regeneration in the existing resin adsorption bed regeneration process by providing the regeneration method of the resin adsorption bed in the sulfur-containing ammonia sewage treatment process, and realizes the technical effects of being capable of quickly regenerating the resin bed after adsorbing impurities, ensuring thorough regeneration and ensuring that the resin can recover more ideally or be close to the original adsorption quantity.
The embodiment of the application provides a regeneration method of a resin adsorption bed layer in a sulfur-ammonia-containing sewage treatment process, wherein the resin adsorption bed layer comprises a cylindrical shell and a plurality of resin particles filled in the shell, and the shell is provided with an upper inlet and a lower outlet; the regeneration method of the resin adsorption bed layer in the sulfur ammonia-containing sewage treatment process provided by the embodiment comprises the following steps:
s1, opening an upper inlet and a lower outlet of a resin adsorption bed layer after adsorption of sulfur-ammonia-containing sewage, injecting water from the upper inlet, collecting liquid flowing out from the lower outlet, and filling the liquid into a container;
s2, stopping injecting water, injecting toluene from an upper inlet after no liquid flows out from a lower outlet, standing and soaking after the toluene is fully soaked in resin particles, continuously injecting toluene from the upper inlet and collecting the liquid flowing out from the lower outlet until the liquid flowing out from the lower outlet is transparent, stopping injecting toluene, and filling the collected liquid into the container;
s3, injecting nitrogen from an upper inlet, collecting liquid flowing out from a lower outlet and filling the liquid into a container; stopping injecting nitrogen after no liquid flows out from the lower outlet, blowing superheated steam from the upper inlet, collecting the liquid flowing out from the lower outlet, cooling, and filling into the container;
s4, stopping injecting superheated steam, injecting water from an outlet at the lower part, stopping injecting water when the inside of the shell of the resin adsorption bed layer is full of liquid, and standing until the resin particles are uniformly dispersed.
In one possible implementation of the present application,
in S1, the internal pressure of the resin adsorption bed layer is controlled to be 0.1MPa.
In one possible implementation of the present application,
the water injected in S1 is desalted water.
In one possible implementation of the present application,
s2, controlling the internal pressure of the vertical adsorption bed layer to be 0.1MPa when toluene is injected.
In one possible implementation of the present application,
and S2, fully soaking the resin particles in toluene, and standing and soaking for 60-70 min.
In one possible implementation of the present application,
s2, toluene flow rate at the time of continuous injection of toluene was 0.2m 3 /h。
In one possible implementation of the present application,
the duration of continuous injection of toluene is not less than 50min.
In one possible implementation of the present application,
the temperature of the superheated steam blown in S3 is 110-120 ℃.
In one possible implementation of the present application,
the pressure of the superheated steam blown in S3 is 0.2-0.3 MPa.
In one possible implementation of the present application,
the water injected in S4 is demineralized water.
One or more technical solutions provided in the embodiments of the present application at least have the following technical effects or advantages:
the regeneration method of the resin adsorption bed layer in the sulfur-ammonia-containing sewage treatment process provided by the embodiment of the application adopts the technical scheme that the resin adsorbed with impurities is sequentially subjected to multistage elution and regeneration by water, toluene and superheated steam, wherein impurities with relatively weak adhesion degree can be washed out from holes and surfaces of the resin by first water washing; toluene soaking and continuous flowing flushing can enable toluene to permeate into the resin, and organic impurities adsorbed in the surface and the holes in the resin are fully extracted, dissolved and carried out; the subsequent nitrogen can blow out a small amount of impurities and partial toluene remained in the holes on the surface and in the interior of the resin to be taken away; the superheated steam purging can fully evaporate and carry out residual toluene in the holes on the surface and the inside of the resin; and finally, back flushing the water flow to fully and uniformly mix the resin particles again and cooling. Through the method flow, the embodiment of the application can quickly and efficiently remove the organic impurities adsorbed in the resin particles, and simultaneously can avoid residual impurities and toluene residues generated in the removal and regeneration process, thereby ensuring a more thorough regeneration effect, avoiding the breakage of the resin particles during regeneration or uneven dispersion of the resin particles after regeneration, further improving the regeneration effect, and enabling the adsorption capacity of the resin adsorption bed after regeneration to be as close as possible or even equal to the initial adsorption capacity of the resin adsorption bed.
