[go: up one dir, main page]
More Web Proxy on the site http://driver.im/

CN112678904A - Scale cleaning device and method for multistage flash evaporation seawater desalination system - Google Patents

Scale cleaning device and method for multistage flash evaporation seawater desalination system Download PDF

Info

Publication number
CN112678904A
CN112678904A CN202011216530.1A CN202011216530A CN112678904A CN 112678904 A CN112678904 A CN 112678904A CN 202011216530 A CN202011216530 A CN 202011216530A CN 112678904 A CN112678904 A CN 112678904A
Authority
CN
China
Prior art keywords
brine
module
flash
flash chamber
stage
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
CN202011216530.1A
Other languages
Chinese (zh)
Other versions
CN112678904B (en
Inventor
黄秋云
江爱朋
陈云
何璐
王剑
张涵羽
姜周曙
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.)
Hangzhou Dianzi University
Original Assignee
Hangzhou Dianzi University
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 Hangzhou Dianzi University filed Critical Hangzhou Dianzi University
Priority to CN202011216530.1A priority Critical patent/CN112678904B/en
Publication of CN112678904A publication Critical patent/CN112678904A/en
Application granted granted Critical
Publication of CN112678904B publication Critical patent/CN112678904B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination

Landscapes

  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)

Abstract

The invention relates to a device and a method for cleaning scale of a multistage flash evaporation seawater desalination system, which are characterized in that structural parameters, necessary coefficients and a data acquisition period of the multistage flash evaporation seawater desalination system are given through a human-computer interaction module; the parameters are acquired by a data acquisition module and are sent to a central processing module through an A/D and D/A conversion module; and the central processing module calls the simulation calculation module according to the problem model stored in the central processing module and sends the calculated parameters to the parameter decision module. The parameter decision module estimates the scaling degree of the current system and the next cleaning time of the system, the simulation calculation module and the parameter decision module send the calculation data to the central processing module, and the central processing module arranges the data and sends the data to the display module. And real-time data acquisition is carried out, and the model is used for calculating to obtain the system scaling coefficient so as to judge the scaling condition of the system and guide a factory to carry out corresponding scaling treatment in time and keep the excellent performance of the system.