Drawings
In order to more clearly illustrate the embodiments of the present application or the technical solutions in the prior art, the drawings that are needed in the embodiments of the present application or the description of the prior art will be briefly described below, and it is obvious that the drawings in the following description are some embodiments of the present application, and other drawings may be obtained according to these drawings without inventive effort for a person skilled in the art.
Fig. 1 is a schematic diagram of an apparatus used in a certain use scenario in a method for regenerating a resin adsorption bed layer in a sulfur ammonia-containing sewage treatment process according to an embodiment of the present application.
In the figure: 1-a superheated steam line; 2-nitrogen line; a 3-toluene line; 4-sulfur ammonia-containing sewage enters a pipeline; 5-water line; 6-a flare exhaust line; 7-a purified sewage discharge line; 8-a regeneration liquid discharge line; 9-cooler.
Detailed Description
The following description of the embodiments of the present application will be made clearly and fully with reference to the accompanying drawings, in which it is evident that the embodiments described are some, but not all embodiments of the application. All other embodiments, which can be made by those skilled in the art based on the embodiments of the application without making any inventive effort, are intended to be within the scope of the application.
In the description of the embodiments of the present application, it should be noted that the terms "center," "upper," "lower," "left," "right," "vertical," "horizontal," "inner," "outer," and the like indicate or are based on the orientation or positional relationship shown in the drawings, merely to facilitate description of the embodiments of the present application and simplify description, and do not indicate or imply that the devices or elements referred to must have a specific orientation, be configured and operated in a specific orientation, and thus should not be construed as limiting the present application. The terms "first," "second," and "third" are used for descriptive purposes only and are not to be construed as indicating or implying relative importance. The specific meaning of the above terms in the embodiments of the present application will be understood by those of ordinary skill in the art according to specific circumstances.
The embodiment of the application provides a regeneration method of a resin adsorption bed layer in a sulfur-ammonia-containing sewage treatment process, wherein the resin adsorption bed layer comprises a cylindrical shell and a plurality of resin particles filled in the shell, and the shell is provided with an upper inlet and a lower outlet; the regeneration method of the resin adsorption bed layer in the sulfur ammonia-containing sewage treatment process provided by the embodiment comprises the following steps:
s1, opening an upper inlet and a lower outlet of a resin adsorption bed layer after adsorption of sulfur-ammonia-containing sewage, introducing water from a water pipeline 5 connected with the upper inlet, collecting liquid flowing out from a regenerated liquid discharge pipeline 8 connected with the lower outlet, and filling the liquid into a container; the water line 5 is connected with the upper inlet and the lower outlet of the resin adsorption bed layer at the same time, as shown in fig. 1;
s2, stopping injecting water, injecting toluene from a toluene pipeline 3 communicated with an upper inlet after no liquid flows out of a regenerated liquid discharge pipeline 8, standing for soaking after the toluene is fully soaked in resin particles, continuously injecting toluene from the toluene pipeline 3, collecting liquid flowing out of the regenerated liquid discharge pipeline 8 until the liquid flowing out of a regenerated liquid discharge pipeline 9 is transparent, stopping injecting toluene, and filling the collected liquid into the container;
s3, injecting nitrogen into the nitrogen pipeline 2 communicated with the upper inlet, collecting liquid flowing out of the regenerated liquid discharge pipeline 8 and filling the liquid into a container; stopping injecting nitrogen after no liquid flows out of the regenerated liquid discharge pipeline 8, blowing in superheated steam from the superheated steam pipeline 1 communicated with the upper inlet, collecting the liquid flowing out of the regenerated liquid discharge pipeline 8, cooling the liquid by the cooler 9, and loading the liquid into the container;
s4, stopping blowing superheated steam, closing one end of the water pipeline 5, which is communicated with the upper inlet of the resin adsorption bed layer, injecting water from the water pipeline 5, enabling the water to enter the resin adsorption bed layer from one end of the water pipeline 5, which is communicated with the lower outlet of the resin adsorption bed layer, stopping injecting water when the inside of the shell of the resin adsorption bed layer is full of liquid, and then standing until resin particles are uniformly dispersed.