Description

Scale cleaning device and method for multistage flash evaporation seawater desalination system
Technical Field
The invention belongs to the technical field of chemical production process control, and particularly relates to a device and a method for cleaning scale in a multistage flash evaporation seawater desalination system.
Background
The multistage flash evaporation is the most mature technology in the seawater desalination industry, has the highest operation safety and large elasticity, and is suitable for large-scale and ultra-large-scale desalination devices. Will continue to play an important role in the future field of seawater desalination.
The MSF seawater desalination device has two classical structures, namely a straight-Through Multistage Flash (OT-MSF) seawater desalination device and a Brine circulating Multistage Flash (BR-MSF) seawater desalination device. The OT-MSF device is of simpler construction, while BR-MSF is more commonly used because of its better overall effect. The BR-MSF device consists of a brine heater, a heat recovery section, a heat discharge section and a mixing and separating module. The classical structure flow of the multi-stage flash seawater desalination system is shown in figure 1. The raw seawater firstly enters a heat discharge section, and is preheated and simultaneously condenses steam generated in a flash evaporation chamber. The feed seawater is divided into two parts after being preheated by the heat discharge section, one part returns to the sea, the other part is mixed with the circulating brine and then is pumped into the tail end of the heat recovery section, when the feed seawater flows through a series of heat exchangers from right to left, the feed seawater is gradually heated, and steam flashed out from the flash evaporation chamber is condensed. Finally, the seawater exits the heat exchanger in the first stage flash chamber of the heat recovery section, flows into a brine heater to be further heated, and flows into the first stage flash chamber in the form of hot brine. Because the pressure in the flash chamber is controlled to be lower than the saturated vapor pressure corresponding to the temperature of the hot brine, the hot brine is changed into superheated water after entering the flash chamber and is gasified partially rapidly, and the generated vapor meets the condensing pipe and is condensed and then drops into the fresh water tray. Repeating the steps until the last stage, discharging the strong brine and extracting the fresh water.
Circulating brine in the multistage flash evaporation process is heated by a preheater, and because the salinity, the hardness, the total solid solution and other impurities in the seawater are high, the solubility of certain components can reach supersaturation, so that the seawater is easy to scale on a heat exchange surface of a multistage flash evaporation seawater desalination device, and the method becomes one of the main problems faced by the hot method seawater desalination. The existence of dirt not only increases the fluid resistance, increases the energy consumption and reduces the heat transfer efficiency, but also blocks the pipeline in serious cases to cause the equipment to be paralyzed. However, the performance of the multistage flash evaporation seawater desalination system is influenced by not only dirt parameters but also the flow rate and salinity of the feed seawater, the amount of circulating strong brine, the highest temperature of brine, parameters of a brine heater and the like in the operation process, so that the water production performance is variable. In the operation process of the system, the scaling characteristic of the system cannot be directly measured, and the cleaning and maintenance of the system are generally operated based on experience and lack of scientific basis.
The invention can calculate the scale factor of the current system through the model according to the input and output operation data of the real-time operation of the system, thereby obtaining the scale degree of the system and providing the corresponding system maintenance and scale treatment method.
Disclosure of Invention
The invention aims to provide a cleaning operation guide by estimating the scaling coefficient of the scaling characteristic on line.
The descaling basis of the traditional multistage flash evaporation seawater desalination device is that the water yield and the water generation ratio are far lower than the standard value or the system performance has serious problems, the device may have irreversible damage to the service life cycle of the device, and the device is also tested when being put into production again. The invention discloses estimation and maintenance decision of scaling characteristic parameters of a thermal seawater desalination system, and relates to soft measurement of scaling parameters and guidance of system cleaning operation by calculating heat transfer coefficient and water production performance under the condition of combining physics and modeling. And real-time data acquisition is carried out, and the model is used for calculating to obtain the system scaling coefficient so as to judge the scaling condition of the system and guide a factory to carry out corresponding scaling treatment in time and keep the excellent performance of the system.
A scale cleaning device of a multistage flash evaporation seawater desalination system comprises a sensor module, a data acquisition module, a man-machine interaction module, a simulation calculation module, an A/D and D/A conversion module, a central processing module, a parameter decision module and a display module; the sensor module comprises five flow sensors, four temperature sensors and two seawater salinity sensors; the data acquisition module is used for acquiring the temperature and the salt content of the feed seawater, the fresh water flow, the circulating brine and the heat discharge seawater flow obtained by the sensor module, and the heating steam flow and the temperature; the human-computer interaction module is used for setting the structural parameters of flash chambers at all levels of the multi-level flash seawater desalination system, the parameters of a brine heater and the data acquisition period; the A/D and D/A conversion module is used for converting the received analog quantity into a corresponding digital quantity or converting the received digital quantity into a corresponding analog quantity; the central processing module is used for storing a scaling coefficient processing problem model of the multi-stage flash seawater desalination system and required physical parameters, receiving and storing data acquired by the data acquisition module through the A/D and D/A conversion module, receiving and storing data obtained by processing of the analog computation module and the parameter decision module, and then transmitting the data to the display module; the simulation calculation module calls a system program to calculate according to the currently acquired data to obtain the scaling coefficient f of the current brine heaterBHFouling factor f of flash chamberj(j is 1,2, …, n is the number of the system flash chamber stages), the water making ratio GOR and the daily operation cost TOC, and the parameters are transmitted to a display module; the parameter decision module analyzes the data stored in the simulation calculation module before, estimates the system scaling degree and the next system cleaning time, and transmits the parameters to the display module; and the display module displays the calculation results of the simulation calculation module and the parameter decision module.
A method for cleaning scale in a multistage flash seawater desalination system comprises the following steps: firstly, an engineer sets the structural parameters of the multistage flash seawater desalination system through a human-computer interaction module, and sets an operation period. Thereafter the device collects the required data in a given cycle, andthe analog signals are sent to a central processing module through an A/D and D/A conversion module, and the central processing module calls an analog calculation module. The simulation calculation module obtains the scaling coefficient f of the brine heater of the current system by calculating the model problem in the central processing moduleBHAnd fouling factor f of flash chamberjGOR (water production ratio), and TOC (total organic carbon) of daily operation cost. And the parameter decision module performs comparison and analysis according to the parameters obtained by the simulation calculation module to obtain the scaling degree of the current system and the next system cleaning time and sends the relevant theory to the system display module. The device repeats the data acquisition, the analog calculation and the comparative analysis process in the next operation period, and continuously estimates the system scaling degree in real time.
The method specifically comprises the following steps:
step A1: an operator or an engineer gives structural parameters, physical property coefficients and a data acquisition period Tc of the multistage flash seawater desalination system through a man-machine interaction module;
step A2: collecting the flow W of the cooling brine entering the hot discharge section at the current time point by using a data collection moduleFFlow rate W of circulating seawaterReHeating steam flow rate WsteamFlow rate W of flash brineBFlash evaporation fresh water flow WDTemperature T of feed seawaterseaTemperature T of heating steamsteamTemperature T of flash brineBFlash fresh water temperature TDFeed brine concentration CFConcentration of flash brine CB. Recording the current time, making a variable T1 equal to the current time, and then sending the parameters to a central processing module through an A/D and D/A conversion module;
step A3: the central processing module calls the simulation calculation module according to the internally stored stable state simulation and daily operation cost model of the multi-stage flash seawater desalination device, so as to calculate the scaling coefficient f of the brine heater at the current T1 momentBHFouling factor f of flash chamberjThe water making ratio GOR and the daily operation cost TOC, and then the parameters are sent to the parameter decision module.
Step A4: the parameter decision module makes the parameter set L obtained in the period1(fBH,fjGOR, TOC) andparameter set L obtained in previous periodsi(fBH,fjGOR, TOC) ((i ═ 1,2, …, m); m is the current period number), the scaling degree of the current system and the next cleaning time of the system are estimated, and the simulation calculation module and the parameter decision module send the calculation data to the central processing module.
Step A5: the central processing module arranges the data and sends the data to the display module, and the display module displays the current time T1 and the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjThe water making ratio GOR, the daily running cost TOC, the system scaling degree and the system cleaning time Tim.
Step A6: recording the current time as T2, and if T2-T1< Tc, continuing to wait; otherwise, go to step A2, and resume data acquisition.
The model of the multistage flash evaporation seawater desalination device in the central processing module for stable state simulation and daily operation cost consists of the formulas (1) to (38);