When the resin adsorption bed is used, the sulfur-containing ammonia sewage communicated with the upper inlet of the resin adsorption bed enters the pipeline 4, the sulfur-containing ammonia sewage is introduced, and after the sulfur-containing ammonia sewage is adsorbed and purified by the resin adsorption bed, the sulfur-containing ammonia sewage is discharged from the regenerated liquid discharge pipeline 8 communicated with the lower outlet of the resin adsorption bed.
The regeneration method of the resin adsorption bed layer in the sulfur-ammonia-containing sewage treatment process provided by the embodiment of the application adopts the technical scheme that the resin adsorbed with impurities is sequentially subjected to multistage elution and regeneration by water, toluene and superheated steam, wherein impurities with relatively weak adhesion degree can be washed out from holes and surfaces of the resin by first water washing; toluene soaking and continuous flowing flushing can enable toluene to permeate into the resin, and organic impurities adsorbed in the surface and the holes in the resin are fully extracted, dissolved and carried out; the subsequent nitrogen can blow out a small amount of impurities and partial toluene remained in the holes on the surface and in the interior of the resin to be taken away; the superheated steam purging can fully evaporate and carry out residual toluene in the holes on the surface and the inside of the resin; and finally, back flushing the water flow to fully and uniformly mix the resin particles again and cooling. Through the method flow, the embodiment of the application can quickly and efficiently remove the organic impurities adsorbed in the resin particles, and simultaneously can avoid residual impurities and toluene residues generated in the removal and regeneration process, thereby ensuring a more thorough regeneration effect, avoiding the breakage of the resin particles during regeneration or uneven dispersion of the resin particles after regeneration, further improving the regeneration effect, and enabling the adsorption capacity of the resin adsorption bed after regeneration to be as close as possible or even equal to the initial adsorption capacity of the resin adsorption bed.
It should be noted that, generally, the lower outlet of the resin adsorption bed is higher than the upper inlet, so that a liquid seal is formed to avoid the excessive liquid in the resin adsorption bed from flowing out, and at the same time, the air pressure in the resin adsorption bed can be stabilized. Thus, in this embodiment, the lower outlet does not normally need to be closed when liquid or blowing gas is injected from the upper inlet of the resin adsorbent bed; the formation of a liquid seal at the lower outlet also ensures that when the upper inlet ceases to inject liquid or gas, the flow of liquid outwardly of the lower outlet ceases immediately, thereby avoiding excessive material loss.
In a preferred implementation of this example,
in S1, the internal pressure of the resin adsorption bed layer is controlled to be 0.1MPa.
Specifically, the internal pressure of the resin adsorption bed layer is controlled to be 0.1MPa in the present preferred embodiment, and the main purpose thereof is to: on one hand, the resin particles in the resin adsorption bed layer are prevented from being crushed by fracturing caused by excessive extrusion caused by excessive pressure; on the other hand, the phenomenon that water cannot smoothly enter due to overlarge pressure in the resin adsorption bed layer, so that the water flow cleaning effect is affected is avoided.
In a preferred implementation of this example,
the water injected in S1 is desalted water.
Specifically, demineralized water is water obtained by removing suspended substances, colloids, inorganic cations, anions, and other impurities from water by various water treatment processes. The resin particles in the resin adsorption bed are cleaned for the first time by desalted water, so that the cleaning effect is ensured, and impurities originally contained in water can be prevented from entering holes of the resin particles to further influence the regeneration effect.
In a preferred implementation of this example,
s2, controlling the internal pressure of the vertical adsorption bed layer to be 0.1MPa when toluene is injected.
Specifically, the internal pressure of the resin adsorption bed layer is controlled to be 0.1MPa in the present preferred embodiment, and the main purpose thereof is to: on one hand, the phenomenon that resin particles are broken and toluene cannot smoothly enter the inside of the resin bed layer due to overlarge internal pressure of the resin adsorption bed layer is avoided, and a better elution effect can be realized when the toluene needs to be fully contacted with the resin particles; on the other hand, the phenomenon that the inside pressure of the resin bed layer is too small, and toluene is not fully contacted with resin particles after entering, namely is sucked out of the inside of the resin bed layer under the action of negative pressure, so that the regeneration effect is influenced is avoided.
In a preferred implementation of this example,
and S2, fully soaking the resin particles in toluene, and standing and soaking for 60-70 min.
Specifically, toluene can gradually penetrate into the resin particles to a certain depth when continuously soaked, so that impurities adsorbed in the resin particles are extracted and dissolved, the eluting effect can be greatly improved, and the adsorption capacity of the resin particles is recovered; however, too long soaking time can cause too deep penetration of toluene into the resin particles, and when subsequent flowing flushing of toluene, nitrogen blowing and steam evaporation are carried out, toluene in deeper places can not be effectively removed, and hidden dangers affecting the regeneration effect and the adsorption capacity recovery effect of the resin can exist. The repeated test proves that the soaking time of 60-70 min can better meet the comprehensive requirements.
In a preferred implementation of this example,
s2, toluene flow rate at the time of continuous injection of toluene was 0.2m 3 /h。
Specifically, the flow rate of toluene is not too small but too large, the flow rate is too small, the fluidity of toluene among the resin particles is insufficient, impurities in the resin particles are difficult to sufficiently and effectively wash out in the flowing process, and the flowing and infiltration of toluene are difficult to ensure uniformity; the flow rate is too high and the flow rate is too high,the time for fully contacting toluene with resin particles is short, impurities are difficult to effectively remove, excessive impact force is brought by excessive flow, and resin particles are easy to crack or even break, so that the adsorption performance of the whole resin adsorption bed layer is influenced. Through repeated experiments, the current measurement value is 0.2m 3 The toluene flow per hour can better meet the comprehensive requirements.
In a preferred implementation of this example,
the duration of continuous injection of toluene is not less than 50min.
Specifically, the toluene flow rinse needs to last for a long time to be able to sufficiently contact each resin particle during the flow rinse, and to extract, dissolve and carry out impurities as thoroughly as possible from the surface and the inside thereof.
In a preferred implementation of this example,
the temperature of the superheated steam blown in S3 is 110-120 ℃.
Specifically, superheated steam is blown in the technical scheme of the embodiment of the application, and the aim is mainly to evaporate and carry out toluene which has deeper penetration inside the resin particles, so as to remove residual toluene and ensure the regeneration effect; the boiling point of toluene is about 110 ℃, and the resin particles can generate deformation, aging, fragmentation and other problems at too high temperature, so the preferred embodiment controls the temperature of superheated steam to be 110-120 ℃, so that the toluene in the resin particles can be fully evaporated and carried out, and the structure and the performance of the resin particles are not adversely affected.
In a preferred implementation of this example,
the pressure of the superheated steam blown in S3 is 0.2-0.3 MPa.
In particular, the pressure of the superheated steam is not too high nor too low: the excessive pressure can cause the resin particles to be in high temperature and high pressure, in the environment, the resin particles are easier to generate problems of deformation, aging, fragmentation and the like, and further the regeneration effect and the adsorption performance of the whole resin adsorption bed layer are possibly and negatively influenced; too little pressure may result in insufficient and effective contact of the superheated steam with the individual resin particles, and even there may be cases where the superheated steam has condensed into droplets without contacting the deeper, lower resin particles, and the regeneration effect may be adversely affected. Through repeated experiments, the superheated steam pressure of 0.2-0.3 MPa can be determined to better meet the comprehensive requirements.
In a preferred implementation of this example,
the water injected in S4 is demineralized water.
Specifically, the demineralized water is backwashed, firstly, the resin particles are cooled together to prevent the resin particles from overheating deformation, ageing and cracking, secondly, the resin particles are dispersed and are uniformly dispersed again, and thirdly, the phenomenon that excessive impurities are adsorbed again by the resin particles which are fully cleaned and regenerated originally due to more impurities in water can be avoided.
In this specification, each embodiment is described in a progressive manner, and the same or similar parts of each embodiment are referred to each other, and each embodiment is mainly described as a difference from other embodiments.
The above embodiments are only for illustrating the technical solution of the present application, and not for limiting the present application; although the application has been described in detail with reference to the foregoing embodiments, it will be understood by those of ordinary skill in the art that: the technical scheme described in the foregoing embodiments can be modified or some or all of the technical features thereof can be replaced with equivalents; such modifications and substitutions do not depart from the spirit of the application.