the steady-state model of the multi-stage flash evaporation seawater desalination device consists of a flash chamber equation, a brine heater equation, a mixing and separating equation and a physical property parameter equation. For the j-th-stage flash chamber, the flash chamber module model consists of the following formulas (1) to (8):
WBj-1+WDj-1=WBj+WDj (1);
WBj-1CBj-1=WBjCBj (2);
WBj-1hBj-1=WBjhBj+VBjhVj (3);
WBj-1-WBj=VBj (4);
Figure BDA0002760582980000041
Figure BDA0002760582980000042
wherein, WBjRepresents the mass flow of flashed brine, W, of the j stageBj-1Represents the mass flow of the flashed brine, W, of the j-1 th stageDjThe mass flow of fresh water W representing the j-th outputDj-1Represents the flash brine mass flow for stage j-1. CBjDenotes the flash brine concentration of the j stage, CBj-1Indicating the flash brine concentration for stage j-1. h isBjRepresents the specific enthalpy, h, of the j-th stage flash brineBj-1Represents the specific enthalpy, h, of the j-1 th stage flash brineVjSpecific enthalpy, V, of the j-th stage flash steamBjAnd the evaporation capacity of the brine in the j-stage flash chamber is shown. WFIndicating the mass flow, CP, of the chilled brine entering the hot discharge sectionRjDenotes the heat capacity, CP, of the cooled brine leaving the j-th stage flash chamberDjDenotes the specific heat capacity, CP, of fresh water leaving the j-th stage flash chamberDj-1Denotes the specific heat capacity, CP, of fresh water leaving the j-1 stage flash chamberBjDenotes the specific heat capacity, CP, of the flashed brine leaving the j-th stage flash chamberBj-1Denotes the specific heat capacity, T, of the flashed brine leaving the j-1 stage flash chamberFjIndicating the temperature, T, of the cooled brine leaving the j-th stage flash chamberFj+1Indicating the temperature, T, of the chilled brine entering the j-th stage flash chamberBjIndicating the temperature, T, of brine leaving the j-th stage flash chamberBj-1Indicating the temperature, T, of the brine leaving the j-1 stage flash chamberDjRepresenting the temperature, T, of the fresh water leaving the j-th flash chamberDj-1The temperature of the fresh water leaving the flash chamber of the j-1 th stage is shown, and T represents the flash reference temperature in an ideal state. A. thejThe heat transfer area of the j-th stage flash chamber is shown,
Figure BDA0002760582980000043
denotes the heat transfer coefficient of the j-th stage flash chamber, wherein W denotes the feed flow rate of the j-th stage flash chamber, and W is W for the heat discharge sectionFDenotes the feed seawater flow rate, and W ═ W for the heat recovery sectionRThe feed flow rate to the heat recovery section is indicated,
Figure BDA0002760582980000044
the outer diameter of each stage of the steaming chamber is expressed,
Figure BDA0002760582980000045
representing the internal diameter of the condenser tube of each stage of flash chamber, DiThe inner diameter is expressed, and the specific formula is expanded in the physical property equation part.
TBj=TDj+ΔBPEj+ΔNETDj+ΔTLj (7);
TVj=TDj+ΔTLj (8);
Wherein, Δ BPEjDenotes the boiling point rise of the j-th brine, Δ NETDjDenotes the unbalance margin, Δ TLjRepresenting the temperature loss through the demister and condenser. T isVjIndicating the flash vapor temperature of the flash chamber of stage j.
The brine heater module model consists of equations (9) - (12):
WB0=WR (9);
CB0=CR (10);
WRCPRH(TB0-TF1)=Wsteamλs (11);
wherein,
Figure BDA0002760582980000051
Figure BDA0002760582980000052
wherein, WB0Represents the mass flow of flashed brine, W, exiting the brine heaterRRepresenting the mass flow of chilled brine into the heat recovery section. CB0Represents the concentration of flashed brine, C, entering the brine heaterRIndicating the concentration of chilled brine entering the heat recovery section. CP (CP)RHIndicating the cooling brine heat capacity, T, into the brine heaterB0Represents the temperature of the flashed brine, W, exiting the brine heatersteamExpressed as heating steam mass flow, lambdasRepresenting the latent heat of vapour, TsteamExpressed as brine heater steam temperature. A. theHTo representThe heat transfer area of the brine heater,
Figure BDA0002760582980000053
denotes the heat transfer coefficient of the brine heater, wherein W denotes the feed flow W of the brine heaterR
Figure BDA0002760582980000054
The outside diameter of the brine heater is shown,
Figure BDA0002760582980000055
the inner diameter of the condensation pipe of the brine heater is expressed, and a specific formula is developed in a physical property equation part.
The mixed separation module model is composed of formulas (13) to (20):
WBD=WBN-WRe (13);
Wm=WF-Wr (14);
S=Wr-Cw (15);
WR=WRe+Wm (16);
WR·CR=WRe·CRe+Wm·Cm (17);
WR·hR=WRe·hRe+Wm·hm (18);
WF=S+WS (19);
Figure BDA0002760582980000056
wherein WBDRepresents the mass flow of the waste seawater, WBNRepresenting the mass flow of brine, W, leaving the last stage flash chamberReRepresenting the circulating brine mass flow. WmRepresents the mass flow of make-up brine, WrRepresenting the hot effluent seawater mass flow. S represents the return flow rate of the hot discharge section, CwRepresenting the mass flow of brine exiting the hot discharge section. CReIndicating circulating saltWater concentration, CmIndicating the make-up brine concentration. h isRRepresents the specific enthalpy of the brine entering the heat recovery section, hReDenotes the specific enthalpy of the circulating brine, hmIndicating the make-up brine specific enthalpy. WSRepresenting the feed seawater mass flow.
Figure BDA0002760582980000057
Represents the specific enthalpy of the brine at the inlet of the heat discharge section, hSRepresenting the specific enthalpy of the returned brine in the heat discharge section,
Figure BDA0002760582980000058
representing the feed seawater specific enthalpy.
The physical property parameter equation model is composed of equations (21) to (31):
Figure BDA0002760582980000059
CPB=[1-CB(0.011311-1.146×10-5TB)]×CPD (22);
hV=596.912+0.46694TS-0.000460256TS 2 (23);
hB=CPB·TB (24);
hD=CPD·TD (25);
Figure BDA0002760582980000061
wherein CC ═ (19.819C)B)/(1-CB) CC denotes concentration conversion, CBIndicating the flash brine concentration.
Figure BDA0002760582980000062
Wherein, ω isj=WF/wj,ωjIndicating the mass per unit length of cooling brine entering the hot discharge section at the j-th stageFlow rate, wjThe width of the condensation pipe of the j-th stage flash chamber is shown.
TL=exp(1.885-0.02063TD)/1.8 (28);
U=4.8857/(y+z+4.8857f) (29);
y=[0.0013(v×Di)0.2]/[(0.2018+0.0031×T)v] (30);
Figure BDA0002760582980000063
GOR=WDN/Wsteam (32);
Wherein CPDThe specific heat capacity of the fresh water in the flash chamber is shown. CP (CP)BIndicating the specific heat capacity of brine in the flash chamber, CBDenotes the flash brine concentration, TBIndicating the flash brine temperature. h isvRepresents the enthalpy of the steam, TSIs the steam temperature. h isBIndicating the enthalpy of the brine. h isDRepresents the enthalpy value, T, of fresh waterDRepresenting the fresh water temperature. BPE indicates the brine boiling point rise, where T indicates the brine temperature in the flash chamber or brine heater. NETD denotes the non-equilibrium temperature difference, HjDenotes the flash brine level, wjDenotes the width, Δ T, of the condensing tube of the j-th stage flash chamberBRepresenting the brine temperature difference between the two stages. TL represents the temperature loss through the demister and condenser tube. U represents the heat transfer coefficient of the brine heater or flash chambers of each stage. y is an intermediate expression relating to the flow rate in the tubes, the brine temperature and the diameter in the condenser tubes, z is an intermediate expression relating to the fresh water temperature in the flash chamber, y and z are simply calculations, and f is the fouling factor of the brine heater or the flash chamber. v represents the flow velocity in the tube, DiDenotes the internal diameter of the condenser tube and T denotes the temperature of the brine at the outlet of the heat exchanger. WDNThe mass flow of the total fresh water in the flash chamber is represented, and GOR represents the water production Ratio (gain Output Ratio) is a key index of the performance of the reaction system.
The daily running cost module model is composed of equations (33) to (38):
C1=22×Wsteam×[(Tsteam-40)/85]×0.00415 (33);
C2=22×(DNw)×0.109 (34);
C3=22×(DNw)×0.082 (35);
C4=22×(DNb)×0.024 (36);
C5=22×(DNw)×0.1 (37);
TOC=C1+C2+C3+C4+C5 (38);
wherein, C1 represents the heating steam cost, C2 represents the electric energy cost consumed by the device, C3 represents the maintenance and idle cost, C4 represents the pretreatment cost, C5 represents the labor cost, and TOC represents the daily operating cost of the system. DNRepresenting the total fresh water production, pwDenotes the pure water density, ρbRepresents the density of the brine.
The simulation calculation module solves the steady-state simulation problem formed by the calculation formulas (1) to (38) by using a quasi-Newton method to determine the scaling coefficient f of the brine heater of the current systemBHFouling factor f of flash chamber in heat recovery section and heat discharge sectionjThe specific steps of the method are as follows:
step B1: the equations of the above equations (1) to (38) for obtaining the unknown quantity are organized into a nonlinear equation system, which is expressed by the following equation (39):
Figure BDA0002760582980000071
the representation of the vector is:
G(x)=0 (40);
here, x ═ x (x)1,x2,…,xp)T,G=(g1,g2,…,gq)T,gi(i=1,2,…,q):Rn→R。
Wherein x is1,x2,…,xpP unknowns representing the system of nonlinear equations, and x represents a matrix of p x 1 dimensions formed by the unknowns of the system of equations. g1,g2,…,gqRepresenting a constituent nonlinear squareThe q equations of the set of equations, G, represent a q × p dimensional matrix of equations of the set of nonlinear equations.
Step B2: let the initial iteration number k equal to 0, set the initial value x0∈RnInitial quasi-Newton matrix BkThe unit matrix is in dimension p multiplied by p, the calculation precision of the function value is epsilon, and the precision of the minimum step length is delta.
Step B3: calculating search direction vector d under iteration times kkTo get the value of the next point:
xk+1=xk+dk (41);
dk=-BkΔG(xk) (42);
step B4: calculate G (x)k) And G (x)k+1) If G (x)k+1) | | < epsilon or | | | xk+1-xkIf | | < delta, terminating the iteration to obtain the solution of the nonlinear equation set and the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjGOR (water production ratio), TOC (total organic carbon) of daily operation cost; otherwise, go to step B5.
Step B5: by modifying BkTo obtain Bk+1
Figure BDA0002760582980000081
Wherein s isk=xk+1-xk,yk=ΔG(xk+1)-ΔG(xk)。xkDenotes the value, x, evaluated at the k-th iterationk+1Denotes the value, s, evaluated in the (k + 1) th iterationkThe difference between the two evaluated values is indicated. Δ G (x)k+1) Represents G (x)k+1) Gradient vector of, Δ G (x)k) Represents G (x)k) Gradient vector of, ykThe gradient vector difference for the (k + 1) th iteration and the k iterations is expressed.
Step B6: let k ═ k +1, go to step B3 for calculation.
The parameter decision module is used for obtaining the scaling coefficient f of the brine heater at all time points according to the simulation calculation moduleBHFouling factor f of flash chamberjWater producing ratioGOR and daily running cost TOC adopt the least square method to carry out fitting and analysis, carry out reasonable judgement to system's scale deposit degree, and the concrete step is as follows:
step C1: inheriting all data of the analog calculation module from the beginning of data acquisition and aiming at the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjGOR (water production ratio), TOC (total organic carbon) of daily operating cost and scaling coefficient f of brine heaterBHSetting the upper limit H1Fouling factor f of flash chamberjSetting the upper limit H2The water making ratio GOR sets the lower limit X1Daily operating cost TOC setting upper limit X2
Step C2: dividing the data into four parts to be fitted respectively, and firstly, fitting the scaling coefficient f of the brine heaterBHAnd (4) performing curve fitting by using a least square method. Suppose a given collected data point (xx)i,yyi)(i=0,1,…,m),xxiRepresenting data acquisition time points Ti,yyiRepresents the scaling coefficient f of the brine heater collected at each time pointBH(i) In that respect The fitting polynomial is
Figure BDA0002760582980000082
To ensure that the module computation speed makes the polynomial order nn equal to 3, so that
Figure BDA0002760582980000083
Wherein I is a0,a1,a2,a3So that the above problem is to find I ═ I (a)0,a1,a2,a3) The extreme value problem of (2).
Step C3: obtaining the necessary condition of extremum by multivariate function
Figure BDA0002760582980000091
Namely, it is
Figure BDA0002760582980000092
Step C4: the formula (46) is rewritten into a normal equation system form
Figure BDA0002760582980000093
It can be shown that the coefficient matrix of the normal equation set (47) is a symmetric positive definite matrix, so that there is a unique solution. Is solved from formula (47) to obtain akk( kk 0,1, …,3), thereby obtaining a polynomial
Figure BDA0002760582980000094
Step C5: repeating the steps C2 to C4 to respectively obtain the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjThe water production ratio GOR and the daily running cost TOC are fitted curves of the running time of the system, and the fitted curve is P1(t)、P2(t)、P3(t) and P4(t), wherein t represents time.
Step C6: judging whether the current system needs to be cleaned according to the upper and lower limits set by the parameters and the four obtained fitted curves, and deducing the time point Tim to be cleaned of the system under the 4 indexes according to a fitted equation1、Tim2、Tim3、Tim4
Step C7: mixing Tim1、Tim2、Tim3、Tim4And comparing to obtain the latest time node which is recorded as Tim, wherein the time point is the next time point to be cleaned of the system.
Step C8: fouling factor f for brine heaterBHFouling factor f of flash chamberjThe scale of the system can be obtained according to the numerical value of the current data acquisition point.
Drawings
FIG. 1 is a block diagram of a multi-stage flash seawater desalination system according to the present invention;
FIG. 2 is a schematic view of the overall structure of the present invention;
FIG. 3 is a flow chart of the operation of the present invention;
FIG. 4 is a flow diagram of a simulation calculation module;
FIG. 5 is a flow chart of a parameter decision module.
Detailed Description
The invention is further analyzed with reference to the following figures and specific examples.
As shown in fig. 2, the scaling treatment device of the multistage flash seawater desalination system comprises a sensor module, a data acquisition module, a man-machine interaction module, a simulation calculation module, an a/D and D/a conversion module, a central processing module, a parameter decision module and a display module; the sensor module comprises five flow sensors, four temperature sensors and two seawater salinity sensors; the data acquisition module is used for acquiring the temperature and the salt content of the feed seawater, the fresh water flow, the circulating brine and the heat discharge seawater flow obtained by the sensor module, and the heating steam flow and the temperature; the human-computer interaction module is used for setting the structural parameters of flash chambers at all levels of the multi-level flash seawater desalination system, the parameters of a brine heater and the data acquisition period; the A/D and D/A conversion module is used for converting the received analog quantity into a corresponding digital quantity or converting the received digital quantity into a corresponding analog quantity; the central processing module is used for storing a scaling coefficient processing problem model of the multi-stage flash seawater desalination system and required physical parameters, receiving and storing data acquired by the data acquisition module through the A/D and D/A conversion module, receiving and storing data obtained by processing of the analog computation module and the parameter decision module, and then transmitting the data to the display module; the simulation calculation module calls a system program to calculate according to the currently acquired data to obtain the scaling coefficient f of the current brine heaterBHFouling factor f of flash chamberj(j is 1,2, …, n is the number of the system flash chamber stages), the water making ratio GOR and the daily operation cost TOC, and the parameters are transmitted to a display module; the parameter decision module analyzes the data stored in the simulation calculation module before to estimate the system scaling degree and the next system cleaningWashing time and transmitting the parameters to a display module; and the display module displays the calculation results of the simulation calculation module and the parameter decision module.
As shown in fig. 3, for a multi-stage flash seawater desalination system using the present invention, in order to estimate the scaling degree of the system on-line and perform the corresponding treatment, the following steps are required:
a1, a user or an engineer gives structural parameters of the multistage flash evaporation seawater desalination system through a human-computer interaction module, wherein the structural parameters comprise a heat recovery section stage number NR equal to 16 and a heat discharge section stage number NJ equal to 3; the size of the brine heater, the flash chamber and other important coefficients; setting a data acquisition period Tc to be 2 hours;
step A2: collecting the flow W of the cooling brine entering the hot discharge section at the current time point by using a data collection moduleFFlow rate W of circulating seawaterReHeating steam flow rate WsteamFlow rate W of flash brineBFlash evaporation fresh water flow WDTemperature T of feed seawaterseaTemperature T of heating steamsteamTemperature T of flash brineBFlash fresh water temperature TDFeed brine concentration CFConcentration of flash brine CB. Recording the current time, making a variable T1 equal to the current time, and then sending the parameters to a central processing module through an A/D and D/A conversion module;
step A3: the central processing module calls the simulation calculation module according to the internally stored stable state simulation and daily operation cost model of the multi-stage flash seawater desalination device, so as to calculate the scaling coefficient f of the brine heater at the current T1 momentBHFouling factor f of flash chamberjThe water making ratio GOR and the daily operation cost TOC, and then the parameters are sent to the parameter decision module.
Step A4: the parameter decision module makes the parameter set L obtained in the period1(fBH,fjGOR, TOC) and the parameter set L obtained in the previous cyclesi(fBH,fjGOR, TOC) ((i ═ 1,2, …, m); m is the current period number), the scaling degree of the current system and the next time of cleaning the system are estimated, and a simulation calculation module and a parameter decision module are used for simulationThe block sends its calculation data to the central processing module.
Step A5: the central processing module arranges the data and sends the data to the display module, and the display module displays the current time T1 and the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjThe water making ratio GOR, the daily running cost TOC, the system scaling degree and the system cleaning time Tim.
Step A6: recording the current time as T2, and if T2-T1< Tc, continuing to wait; otherwise, go to step A2, and resume data acquisition.
The model of the multistage flash evaporation seawater desalination device in the central processing module for stable state simulation and daily operation cost is composed of the following formulas (1) to (38):
the steady-state model of the multi-stage flash evaporation seawater desalination device consists of a flash chamber equation, a brine heater equation, a mixing and separating equation and a physical property parameter equation. For the j-stage flash chamber, the flash chamber module model consists of the following formulas (1) to (8)
WBj-1+WDj-1=WBj+WDj (1);
WBj-1CBj-1=WBjCBj (2);
WBj-1hBj-1=WBjhBj+VBjhVj (3);
WBj-1-WBj=VBj (4);
Figure BDA0002760582980000111
Figure BDA0002760582980000112
Wherein, WBjRepresents the mass flow of flashed brine, W, of the j stageBj-1Represents the mass flow of the flashed brine, W, of the j-1 th stageDjThe mass flow of fresh water W representing the j-th outputDj-1Represents the flash brine mass flow for stage j-1. CBjDenotes the flash brine concentration of the j stage, CBj-1Indicating the flash brine concentration for stage j-1. h isBjRepresents the specific enthalpy, h, of the j-th stage flash brineBj-1Represents the specific enthalpy, h, of the j-1 th stage flash brineVjSpecific enthalpy, V, of the j-th stage flash steamBjAnd the evaporation capacity of the brine in the j-stage flash chamber is shown. WFIndicating the mass flow, CP, of the chilled brine entering the hot discharge sectionRjDenotes the heat capacity, CP, of the cooled brine leaving the j-th stage flash chamberDjDenotes the specific heat capacity, CP, of fresh water leaving the j-th stage flash chamberDj-1Denotes the specific heat capacity, CP, of fresh water leaving the j-1 stage flash chamberBjDenotes the specific heat capacity, CP, of the flashed brine leaving the j-th stage flash chamberBj-1Denotes the specific heat capacity, T, of the flashed brine leaving the j-1 stage flash chamberFjIndicating the temperature, T, of the cooled brine leaving the j-th stage flash chamberFj+1Indicating the temperature, T, of the chilled brine entering the j-th stage flash chamberBjIndicating the temperature, T, of brine leaving the j-th stage flash chamberBj-1Indicating the temperature, T, of the brine leaving the j-1 stage flash chamberDjRepresenting the temperature, T, of the fresh water leaving the j-th flash chamberDj-1The temperature of the fresh water leaving the flash chamber of the j-1 th stage is shown, and T represents the flash reference temperature in an ideal state. A. thejThe heat transfer area of the j-th stage flash chamber is shown,
Figure BDA0002760582980000121
denotes the heat transfer coefficient of the j-th stage flash chamber, wherein W denotes the feed flow rate of the j-th stage flash chamber, and W is W for the heat discharge sectionFDenotes the feed seawater flow rate, and W ═ W for the heat recovery sectionRThe feed flow rate to the heat recovery section is indicated,
Figure BDA0002760582980000122
the outer diameter of each stage of the steaming chamber is expressed,
Figure BDA0002760582980000123
representing the internal diameter of the condenser tube of each stage of flash chamber, DiThe inner diameter is expressed, and the specific formula is expanded in the physical property equation part.
TBj=TDj+ΔBPEj+ΔNETDj+ΔTLj (7);
TVj=TDj+ΔTLj (8);