Claims (10)

1. The regeneration method of the resin adsorption bed layer in the sulfur ammonia-containing sewage treatment process comprises a cylindrical shell which is vertically arranged, and a plurality of resin particles filled in the shell, wherein the shell is provided with an upper inlet and a lower outlet; the method is characterized by comprising the following steps of:
s1, opening an upper inlet and a lower outlet of a resin adsorption bed layer after adsorption of sulfur-ammonia-containing sewage, injecting water from the upper inlet, and then collecting liquid flowing out from the lower outlet and filling the liquid into a container;
s2, stopping injecting water, injecting toluene from the upper inlet after no liquid flows out of the lower outlet, standing for soaking after the toluene is fully soaked in resin particles, continuously injecting toluene from the upper inlet, collecting liquid flowing out of the lower outlet until the liquid flowing out of the lower outlet is transparent, stopping injecting toluene, and filling the collected liquid into the container;
s3, injecting nitrogen from the upper inlet, collecting liquid flowing out from the lower outlet and filling the liquid into the container; stopping injecting nitrogen after no liquid flows out of the lower outlet, blowing superheated steam from the upper inlet, collecting the liquid flowing out of the lower outlet, cooling and then filling the liquid into the container;
s4, stopping injecting superheated steam, injecting water from the lower outlet, stopping injecting water when the inside of the shell of the resin adsorption bed layer is full of liquid, and standing until the resin particles are uniformly dispersed.
2. The method for regenerating a resin adsorption bed in a sulfur ammonia wastewater treatment process according to claim 1, wherein in S1, the internal pressure of the resin adsorption bed is controlled to be 0.1MPa.
3. The method for regenerating a resin adsorption bed in a sulfur-containing ammonia wastewater treatment process according to claim 1, wherein the water injected in S1 is demineralized water.
4. The method for regenerating a resin adsorption bed in a sulfur ammonia wastewater treatment process according to claim 1, wherein the internal pressure of the vertical adsorption bed is controlled to be 0.1mpa when toluene is injected in S2.
5. The method for regenerating a resin adsorption bed in a sulfur-containing ammonia wastewater treatment process according to claim 1, wherein in S2, toluene fully infiltrates resin particles and then stands for soaking for 60-70 min.
6. The method for regenerating a resin adsorption bed in a sulfur-containing ammonia wastewater treatment process according to claim 1, wherein in S2, the toluene flow rate when continuously injecting toluene is 0.2m 3 /h。
7. The method for regenerating a resin adsorption bed in a sulfur ammonia wastewater treatment process according to claim 1, wherein the duration of continuous injection of toluene is not less than 50min.
8. The method for regenerating a resin adsorption bed in a sulfur-containing ammonia wastewater treatment process according to claim 1, wherein the temperature of the superheated steam blown in S3 is 110 ℃ to 120 ℃.
9. The method for regenerating a resin adsorption bed in a sulfur ammonia-containing sewage treatment process according to claim 1, wherein the pressure of the superheated steam blown in S3 is 0.2 to 0.3MPa.
10. The method for regenerating a resin adsorption bed in a sulfur-containing ammonia wastewater treatment process according to claim 1, wherein the water injected in S4 is demineralized water.
CN202310568568.2A 2023-05-19 2023-05-19 Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process Active CN116637606B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310568568.2A CN116637606B (en) 2023-05-19 2023-05-19 Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310568568.2A CN116637606B (en) 2023-05-19 2023-05-19 Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process