Wherein, Δ BPEjDenotes the boiling point rise of the j-th brine, Δ NETDjDenotes the unbalance margin, Δ TLjRepresenting the temperature loss through the demister and condenser. T isVjIndicating the flash vapor temperature of the flash chamber of stage j.
The brine heater module model consists of equations (9) - (12):
WB0=WR (9);
CB0=CR (10);
WRCPRH(TB0-TF1)=Wsteamλs (11);
wherein,
Figure BDA0002760582980000124
Figure BDA0002760582980000125
wherein WB0Represents the mass flow of flashed brine, W, exiting the brine heaterRRepresenting the mass flow of chilled brine into the heat recovery section. CB0Represents the concentration of flashed brine, C, entering the brine heaterRIndicating the concentration of chilled brine entering the heat recovery section. CP (CP)RHIndicating the cooling brine heat capacity, T, into the brine heaterB0Represents the temperature of the flashed brine, W, exiting the brine heatersteamExpressed as heating steam mass flow, lambdasRepresenting the latent heat of vapour, TsteamExpressed as brine heater steam temperature. A. theHThe heat transfer area of the brine heater is shown,
Figure BDA0002760582980000126
denotes the heat transfer coefficient of the brine heater, wherein W denotes the feed flow W of the brine heaterR
Figure BDA0002760582980000127
The outside diameter of the brine heater is shown,
Figure BDA0002760582980000128
the inner diameter of the condensation pipe of the brine heater is expressed, and a specific formula is developed in a physical property equation part.
The mixed separation module model is composed of formulas (13) to (20):
WBD=WBN-WRe (13);
Wm=WF-Wr (14);
S=Wr-Cw (15);
WR=WRe+Wm (16);
WR·CR=WRe·CRe+Wm·Cm (17);
WR·hR=WRe·hRe+Wm·hm (18);
WF=S+WS (19);
Figure BDA0002760582980000131
wherein WBDRepresents the mass flow of the waste seawater, WBNRepresenting the mass flow of brine, W, leaving the last stage flash chamberReRepresenting the circulating brine mass flow. WmRepresents the mass flow of make-up brine, WrRepresenting the hot effluent seawater mass flow. S represents the return flow rate of the hot discharge section, CwRepresenting the mass flow of brine exiting the hot discharge section. CReDenotes circulating brine concentration, CmIndicating the make-up brine concentration. h isRRepresents the specific enthalpy of the brine entering the heat recovery section, hReDenotes the specific enthalpy of the circulating brine, hmIndicating the make-up brine specific enthalpy. WSRepresenting the feed seawater mass flow.
Figure BDA0002760582980000132
Represents the specific enthalpy of the brine at the inlet of the heat discharge section, hSRepresenting the specific enthalpy of the returned brine in the heat discharge section,
Figure BDA0002760582980000133
representing the feed seawater specific enthalpy.
The physical property parameter equation model is composed of equations (21) to (31):
Figure BDA0002760582980000134
CPB=[1-CB(0.011311-1.146×10-5TB)]×CPD (22);
hV=596.912+0.46694TS-0.000460256TS 2 (23);
hB=CPB·TB (24);
hD=CPD·TD (25);
Figure BDA0002760582980000135
wherein CC ═ (19.819C)B)/(1-CB) CC denotes concentration conversion, CBIndicating the flash brine concentration.
Figure BDA0002760582980000136
Wherein, ω isj=WF/wj,ωjDenotes the mass flow per unit length of the cooled brine entering the hot discharge section of the j-th stage, wjThe width of the condensation pipe of the j-th stage flash chamber is shown.
TL=exp(1.885-0.02063TD)/1.8 (28);
U=4.8857/(y+z+4.8857f) (29);
y=[0.0013(v×Di)0.2]/[(0.2018+0.0031×T)v] (30);
Figure BDA0002760582980000141
GOR=WDN/Wsteam (32);
Wherein CPDThe specific heat capacity of the fresh water in the flash chamber is shown. CP (CP)BIndicating the specific heat capacity of brine in the flash chamber, CBDenotes the flash brine concentration, TBIndicating the flash brine temperature. h isvRepresents the enthalpy of the steam, TSIs the steam temperature. h isBIndicating the enthalpy of the brine. h isDRepresents the enthalpy value, T, of fresh waterDRepresenting the fresh water temperature. BPE indicates the brine boiling point rise, where T indicates the brine temperature in the flash chamber or brine heater. NETD denotes the non-equilibrium temperature difference, HjDenotes the flash brine level, wjDenotes the width, Δ T, of the condensing tube of the j-th stage flash chamberBRepresenting the brine temperature difference between the two stages. TL represents the temperature loss through the demister and condenser tube. U represents the heat transfer coefficient of the brine heater or flash chambers of each stage. y is an intermediate expression relating to the flow rate in the tubes, the brine temperature and the diameter in the condenser tubes, z is an intermediate expression relating to the fresh water temperature in the flash chamber, y and z are simply calculations, and f is the fouling factor of the brine heater or the flash chamber. v represents the flow velocity in the tube, DiDenotes the internal diameter of the condenser tube and T denotes the temperature of the brine at the outlet of the heat exchanger. WDNThe mass flow of the total fresh water in the flash chamber is represented, and GOR represents the water production Ratio (gain Output Ratio) is a key index of the performance of the reaction system.
The daily running cost module model is composed of equations (33) to (38):
C1=22×Wsteam×[(Tsteam-40)/85]×0.00415 (33);
C2=22×(DNw)×0.109 (34);
C3=22×(DNw)×0.082 (35);
C4=22×(DNb)×0.024 (36);
C5=22×(DNw)×0.1 (37);
TOC=C1+C2+C3+C4+C5 (38);
wherein, C1 represents the heating steam cost, C2 represents the electric energy cost consumed by the device, C3 represents the maintenance and idle cost, C4 represents the pretreatment cost, C5 represents the labor cost, and TOC represents the daily operating cost of the system. DNRepresenting the total fresh water production, pwDenotes the pure water density, ρbRepresents the density of the brine.
The simulation calculation module solves the steady-state simulation problem formed by the calculation formulas (1) to (38) by using a quasi-Newton method to determine the scaling coefficient f of the brine heater of the current systemBHFouling factor f of flash chamber in heat recovery section and heat discharge sectionjThe specific steps of the method are as follows:
step B1: the equations of the above equations (1) to (38) for obtaining the unknown quantity are organized into a nonlinear equation system, which is expressed by the following equation (39):
Figure BDA0002760582980000151
the representation of the vector is:
G(x)=0 (40);
here, x ═ x (x)1,x2,…,xp)T,G=(g1,g2,…,gq)T,gi(i=1,2,…,q):Rn→R。
Wherein x is1,x2,…,xpP unknowns representing the system of nonlinear equations, and x represents a matrix of p x 1 dimensions formed by the unknowns of the system of equations. g1,g2,…,gqQ equations constituting the nonlinear equation system are expressed, and G denotes a matrix of q × p dimensions constituted by the equations of the nonlinear equation system.
Step B2: let the initial iteration number k equal to 0, set the initial value x0∈RnInitial quasi-Newton matrix BkIs in p × p dimension unitThe calculation precision of the matrix and the function value is epsilon, and the minimum step precision is delta.
Step B3: calculating search direction vector d under iteration times kkTo get the value of the next point:
xk+1=xk+dk (41);
dk=-BkΔG(xk) (42);
step B4: calculate G (x)k) And G (x)k+1) If G (x)k+1) | | < epsilon or | | | xk+1-xkIf | | < delta, terminating the iteration to obtain the solution of the nonlinear equation set and the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjGOR (water production ratio), TOC (total organic carbon) of daily operation cost; otherwise, go to step B5.
Step B5: by modifying BkTo obtain Bk+1
Figure BDA0002760582980000152
Wherein s isk=xk+1-xk,yk=ΔG(xk+1)-ΔG(xk)。xkDenotes the value, x, evaluated at the k-th iterationk+1Denotes the value, s, evaluated in the (k + 1) th iterationkThe difference between the two evaluated values is indicated. Δ G (x)k+1) Represents G (x)k+1) Gradient vector of, Δ G (x)k) Represents G (x)k) Gradient vector of, ykThe gradient vector difference for the (k + 1) th iteration and the k iterations is expressed.
Step B6: let k ═ k +1, go to step B3 for calculation.
The parameter decision module is used for obtaining the scaling coefficient f of the brine heater at all time points according to the simulation calculation moduleBHFouling factor f of flash chamberjThe water making ratio GOR and the daily running cost TOC are fitted and analyzed by adopting a least square method, and the system scaling degree is reasonably judged, and the specific steps are as follows:
step C1: inheriting the place of the analog computation module from the beginning of data acquisitionHas data and aims at the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjGOR (water production ratio), TOC (total organic carbon) of daily operating cost and scaling coefficient f of brine heaterBHSetting the upper limit H1Fouling factor f of flash chamberjSetting the upper limit H2The water making ratio GOR sets the lower limit X1Daily operating cost TOC setting upper limit X2
Step C2: dividing the data into four parts to be fitted respectively, and firstly, fitting the scaling coefficient f of the brine heaterBHAnd (4) performing curve fitting by using a least square method. Suppose a given collected data point (xx)i,yyi)(i=0,1,…,m),xxiRepresenting data acquisition time points Ti,yyiRepresents the scaling coefficient f of the brine heater collected at each time pointBH(i) In that respect The fitting polynomial is
Figure BDA0002760582980000161
To ensure that the module computation speed makes the polynomial order nn equal to 3, so that
Figure BDA0002760582980000162
Wherein I is a0,a1,a2,a3So that the above problem is to find I ═ I (a)0,a1,a2,a3) The extreme value problem of (2).
Step C3: obtaining the necessary condition of extremum by multivariate function
Figure BDA0002760582980000163
Namely, it is
Figure BDA0002760582980000164
Step C4: the formula (46) is rewritten into a normal equation system form
Figure BDA0002760582980000171
It can be shown that the coefficient matrix of the normal equation set (47) is a symmetric positive definite matrix, so that there is a unique solution. Is solved from formula (47) to obtain akk( kk 0,1, …,3), thereby obtaining a polynomial
Figure BDA0002760582980000172
Step C5: repeating the steps C2 to C4 to respectively obtain the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjThe water production ratio GOR and the daily running cost TOC are fitted curves of the running time of the system, and the fitted curve is P1(t)、P2(t)、P3(t) and P4(t), wherein t represents time.
Step C6: judging whether the current system needs to be cleaned according to the upper and lower limits set by the parameters and the four obtained fitted curves, and deducing the time point Tim to be cleaned of the system under the 4 indexes according to a fitted equation1、Tim2、Tim3、Tim4
Step C7: mixing Tim1、Tim2、Tim3、Tim4And comparing to obtain the latest time node which is recorded as Tim, wherein the time point is the next time point to be cleaned of the system.
Step C8: fouling factor f for brine heaterBHFouling factor f of flash chamberjThe scale of the system can be obtained according to the numerical value of the current data acquisition point.
The foregoing is a further description of the present invention given in connection with the specific examples provided below, and the practice of the present invention is not to be considered limited to these descriptions. Those skilled in the art to which the invention relates will readily appreciate that certain modifications and substitutions can be made without departing from the spirit and scope of the invention.

Claims (4)

1. A scale cleaning device of a multistage flash evaporation seawater desalination system is characterized in that; the system comprises a sensor module, a data acquisition module, a man-machine interaction module, a simulation calculation module, an A/D and D/A conversion module, a central processing module, a parameter decision module and a display module; the sensor module comprises five flow sensors, four temperature sensors and two seawater salinity sensors; the data acquisition module is used for acquiring the temperature and the salt content of the feed seawater, the fresh water flow, the circulating brine and the heat discharge seawater flow obtained by the sensor module, and the heating steam flow and the temperature; the human-computer interaction module is used for setting the structural parameters of flash chambers at all levels of the multi-level flash seawater desalination system, the parameters of a brine heater and the data acquisition period; the A/D and D/A conversion module is used for converting the received analog quantity into a corresponding digital quantity or converting the received digital quantity into a corresponding analog quantity; the central processing module is used for storing a scaling coefficient processing problem model of the multi-stage flash seawater desalination system and required physical parameters, receiving and storing data acquired by the data acquisition module through the A/D and D/A conversion module, receiving and storing data obtained by processing of the analog computation module and the parameter decision module, and then transmitting the data to the display module; the simulation calculation module calls a system program to calculate according to the currently acquired data to obtain the scaling coefficient f of the current brine heaterBHFouling factor f of flash chamberjThe water making ratio GOR and the daily running cost TOC are obtained, and the parameters are transmitted to a display module; the parameter decision module analyzes the data stored in the simulation calculation module before, estimates the system scaling degree and the next system cleaning time, and transmits the parameters to the display module; and the display module displays the calculation results of the simulation calculation module and the parameter decision module.
2. A method for cleaning scale in a multistage flash seawater desalination system is characterized by comprising the following steps:
the method comprises the following steps: firstly, an engineer sets the structural parameters of the multistage flash seawater desalination system through a human-computer interaction module and sets the parameters for transportationA line period; the device collects the needed data in a given period and sends the data to the central processing module through the A/D and D/A conversion module, and the central processing module calls the simulation calculation module; the simulation calculation module obtains the scaling coefficient f of the brine heater of the current system by calculating the model problem in the central processing moduleBHAnd fouling factor f of flash chamberjGOR (water production ratio), TOC (total organic carbon) of daily operation cost; the parameter decision module performs comparative analysis according to the parameters obtained by the analog calculation module to obtain the scaling degree of the current system and the next system cleaning time and sends the relevant theory to the system display module; in the next operation period, repeating the data acquisition, simulation calculation and comparative analysis processes, and continuously estimating the system scaling degree in real time;
the method specifically comprises the following steps:
step A1: an operator or an engineer gives structural parameters, physical property coefficients and a data acquisition period Tc of the multistage flash seawater desalination system through a man-machine interaction module;
step A2: collecting the flow W of the cooling brine entering the hot discharge section at the current time point by using a data collection moduleFFlow rate W of circulating seawaterReHeating steam flow rate WsteamFlow rate W of flash brineBFlash evaporation fresh water flow WDTemperature T of feed seawaterseaTemperature T of heating steamsteamTemperature T of flash brineBFlash fresh water temperature TDFeed brine concentration CFConcentration of flash brine CB(ii) a Recording the current time, making a variable T1 equal to the current time, and then sending the parameters to a central processing module through an A/D and D/A conversion module;
step A3: the central processing module calls the simulation calculation module according to the internally stored stable state simulation and daily operation cost model of the multi-stage flash seawater desalination device, so as to calculate the scaling coefficient f of the brine heater at the current T1 momentBHFouling factor f of flash chamberjThe water making ratio GOR and the daily running cost TOC, and then sending the parameters to a parameter decision module;
step A4: the parameter decision module obtains parameters in the periodNumber set L1(fBH,fjGOR, TOC) and the parameter set L obtained in the previous cyclesi(fBH,fjGOR, TOC), i is 1,2, …, m is the current period number, comparative analysis is carried out, the scaling degree of the current system and the next time of cleaning the system are estimated, and the simulation calculation module and the parameter decision module send the calculation data to the central processing module;
step A5: the central processing module arranges the data and sends the data to the display module, and the display module displays the current time T1 and the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjThe water making ratio GOR, the daily running cost TOC, the system scaling degree and the system time to be cleaned Tim;
step A6: recording the current time as T2, and if T2-T1< Tc, continuing to wait; otherwise, go to step A2, and resume data acquisition.
3. The method for cleaning the scale in the multi-stage flash evaporation seawater desalination system as claimed in claim 2, wherein: the model of the multistage flash evaporation seawater desalination device in the central processing module for stable state simulation and daily operation cost consists of the formulas (1) to (38);
the steady-state model of the multi-stage flash evaporation seawater desalination device consists of a flash chamber equation, a brine heater equation, a mixing and separating equation and a physical property parameter equation; for the j-th-stage flash chamber, the flash chamber module model consists of the following formulas (1) to (8):
WBj-1+WDj-1=WBj+WDj (1);
WBj-1CBj-1=WBjCBj (2);
WBj-1hBj-1=WBjhBj+VBjhVj (3);
WBj-1-WBj=VBj (4);
Figure FDA0002760582970000021
Figure FDA0002760582970000022
wherein, WBjRepresents the mass flow of flashed brine, W, of the j stageBj-1Represents the mass flow of the flashed brine, W, of the j-1 th stageDjThe mass flow of fresh water W representing the j-th outputDj-1Represents the mass flow of the flash brine of the j-1 stage; cBjDenotes the flash brine concentration of the j stage, CBj-1Represents the flash brine concentration of the j-1 stage; h isBjRepresents the specific enthalpy, h, of the j-th stage flash brineBj-1Represents the specific enthalpy, h, of the j-1 th stage flash brineVjSpecific enthalpy, V, of the j-th stage flash steamBjExpressing the evaporation amount of the brine in the j-stage flash chamber; wFIndicating the mass flow, CP, of the chilled brine entering the hot discharge sectionRjDenotes the heat capacity, CP, of the cooled brine leaving the j-th stage flash chamberDjDenotes the specific heat capacity, CP, of fresh water leaving the j-th stage flash chamberDj-1Denotes the specific heat capacity, CP, of fresh water leaving the j-1 stage flash chamberBjDenotes the specific heat capacity, CP, of the flashed brine leaving the j-th stage flash chamberBj-1Denotes the specific heat capacity, T, of the flashed brine leaving the j-1 stage flash chamberFjIndicating the temperature, T, of the cooled brine leaving the j-th stage flash chamberFj+1Indicating the temperature, T, of the chilled brine entering the j-th stage flash chamberBjIndicating the temperature, T, of brine leaving the j-th stage flash chamberBj-1Indicating the temperature, T, of the brine leaving the j-1 stage flash chamberDjRepresenting the temperature, T, of the fresh water leaving the j-th flash chamberDj-1The temperature of the fresh water leaving the j-1 stage flash chamber is shown, and T represents the reference temperature of the flash chamber in an ideal state; a. thejThe heat transfer area of the j-th stage flash chamber is shown,
Figure FDA0002760582970000031
denotes the heat transfer coefficient of the j-th stage flash chamber, wherein W denotes the feed flow rate of the j-th stage flash chamber, and W is W for the heat discharge sectionFDenotes the feed seawater flow rate, whereas for the heat recovery sectionW=WRThe feed flow rate to the heat recovery section is indicated,
Figure FDA0002760582970000032
the outer diameter of each stage of the steaming chamber is expressed,
Figure FDA0002760582970000033
representing the internal diameter of the condenser tube of each stage of flash chamber, DiThe inner diameter is expressed, and a specific formula is expanded in a physical property equation part;
TBj=TDj+ΔBPEj+ΔNETDj+ΔTLj (7);
TVj=TDj+ΔTLj (8);
wherein, Δ BPEjDenotes the boiling point rise of the j-th brine, Δ NETDjDenotes the unbalance margin, Δ TLjRepresents the temperature loss through the demister and condenser; t isVjIndicating the flash steam temperature of the j-stage flash chamber;
the brine heater module model consists of equations (9) - (12):
WB0=WR (9);
CB0=CR (10);
WRCPRH(TB0-TF1)=Wsteamλs (11);
wherein,
Figure FDA0002760582970000034
Figure FDA0002760582970000035
wherein, WB0Represents the mass flow of flashed brine, W, exiting the brine heaterRRepresents the mass flow of chilled brine entering the heat recovery section; cB0Represents the concentration of flashed brine, C, entering the brine heaterRIndicating cooling into the heat recovery sectionBrine concentration; CP (CP)RHIndicating the cooling brine heat capacity, T, into the brine heaterB0Represents the temperature of the flashed brine, W, exiting the brine heatersteamExpressed as heating steam mass flow, lambdasRepresenting the latent heat of vapour, TsteamExpressed as brine heater steam temperature; a. theHThe heat transfer area of the brine heater is shown,
Figure FDA0002760582970000036
denotes the heat transfer coefficient of the brine heater, wherein W denotes the feed flow W of the brine heaterR
Figure FDA0002760582970000037
The outside diameter of the brine heater is shown,