Publications (2)

Publication Number Publication Date
CN116637606A true CN116637606A (en) 2023-08-25
CN116637606B CN116637606B (en) 2024-10-01

Family

ID=87622349

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310568568.2A Active CN116637606B (en) 2023-05-19 2023-05-19 Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process

Country Status (1)

Country Link
CN (1) CN116637606B (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1562789A (en) * 2004-03-25 2005-01-12 南京大学 Reclaiming technique by using resin to adsorb nitro chlorobenzene in wastewater from producing nitro chlorobenzene
CN110252269A (en) * 2019-06-13 2019-09-20 江苏南大环保科技有限公司 A kind of resin regeneration method for handling containing high-boiling components waste water
CN110252268A (en) * 2019-06-13 2019-09-20 江苏南大环保科技有限公司 A kind of regeneration method of chlorobenzene production waste water absorption resin
CN110975851A (en) * 2019-12-26 2020-04-10 江苏南大环保科技有限公司 Resin desorption regeneration method for adsorbing organic matters
CN115974321A (en) * 2022-12-30 2023-04-18 陕西延长中煤榆林能源化工有限公司 Sewage treatment system and method for heavy oil catalytic thermal cracking DCC device

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1562789A (en) * 2004-03-25 2005-01-12 南京大学 Reclaiming technique by using resin to adsorb nitro chlorobenzene in wastewater from producing nitro chlorobenzene
CN110252269A (en) * 2019-06-13 2019-09-20 江苏南大环保科技有限公司 A kind of resin regeneration method for handling containing high-boiling components waste water
CN110252268A (en) * 2019-06-13 2019-09-20 江苏南大环保科技有限公司 A kind of regeneration method of chlorobenzene production waste water absorption resin
CN110975851A (en) * 2019-12-26 2020-04-10 江苏南大环保科技有限公司 Resin desorption regeneration method for adsorbing organic matters
CN115974321A (en) * 2022-12-30 2023-04-18 陕西延长中煤榆林能源化工有限公司 Sewage treatment system and method for heavy oil catalytic thermal cracking DCC device

Also Published As

Publication number Publication date
CN116637606B (en) 2024-10-01

Similar Documents

Publication Publication Date Title
US8187991B2 (en) Methods for regeneration of adsorbent material
CN103055704B (en) Regeneration method of performance of immersion-type ultrafiltration membrane used in reclaimed water recycling
CN116637606B (en) Regeneration method of resin adsorption bed layer in sulfur-ammonia-containing sewage treatment process
CN110787512A (en) Pickling process for metal filter element
US20160214861A1 (en) Method and apparatus for producing hydrochloric acid
CN110559793A (en) Novel method for removing mercury from renewable natural gas
CN109382043A (en) The in situ regeneration method of Fischer-Tropsch synthesis device filter element and the F- T synthesis system of application in situ regeneration method
JP2010194392A (en) Method of removing sludge during cleaning oil tank using common oil
CN104193034B (en) A kind of amine purification processes system
KR101434437B1 (en) Re-generating system and method of used-catalyst for RHDS and VRHDS desulfurization
CN115974321A (en) Sewage treatment system and method for heavy oil catalytic thermal cracking DCC device
JP2018043220A (en) Cleaning/regeneration method and cleaning/regeneration device for desulfurization tower of gas to be processed
KR20110102724A (en) A system phosphorus chemisorption and collection and method using it
CN110743215A (en) Sewage filter
CN106277155B (en) Deep purification method for sewage
CN114849792A (en) Heavy oil hydrocracking catalyst regeneration device and method
CN111995096A (en) Ternary precursor wastewater oil removal system and process method thereof
CN215161840U (en) High-temperature condensed water deoiling and deironing treatment device
JP2010194391A (en) Strainer for sludge recovery
JP5086742B2 (en) Water treatment method
KR200234658Y1 (en) VOCs remove apparatus using cartridge type AC/ACF and solvent recovery and regeneration apparatus thereof
CN208912092U (en) A kind of strongly basic anionic resin activation system
KR101798623B1 (en) the method for recycling BTX absorption oil in coke gas refining process
KR100759387B1 (en) Ion-Exchange Filter System
CN106395979B (en) Cyclonic separation water treatment facilities and method for treating water

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
CB03 Change of inventor or designer information

Inventor after: Liu Shenghai

Inventor after: Ma Jipeng

Inventor after: Ai Xiaobing

Inventor after: Hao Yong

Inventor after: Liu Jianming

Inventor after: Wang Jiangpeng

Inventor after: Wang Qiang

Inventor before: Ma Jipeng

Inventor before: Liu Shenghai

Inventor before: Ai Xiaobing

Inventor before: Hao Yong

Inventor before: Liu Jianming

Inventor before: Wang Jiangpeng

Inventor before: Wang Qiang

CB03 Change of inventor or designer information
GR01 Patent grant
GR01 Patent grant