Figure FDA0002760582970000038
the diameter of the inside of the condensation pipe of the brine heater is expressed, and a specific formula is developed in a physical property equation part;
the mixed separation module model is composed of formulas (13) to (20):
WBD=WBN-WRe (13);
Wm=WF-Wr (14);
S=Wr-Cw (15);
WR=WRe+Wm (16);
WR·CR=WRe·CRe+Wm·Cm (17);
WR·hR=WRe·hRe+Wm·hm (18);
WF=S+WS (19);
Figure FDA0002760582970000041
wherein WBDRepresents the mass flow of the waste seawater, WBNRepresenting the mass flow of brine, W, leaving the last stage flash chamberReRepresents the circulating brine mass flow; wmRepresents the mass flow of make-up brine, WrRepresenting the hot discharge seawater mass flow; s represents the return flow rate of the hot discharge section, CwRepresenting the mass flow of brine exiting the hot discharge section; cReDenotes circulating brine concentration, CmIndicates make-up brine concentration; h isRRepresents the specific enthalpy of the brine entering the heat recovery section, hReDenotes the specific enthalpy of the circulating brine, hmRepresents the specific enthalpy of make-up brine; wSRepresenting the feed seawater mass flow;
Figure FDA0002760582970000042
represents the specific enthalpy of the brine at the inlet of the heat discharge section, hSRepresenting the specific enthalpy of the returned brine in the heat discharge section,
Figure FDA0002760582970000043
represents the specific enthalpy of the feed seawater;
the physical property parameter equation model is composed of equations (21) to (31):
Figure FDA0002760582970000044
CPB=[1-CB(0.011311-1.146×10-5TB)]×CPD (22);
hV=596.912+0.46694TS-0.000460256TS 2 (23);
hB=CPB·TB (24);
hD=CPD·TD (25);
Figure FDA0002760582970000045
wherein CC ═ (19.819C)B)/(1-CB),CC denotes concentration conversion, CBRepresents the flash brine concentration;
Figure FDA0002760582970000046
wherein, ω isj=WF/wj,ωjDenotes the mass flow per unit length of the cooled brine entering the hot discharge section of the j-th stage, wjThe width of a condensation pipe of a j-stage flash chamber is shown;
TL=exp(1.885-0.02063TD)/1.8 (28);
U=4.8857/(y+z+4.8857f) (29);
y=[0.0013(v×Di)0.2]/[(0.2018+0.0031×T)v] (30);
Figure FDA0002760582970000051
GOR=WDN/Wsteam (32);
wherein CPDThe specific heat capacity of the fresh water in the flash chamber is represented; CP (CP)BIndicating the specific heat capacity of brine in the flash chamber, CBDenotes the flash brine concentration, TBRepresents the flash brine temperature; h isvRepresents the enthalpy of the steam, TSIs the steam temperature; h isBRepresents the enthalpy of the brine; h isDRepresents the enthalpy value, T, of fresh waterDRepresents the fresh water temperature; BPE represents the brine boiling point rise, where T represents the brine temperature in the flash chamber or brine heater; NETD denotes the non-equilibrium temperature difference, HjDenotes the flash brine level, wjDenotes the width, Δ T, of the condensing tube of the j-th stage flash chamberBRepresenting the temperature difference of the brine between two stages; TL represents the temperature loss through the demister and condenser tube; u represents the heat transfer coefficient of the brine heater or each stage of flash chamber; y is an intermediate expression relating to flow velocity in the tube, brine temperature and diameter in the condenser tube, z is an intermediate expression relating to fresh water temperature in the flash chamber, y and z are simply calculations, and f is the fouling factor of the brine heater or the flash chamber(ii) a v represents the flow velocity in the tube, DiRepresents the internal diameter of the condenser tube, T represents the temperature of the brine at the outlet of the heat exchanger; wDNThe mass flow of the total fresh water in the flash chamber is represented, and the GOR represents the water generation ratio which is a key index of the performance of the reaction system;
the daily running cost module model is composed of equations (33) to (38):
C1=22×Wsteam×[(Tsteam-40)/85]×0.00415 (33);
C2=22×(DNw)×0.109 (34);
C3=22×(DNw)×0.082 (35);
C4=22×(DNb)×0.024 (36);
C5=22×(DNw)×0.1 (37);
TOC=C1+C2+C3+C4+C5 (38);
wherein, C1 represents the heating steam cost, C2 represents the electric energy cost consumed by the device, C3 represents the maintenance and idle cost, C4 represents the pretreatment cost, C5 represents the labor cost, and TOC represents the daily operating cost of the system; dNRepresenting the total fresh water production, pwDenotes the pure water density, ρbRepresents the density of the concentrated brine;
the simulation calculation module solves the steady-state simulation problem formed by the calculation formulas (1) to (38) by using a quasi-Newton method to determine the scaling coefficient f of the brine heater of the current systemBHFouling factor f of flash chamber in heat recovery section and heat discharge sectionjThe specific steps of the method are as follows:
step B1: the equations of the above equations (1) to (38) for obtaining the unknown quantity are organized into a nonlinear equation system, which is expressed by the following equation (39):
Figure FDA0002760582970000052
the representation of the vector is:
G(x)=0 (40);
here, x ═ x (x)1,x2,…,xp)T,G=(g1,g2,…,gq)T,gi(i=1,2,…,q):Rn→R;
Wherein x is1,x2,…,xpP unknowns representing a nonlinear system of equations, x representing a matrix of dimension p x 1 formed by the unknowns of the system of equations; g1,g2,…,gqRepresenting q equations constituting the nonlinear system of equations, G representing a q × p dimensional matrix constituted by the equations of the nonlinear system of equations;
step B2: let the initial iteration number k equal to 0, set the initial value x0∈RnInitial quasi-Newton matrix BkThe method is characterized in that the method is a unit matrix of dimension p multiplied by p, the calculation precision of a function value is epsilon, and the precision of the minimum step length is delta;
step B3: calculating search direction vector d under iteration times kkTo get the value of the next point:
xk+1=xk+dk (41);
dk=-BkΔG(xk) (42);
step B4: calculate G (x)k) And G (x)k+1) If G (x)k+1) | | < epsilon or | | | xk+1-xkIf | | < delta, terminating the iteration to obtain the solution of the nonlinear equation set and the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjGOR (water production ratio), TOC (total organic carbon) of daily operation cost; otherwise, go to step B5;
step B5: by modifying BkTo obtain Bk+1
Figure FDA0002760582970000061
Wherein s isk=xk+1-xk,yk=ΔG(xk+1)-ΔG(xk);xkDenotes the value, x, evaluated at the k-th iterationk+1Denotes the value, s, evaluated in the (k + 1) th iterationkRepresenting the difference between the two evaluated values; Δ G (x)k+1) Watch (A)Show G (x)k+1) Gradient vector of, Δ G (x)k) Represents G (x)k) Gradient vector of, ykExpressing the gradient vector difference of the (k + 1) th iteration and the (k) th iteration;
step B6: let k ═ k +1, go to step B3 for calculation.
4. The method for cleaning the scale in the multi-stage flash evaporation seawater desalination system as claimed in claim 2, wherein: the parameter decision module is used for obtaining the scaling coefficient f of the brine heater at all time points according to the simulation calculation moduleBHFouling factor f of flash chamberjThe water making ratio GOR and the daily running cost TOC are fitted and analyzed by adopting a least square method, and the system scaling degree is reasonably judged, and the specific steps are as follows:
step C1: inheriting all data of the analog calculation module from the beginning of data acquisition and aiming at the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjGOR (water production ratio), TOC (total organic carbon) of daily operating cost and scaling coefficient f of brine heaterBHSetting the upper limit H1Fouling factor f of flash chamberjSetting the upper limit H2The water making ratio GOR sets the lower limit X1Daily operating cost TOC setting upper limit X2
Step C2: dividing the data into four parts to be fitted respectively, and firstly, fitting the scaling coefficient f of the brine heaterBHPerforming curve fitting by adopting a least square method; suppose a given collected data point (xx)i,yyi),i=0,1,…,m,xxiRepresenting data acquisition time points Ti,yyiRepresents the scaling coefficient f of the brine heater collected at each time pointBH(i) (ii) a The fitting polynomial is
Figure FDA0002760582970000071
To ensure that the module computation speed makes the polynomial order nn equal to 3, so that:
Figure FDA0002760582970000072
wherein I is a0,a1,a2,a3So that the above problem is to find I ═ I (a)0,a1,a2,a3) The problem of extreme values of (a);
step C3: the necessary condition of extreme value is solved by a multivariate function, and the following results are obtained:
Figure FDA0002760582970000073
namely, it is
Figure FDA0002760582970000074
Step C4: rewrite equation (46) to normal equation set form:
Figure FDA0002760582970000075
the coefficient matrix of the normal equation set (47) can be proved to be a symmetrical positive definite matrix, so that a unique solution exists; is solved from formula (47) to obtain akk(kk ═ 0,1, …,3), giving a polynomial:
Figure FDA0002760582970000076
step C5: repeating the steps C2 to C4 to respectively obtain the scaling coefficient f of the brine heaterBHFouling factor f of flash chamberjThe water production ratio GOR and the daily running cost TOC are fitted curves of the running time of the system, and the fitted curve is P1(t)、P2(t)、P3(t) and P4(t), wherein t represents time;
step C6: judging whether the current system needs to be cleaned according to the upper and lower limits set by the parameters and the four obtained fitting curves, and deducing the system waiting time under the 4 indexes according to a fitting equationCleaning time Tim1、Tim2、Tim3、Tim4
Step C7: mixing Tim1、Tim2、Tim3、Tim4Comparing to obtain the latest time node which is marked as Tim and is the time point to be cleaned next time;
step C8: fouling factor f for brine heaterBHFouling factor f of flash chamberjThe scale of the system can be obtained according to the numerical value of the current data acquisition point.
CN202011216530.1A 2020-11-04 2020-11-04 Scale cleaning device and method for multistage flash evaporation seawater desalination system Active CN112678904B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202011216530.1A CN112678904B (en) 2020-11-04 2020-11-04 Scale cleaning device and method for multistage flash evaporation seawater desalination system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202011216530.1A CN112678904B (en) 2020-11-04 2020-11-04 Scale cleaning device and method for multistage flash evaporation seawater desalination system

Publications (2)

Publication Number Publication Date
CN112678904A true CN112678904A (en) 2021-04-20
CN112678904B CN112678904B (en) 2023-03-17

Family

ID=75445842

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202011216530.1A Active CN112678904B (en) 2020-11-04 2020-11-04 Scale cleaning device and method for multistage flash evaporation seawater desalination system

Country Status (1)

Country Link
CN (1) CN112678904B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113158466A (en) * 2021-04-23 2021-07-23 浙江捷创智能技术有限公司 Method for predicting maintenance of pipe blockage of phosphorus chemical dilute phosphoric acid supply system

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1866140A (en) * 2005-02-10 2006-11-22 通用电气公司 Methods and apparatus for optimizing combined cycle/combined process facilities
CN102706387A (en) * 2012-05-31 2012-10-03 苏州市金翔钛设备有限公司 Dirty factor detection device for condenser
US20150175442A1 (en) * 2013-12-20 2015-06-25 Massachusetts Institute Of Technology Thermal Desalination for Increased Distillate Production
CN205426201U (en) * 2016-02-15 2016-08-03 北京洁禹通环保科技有限公司 Condenser dirt accumulation degree detection device
CN106872514A (en) * 2017-02-21 2017-06-20 沈阳艾柏瑞环境科技有限公司 Steady Heat Transfer process heat transfer coefficient and dirtiness resistance value on-line monitoring system and method
CN110143635A (en) * 2019-04-03 2019-08-20 杭州电子科技大学 A kind of optimizing operation method and device of multi-stage Flash Desalination System for Seawater
CN111059957A (en) * 2019-12-28 2020-04-24 上海九瀚机电设备有限公司 System and method for monitoring fouling coefficient of plate heat exchanger in real time

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1866140A (en) * 2005-02-10 2006-11-22 通用电气公司 Methods and apparatus for optimizing combined cycle/combined process facilities
CN102706387A (en) * 2012-05-31 2012-10-03 苏州市金翔钛设备有限公司 Dirty factor detection device for condenser
US20150175442A1 (en) * 2013-12-20 2015-06-25 Massachusetts Institute Of Technology Thermal Desalination for Increased Distillate Production
CN205426201U (en) * 2016-02-15 2016-08-03 北京洁禹通环保科技有限公司 Condenser dirt accumulation degree detection device
CN106872514A (en) * 2017-02-21 2017-06-20 沈阳艾柏瑞环境科技有限公司 Steady Heat Transfer process heat transfer coefficient and dirtiness resistance value on-line monitoring system and method
CN110143635A (en) * 2019-04-03 2019-08-20 杭州电子科技大学 A kind of optimizing operation method and device of multi-stage Flash Desalination System for Seawater
CN111059957A (en) * 2019-12-28 2020-04-24 上海九瀚机电设备有限公司 System and method for monitoring fouling coefficient of plate heat exchanger in real time

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
高寒寒等: ""多级闪蒸海水淡化系统的动态模拟与优化"", 《计算机与应用化学》 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113158466A (en) * 2021-04-23 2021-07-23 浙江捷创智能技术有限公司 Method for predicting maintenance of pipe blockage of phosphorus chemical dilute phosphoric acid supply system

Also Published As

Publication number Publication date
CN112678904B (en) 2023-03-17

Similar Documents

Publication Publication Date Title
Alatiqi et al. Process control in water desalination industry: an overview
CN112678904B (en) Scale cleaning device and method for multistage flash evaporation seawater desalination system
Abdul‐Wahab et al. Development of a steady‐state mathematical model for multistage flash (MSF) desalination plant
Li et al. On-line fouling monitoring model of condenser in coal-fired power plants
CN102735708B (en) Determination system and method for heat exchange coefficient of cooper pipe
Jradi et al. Application of an artificial neural networks method for the prediction of the tube-side fouling resistance in a shell-and-tube heat exchanger
CN110143635B (en) Optimized operation method and device of multistage flash evaporation seawater desalination system
CN113685797B (en) Variable working condition thermodynamic calculation method for waste heat boiler economizer
El-Nashar Predicting part load performance of small MED evaporators-a simple simulation program and its experimental verification
Palenzuela et al. Modeling of the heat transfer of a solar multi-effect distillation plant at the Plataforma Solar de Almería
Yang Neural networks for predicting air gap membrane distillation performance
Alasfour et al. Rigorous steady state modeling of MSF-BR desalination system
Ettouney Conventional thermal processes
CN101274784A (en) Steam-water four-stage separating five-effect water distillator
Sadri et al. Multi objective optimization of the MED-TVC system with exergetic and heat transfer analysis
Marmouch et al. Effect of a cooling tower on a solar desalination system
Liu et al. Design optimization of the parallel-feeding multi-effect evaporation system using multi-objective genetic algorithm
Alatiqi et al. Measurements of dynamic behavior of a multistage flash water desalination system
CN109189029B (en) Energy-saving on-line monitoring system and method for low-temperature economizer of thermal power plant
CN111048157B (en) Waste heat recovery device applied to air separation purification system and key parameter determination method thereof
Baig et al. Performance characteristics of a once-through multi-stage flash distillation process
Hawaidi Simulation, optimisation and flexible scheduling of MSF desalination process under fouling. Optimal design and operation of MSF desalination process with brine heater and demister fouling, flexible design operation and scheduling under variable demand and seawater temperature using gPROMS.
CN113033649B (en) PTA process anomaly monitoring method based on real-time discriminant dynamic feature extraction
Tajeldin Development of a steady-state mathematical model for multistage flash (MSF) desalination plant
KR100838940B1 (en) Sampling device for vacuum condition equipment or pipeline of desalination plant

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant