[go: up one dir, main page]

CN113880155B - Online adjusting method for water quality of low-pressure boiler water - Google Patents

Online adjusting method for water quality of low-pressure boiler water Download PDF

Info

Publication number
CN113880155B
CN113880155B CN202111184258.8A CN202111184258A CN113880155B CN 113880155 B CN113880155 B CN 113880155B CN 202111184258 A CN202111184258 A CN 202111184258A CN 113880155 B CN113880155 B CN 113880155B
Authority
CN
China
Prior art keywords
phosphate
concentration
value
furnace water
water
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.)
Active
Application number
CN202111184258.8A
Other languages
Chinese (zh)
Other versions
CN113880155A (en
Inventor
张霞
王长荣
刘勇
张久政
赵金良
石子睿
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.)
Jiujiang 707 Institute Of Precision Mechatronics Sci & Tech Co ltd
Original Assignee
Jiujiang 707 Institute Of Precision Mechatronics Sci & Tech 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 Jiujiang 707 Institute Of Precision Mechatronics Sci & Tech Co ltd filed Critical Jiujiang 707 Institute Of Precision Mechatronics Sci & Tech Co ltd
Priority to CN202111184258.8A priority Critical patent/CN113880155B/en
Publication of CN113880155A publication Critical patent/CN113880155A/en
Application granted granted Critical
Publication of CN113880155B publication Critical patent/CN113880155B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/18PO4-P

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Control Of Steam Boilers And Waste-Gas Boilers (AREA)
  • Control Of Non-Electrical Variables (AREA)

Abstract

The invention discloses a method for online adjusting the water quality of low-pressure boiler water, which comprises the following steps ofThe method comprises the following steps: (1) The furnace water adopts a continuous coordination phosphate treatment mode, a mathematical function model of the phosphate concentration at the moment t is built, and the phosphate concentration C at the moment t is solved; (2) Establishing a mathematical function model of the sodium-phosphorus molar ratio R, and calculating the furnace water R value at the moment t; (3) Build time t Na 3 PO 4 Adding quantity mathematical function model to calculate furnace water Na at time t 3 PO 4 The addition amount is calculated; (4) Establishing NaH at t moment 2 PO 4 Adding quantity mathematical function model to calculate furnace water NaH at time t 2 PO 4 The addition amount is as follows. The furnace water is regulated by the concentration C of phosphate radical, the R value of the furnace water and the adding amount of phosphate, so that the water quality of the furnace water is regulated, the phosphate radical, the pH value and the R value in the furnace water are ensured to be in the index range, and the phenomena of free sodium hydroxide corrosion and phosphate hiding are prevented.

Description

Online adjusting method for water quality of low-pressure boiler water
Technical Field
The invention belongs to the field of water treatment, and particularly relates to an online adjustment method for the water quality of low-pressure boiler water.
Background
In the running process of some low-pressure boilers, the working condition is changed frequently, the stability of the water quality of the boiler is poor, the qualification rate of the water quality index of the boiler is difficult to ensure by the traditional offline detection intermittent adjustment coordinated phosphate method, so that the contents of free alkali and sludge in the boiler are more, the boiler is rusted to different degrees, the safe running of the system is seriously affected, and an online water quality adjustment method is urgently needed to improve the qualification rate of the water quality index of the boiler. However, due to the restriction of the phosphate online detection technology, the online detection value of the phosphorus meter has delay of 5-15 minutes, the working condition of certain low-pressure boilers is frequently changed, the stability of the water quality of the boiler is poor, the existing phosphate online detection technology is directly applied to the low-pressure boilers, and the qualification rate of the water quality index of the boiler is difficult to improve. In order to improve the qualification rate of the boiler water index, reduce the content of free alkali and sludge in the boiler and ensure the safe operation of the system, an online boiler water quality adjusting method which is suitable for the low-pressure boiler and is suitable for the existing detection technology is urgently needed.
Disclosure of Invention
The invention aims to provide the online water quality adjusting method for the low-pressure boiler water, which solves the problems in the background art, is suitable for the water quality adjustment of the low-pressure boiler water with frequent working condition change and poor water quality stability, and can effectively improve the qualification rate of the water index.
The technical scheme adopted for achieving the purpose is that the low-pressure boiler water quality online adjusting method comprises the following steps:
(1) The furnace water adopts a continuous coordination phosphate treatment mode, a mathematical function model of the phosphate radical concentration at the moment t is built, and the phosphate radical concentration C at the moment t is solved: according to the evaporation capacity, the pollution discharge capacity, the initial phosphate radical concentration, the water supply flow, the furnace water volume, the water supply hardness, the steam humidity and the running time of a steam system, a mathematical function model of the phosphate radical concentration at the moment t is built, the evaporation capacity, the pollution discharge capacity, the phosphate radical, the water supply flow, the furnace water volume, the water supply hardness, the steam humidity and the running time of the steam system at the moment t are input, and the phosphate radical concentration C at the moment t is calculated;
(2) Establishing a mathematical function model of the sodium-phosphorus molar ratio R, and calculating the furnace water R value at the moment t: according to the pH value and the phosphate concentration C, a mathematical function model of the sodium-phosphorus molar ratio R is established, the pH value and the phosphate concentration at the moment t are input, and the furnace water R value at the moment t is calculated;
(3) Build time t Na 3 PO 4 Adding quantity mathematical function model to calculate furnace water Na at time t 3 PO 4 The addition amount is as follows: according to the phosphate radical, the phosphate radical of the control point, the furnace water R, the control point R and Na of the steam system 3 PO 4 Solution concentration, build up of time t Na 3 PO 4 The mathematical function model of the addition quantity is input into the system, namely the concentration of phosphate radical at the time t, phosphate radical at the control point, furnace water R at the time t, control point R and Na 3 PO 4 Solution concentration, solution furnace water Na at time t 3 PO 4 The addition amount is calculated;
(4) Establishing NaH at t moment 2 PO 4 Adding quantity mathematical function model and calculating t momentFurnace water NaH 2 PO 4 The addition amount is as follows: according to the phosphate radical, the phosphate radical of the control point, the furnace water R, the control point R and the NaH of the steam system 2 PO 4 Solution concentration, naH at t moment is established 2 PO 4 The addition quantity mathematical function model is input into the system, namely the concentration of phosphate radical at the time t, phosphate radical at the control point, furnace water R at the time t, control point R and NaH 2 PO 4 Solution concentration, and solving furnace water NaH at time t 2 PO 4 The adding amount of the furnace water is regulated by the concentration of phosphate radical, R and the adding amount of phosphate, so as to realize the water quality regulation of the furnace water.
Further, the expression of the mathematical function model of the phosphate concentration at the time t in the step (1) is as follows:
Figure BDA0003297623670000021
wherein:
f 1 (p,W,u,H,Q,C 0 ) -a function;
f 2 (p,W,u,V 0 ) -a function;
f 3 (p, W, u, H, Q) -function;
c0—initial phosphate concentration;
phosphate concentration at C-t;
t-elapsed time from C0 to C;
v0-furnace water volume;
h-hardness of water supply;
q-feed water flow;
p-discharge capacity;
u-steam humidity;
w-evaporation amount.
Further, the function f 1 (p,W,u,H,Q,C 0 ) Is p, W, u, H, Q, C 0 As p, W, u, H, Q, C 0 Is increased and decreased; the function f 2 (p,W,u,V 0 ) Is p, W, u, V 0 F is a function of (f) 2 (p,W,u,V 0 ) Is a linear function of p, W, u, with p, W, uIncrease and decrease and increase, f 2 (p,W,u,V 0 ) V of yes 0 Inverse proportional function, following V 0 Is increased and decreased; the function f 3 (p, W, u, H, Q) is a function of p, W, u, H, Q, f 3 (p, W, u, H, Q) is a complex function of p, W, u, decreasing with increasing p, W, u, f 3 (p, W, u, H, Q) is a H, Q direct proportional function that decreases with increasing H, Q and increases with decreasing H, Q.
Further, the pH value in the step (2) is a furnace water pH detection value, and is generated by phosphate hydrolysis, and the range is as follows: the pH value is more than or equal to 9 and less than or equal to 11.
Further, the molar ratio R of sodium to phosphorus in the step (2) is the ratio of phosphate hydrolysis sodium ions to phosphate radicals, and the range is as follows: pH is more than or equal to 2 and less than or equal to 3; the R value is calculated by solving a mathematical function model of the R value and the furnace water phosphate concentration C, pH at the moment t, and the mathematical function model expression of the R value is as follows:
R=f 4 (pH,C)
wherein the R value is an exponential function of the pH value, and the R value increases and decreases with increasing pH value; the R value is a hyperbolic function of the phosphate concentration C at time t, and decreases as the C value increases, and increases as the C value increases.
Further, na in the step (3) 3 PO 4 The concentration of the independent aqueous solution is 1 to 10 percent, and the adding amount of the independent aqueous solution is Na 3 PO 4 Furnace water R at the moment of adding quantity G and t and sodium-phosphorus mole ratio R at control point Control device Phosphate radical concentration C at time t and control point phosphate radical concentration C Control device Obtaining a mathematical function model through calculation; na (Na) 3 PO 4 The mathematical function model expression of the addition amount G is as follows:
Figure BDA0003297623670000041
g and R, R in the formula Control device 、C、C Control device In linear function, G value is related to R Control device 、C Control device The value increases and decreases, the G value decreases and increases as the R, C value increases and decreases.
Further, naH in the step (4) 2 PO 4 The concentration of the independent aqueous solution is 1 to 10 percent, and the adding amount of the independent aqueous solution is NaH 2 PO 4 Dosage G 1 Molar ratio R of sodium to phosphorus with furnace water R and control point at time t Control device Phosphate concentration C at time t and phosphate concentration C at control point Control device Obtaining a mathematical function model through calculation; naH (NaH) 2 PO 4 Dosage G 1 The mathematical function model expression of (2) is as follows:
Figure BDA0003297623670000042
g in 1 And R, R Control device 、C、C Control device In linear function relation, G 1 Value with R Control device The C value increases and decreases, the G value increases with R, C Control device The value increases and increases, and decreases.
Advantageous effects
Compared with the prior art, the invention has the following advantages.
1. According to the invention, the water quality of the furnace water is regulated on line, the water quality deviation of the furnace water is controlled, and experiments show that the qualification rate of the water quality index of the furnace water can be effectively improved;
2. according to the method, the phosphate radical concentration at the time t of the boiler water is accurately calculated, the content of free sodium hydroxide in the boiler water is controlled, the free alkali corrosion perforation phenomenon of the boiler heat transfer pipe is effectively prevented, and the safe operation of the system is ensured;
3. the invention can accurately calculate the phosphate concentration of the furnace water at the moment t, effectively control the phosphate content in the furnace water, prevent the occurrence of the 'phosphate hiding phenomenon', and provide guarantee for the safe operation of the system;
4. the invention can accurately calculate the adding amount of phosphate, control the total content of phosphate in furnace water, and effectively reduce the sludge amount and the sludge treatment cost in the boiler.
Drawings
The present invention is described in further detail below with reference to the accompanying drawings.
FIG. 1 is a flow chart of an embodiment of the present invention.
Detailed Description
The invention is further described below with reference to examples and figures.
An online adjustment method for the water quality of low-pressure boiler water, as shown in fig. 1, comprises the following steps:
(1) The furnace water adopts a continuous coordination phosphate treatment mode, a mathematical function model of the phosphate radical concentration at the moment t is built, and the phosphate radical concentration C at the moment t is solved: according to the evaporation capacity, the pollution discharge capacity, the initial phosphate radical concentration, the water supply flow, the furnace water volume, the water supply hardness, the steam humidity and the running time of a steam system, a mathematical function model of the phosphate radical concentration at the moment t is built, the evaporation capacity, the pollution discharge capacity, the phosphate radical, the water supply flow, the furnace water volume, the water supply hardness, the steam humidity and the running time of the steam system at the moment t are input, and the phosphate radical concentration C at the moment t is calculated;
(2) Establishing a mathematical function model of the sodium-phosphorus molar ratio R, and calculating the furnace water R value at the moment t: according to the pH value and the phosphate concentration C, a mathematical function model of the sodium-phosphorus molar ratio R is established, the pH value and the phosphate concentration at the moment t are input, and the furnace water R value at the moment t is calculated;
(3) Build time t Na 3 PO 4 Adding quantity mathematical function model to calculate furnace water Na at time t 3 PO 4 The addition amount is as follows: according to the phosphate radical, the phosphate radical of the control point, the furnace water R, the control point R and Na of the steam system 3 PO 4 Solution concentration, build up of time t Na 3 PO 4 The mathematical function model of the addition quantity is input into the system, namely the concentration of phosphate radical at the time t, phosphate radical at the control point, furnace water R at the time t, control point R and Na 3 PO 4 Solution concentration, solution furnace water Na at time t 3 PO 4 The addition amount is calculated;
(4) Establishing NaH at t moment 2 PO 4 Adding quantity mathematical function model to calculate furnace water NaH at time t 2 PO 4 The addition amount is as follows: according to the phosphate radical, the phosphate radical of the control point, the furnace water R, the control point R and the NaH of the steam system 2 PO 4 Solution concentration, naH at t moment is established 2 PO 4 The addition quantity mathematical function model is input into the system, namely the concentration of phosphate radical at the time t, phosphate radical at the control point, furnace water R at the time t, control point R and NaH 2 PO 4 Solution concentration, and solving furnace water NaH at time t 2 PO 4 The adding amount of the furnace water is regulated by the concentration of phosphate radical, R and the adding amount of phosphate, so as to realize the water quality regulation of the furnace water.
The expression of the mathematical function model of the phosphate concentration at the moment t in the step (1) is as follows:
Figure BDA0003297623670000061
wherein:
f 1 (p,W,u,H,Q,C 0 ) -a function;
f 2 (p,W,u,V 0 ) -a function;
f 3 (p, W, u, H, Q) -function;
c0—initial phosphate concentration;
phosphate concentration at C-t;
t-elapsed time from C0 to C;
v0-furnace water volume;
h-hardness of water supply;
q-feed water flow;
p-discharge capacity;
u-steam humidity;
w-evaporation amount.
The function f 1 (p,W,u,H,Q,C 0 ) Is p, W, u, H, Q, C 0 As p, W, u, H, Q, C 0 Is increased and decreased; the function f 2 (p,W,u,V 0 ) Is p, W, u, V 0 F is a function of (f) 2 (p,W,u,V 0 ) Is a linear function of p, W, u, decreasing with increasing f 2 (p,W,u,V 0 ) V of yes 0 Inverse proportional function, following V 0 Is increased and decreased; the function f 3 (p, W, u, H, Q) is a function of p, W, u, H, Q, f 3 (p, W, u, H, Q) is a complex function of p, W, u, decreasing with increasing p, W, u, f 3 (p, W, u, H, Q) is proportional to H, QThe example function decreases with increasing H, Q and increases with decreasing.
The pH value in the step (2) is the detection value of the pH of furnace water, and is generated by phosphate hydrolysis, and the range is as follows: the pH value is more than or equal to 9 and less than or equal to 11.
The molar ratio R of sodium to phosphorus in the step (2) is the ratio of phosphate hydrolysis sodium ions to phosphate radicals, and the range is as follows: pH is more than or equal to 2 and less than or equal to 3; the R value is calculated by solving a mathematical function model of the R value and the furnace water phosphate concentration C, pH at the moment t, and the mathematical function model expression of the R value is as follows:
R=f 4 (pH,C)
wherein the R value is an exponential function of the pH value, and the R value increases and decreases with increasing pH value; the R value is a hyperbolic function of the phosphate concentration C at time t, and decreases as the C value increases, and increases as the C value increases.
Na in the step (3) 3 PO 4 The concentration of the independent aqueous solution is 1 to 10 percent, and the adding amount of the independent aqueous solution is Na 3 PO 4 Furnace water R at the moment of adding quantity G and t and sodium-phosphorus mole ratio R at control point Control device Phosphate radical concentration C at time t and control point phosphate radical concentration C Control device Obtaining a mathematical function model through calculation; na (Na) 3 PO 4 The mathematical function model expression of the addition amount G is as follows:
Figure BDA0003297623670000071
g and R, R in the formula Control device 、C、C Control device In linear function, G value is related to R Control device 、C Control device The value increases and decreases, the G value decreases and increases as the R, C value increases and decreases.
NaH in the step (4) 2 PO 4 The concentration of the independent aqueous solution is 1 to 10 percent, and the adding amount of the independent aqueous solution is NaH 2 PO 4 Dosage G 1 Molar ratio R of sodium to phosphorus with furnace water R and control point at time t Control device Phosphate concentration C at time t and phosphate concentration C at control point Control device Obtaining a mathematical function model through calculation; naH (NaH) 2 PO 4 Dosage G 1 The mathematical function model expression of (2) is as follows:
Figure BDA0003297623670000082
g in 1 And R, R Control device 、C、C Control device In linear function relation, G 1 Value with R Control device The C value increases and decreases, the G value increases with R, C Control device The value increases and increases, and decreases.
In the specific implementation of the invention, the furnace water adopts a continuous coordination phosphate treatment mode, a phosphate mathematical function model is established according to the evaporation capacity, the pollution discharge capacity, the initial phosphate concentration, the water supply flow, the furnace water volume, the water supply hardness, the steam humidity and the running time of a steam system, the evaporation capacity, the pollution discharge capacity, the initial phosphate concentration, the water supply flow, the water supply hardness, the steam humidity and the running time of the system are input at the moment t, and the phosphate concentration at the moment t is calculated. The phosphate mathematical function model expression is as follows:
Figure BDA0003297623670000081
function f 1 (p,W,u,H,Q,C 0 ) Is p, W, u, H, Q, C 0 As p, W, u, H, Q, C 0 And increases and decreases.
Function f 2 (p,W,u,V 0 ) Is p, W, u, V 0 F is a function of (f) 2 (p,W,u,V 0 ) Is a linear function of p, W, u, decreasing with increasing p, W, u, decreasing with decreasing p, W, u. f (f) 2 (p,W,u,V 0 ) V of yes 0 Inverse proportional function, following V 0 And increases and decreases.
Function f 3 (p, W, u, H, Q) is a function of p, W, u, H, Q, f 3 (p, W, u, H, Q) is a complex function of p, W, u, increasing with increasing p, W, u, decreasing with decreasing p, W, u. f (f) 3 (p, W, u, H, Q) is a H, Q direct proportional function that decreases with increasing H, Q, decreases and increases。
The online instrument detects the pH value of the furnace water, wherein the pH value is generated by phosphate hydrolysis, and the range is as follows: the pH value is more than or equal to 9 and less than or equal to 11.
And (3) establishing an R mathematical function model according to the pH value and the phosphate concentration, inputting the pH value and the phosphate concentration at the moment t, and calculating the R value of the furnace water at the moment t. The expression of the R mathematical function model is as follows:
R=f 4 (pH,C)
wherein the R value is an exponential function of the pH value, and the R value increases and decreases as the pH value increases. The R value is a hyperbolic function of the phosphate concentration C at time t, and decreases as the C value increases, and increases as the C value increases.
According to the phosphate radical, the phosphate radical of the control point, the furnace water R, the control point R and Na of the steam system 3 PO 4 Concentration of solution, build up of Na 3 PO 4 The mathematical function model of the addition quantity is input into the system, namely the concentration of phosphate radical at the time t, phosphate radical at the control point, furnace water R at the time t, control point R and Na 3 PO 4 Solution concentration, solution furnace water Na at time t 3 PO 4 The addition amount is as follows. Na (Na) 3 PO 4 Is an independent aqueous solution with the concentration of 1 to 10 percent, na 3 PO 4 The mathematical function model expression of the addition amount G is as follows:
Figure BDA0003297623670000091
g and R, R in the formula Control device 、C、C Control device In linear function, G value is related to R Control device 、C Control device Increasing and decreasing the value, and decreasing the G value with R, C,
Figure BDA0003297623670000092
The value increases and decreases and increases.
According to the phosphate radical, the phosphate radical of the control point, the furnace water R, the control point R and the NaH of the steam system 2 PO 4 Solution concentration, build up of NaH 2 PO 4 The addition quantity mathematical function model is input into the system, namely the concentration of phosphate radical at the time t, phosphate radical at the control point, furnace water R at the time t, control point RNaH 2 PO 4 Solution concentration, and solving furnace water NaH at time t 2 PO 4 The addition amount is as follows. Wherein NaH is 2 PO 4 Is an independent aqueous solution with the concentration of 1 to 10 percent, naH 2 PO 4 Dosage G 1 The mathematical function model expression of (2) is as follows:
Figure BDA0003297623670000093
g in 1 And R, R Control device 、C、C Control device In linear function relation, G 1 Value with R Control device 、C、
Figure BDA0003297623670000094
The value increases and decreases, decreases and increases, G 1 Value of R, C Control device The value increases and increases, and decreases.
And the concentration of phosphate radical, R and the addition amount of phosphate are adjusted to realize the water quality adjustment of the furnace water.

Claims (2)

1. The online water quality adjusting method for the low-pressure boiler water is characterized by comprising the following steps of:
(1) The furnace water adopts a continuous coordination phosphate treatment mode, a mathematical function model of the phosphate radical concentration at the moment t is built, and the phosphate radical concentration C at the moment t is solved: according to the evaporation capacity, the pollution discharge capacity, the initial phosphate radical concentration, the water supply flow, the furnace water volume, the water supply hardness, the steam humidity and the running time of a steam system, a mathematical function model of the phosphate radical concentration at the moment t is built, the evaporation capacity, the pollution discharge capacity, the initial phosphate radical concentration, the water supply flow, the furnace water volume, the water supply hardness, the steam humidity and the running time of the steam system at the moment t are input, and the phosphate radical concentration C at the moment t is calculated;
the expression of the mathematical function model of the phosphate concentration at the time t is as follows:
Figure QLYQS_1
wherein: f (f) 1 (p,W,u,H,Q,C 0 ) -a function;
f 2 (p,W,u,V 0 ) -a function;
f 3 (p, W, u, H, Q) -function;
C 0 -starting phosphate concentration;
phosphate concentration at C-t;
t is represented by C 0 Time elapsed until C;
V 0 -furnace water volume;
h-hardness of water supply;
q-feed water flow;
p-discharge capacity;
u-steam humidity;
w is the evaporation capacity;
the function f 1 (p,W,u,H,Q,C 0 ) Is p, W, u, H, Q, C 0 As p, W, u, H, Q, C 0 Is increased and decreased; the function f 2 (p,W,u,V 0 ) Is p, W, u, V 0 F is a function of (f) 2 (p,W,u,V 0 ) Is a linear function of p, W, u, decreasing with increasing f 2 (p,W,u,V 0 ) V of yes 0 Inverse proportional function, following V 0 Is increased and decreased; the function f 3 (p, W, u, H, Q) is a function of p, W, u, H, Q, f 3 (p, W, u, H, Q) is a complex function of p, W, u, decreasing with increasing p, W, u, f 3 (p, W, u, H, Q) is a H, Q direct proportional function that decreases with increasing H, Q and increases with decreasing;
(2) Establishing a mathematical function model of the sodium-phosphorus molar ratio R, and calculating the furnace water R value at the moment t: according to the pH value of the furnace water and the phosphate concentration C, a mathematical function model of the sodium-phosphorus molar ratio R is established, the pH value of the furnace water and the phosphate concentration at the moment t are input, and the furnace water R at the moment t is calculated;
the molar ratio R of sodium to phosphorus is the ratio of phosphate hydrolyzed sodium ions to phosphate radicals, and the range is as follows: pH is more than or equal to 2 and less than or equal to 3; the R value is calculated by solving a mathematical function model of the R value and the furnace water phosphate concentration C, pH at the moment t, and the mathematical function model expression of the R value is as follows:
R=f 4 (pH,C)
wherein the R value is an exponential function of the pH value, and the R value increases and decreases with increasing pH value; the R value is a hyperbolic function of the phosphate concentration C at the moment t, and decreases as the C value increases and increases;
(3) Build time t Na 3 PO 4 Adding quantity mathematical function model to calculate furnace water Na at time t 3 PO 4 The addition amount is as follows: according to the phosphate radical concentration of the steam system, the phosphate radical concentration of the control point, the furnace water R and the control point R Control device Na and Na 3 PO 4 Solution concentration, build up of time t Na 3 PO 4 The addition quantity mathematical function model is input into a system at the time t of the phosphate concentration, the phosphate concentration at the control point, the furnace water R at the time t and the control point R Control device Na and Na 3 PO 4 Solution concentration, solution furnace water Na at time t 3 PO 4 The addition amount is calculated;
the Na is 3 PO 4 The concentration of the independent aqueous solution is 1 to 10 percent, and the adding amount of the independent aqueous solution is Na 3 PO 4 Furnace water R at the moment of adding quantity G and t and sodium-phosphorus mole ratio R at control point Control device Phosphate radical concentration C at time t and control point phosphate radical concentration C Control device Obtaining a mathematical function model through calculation; na (Na) 3 PO 4 The mathematical function model expression of the addition amount G is as follows:
Figure QLYQS_2
g and R, R in the formula Control device 、C、C Control device In linear function, G value is related to R Control device 、C Control device The value increases and increases, decreases and decreases, and the G value increases and decreases as the R, C value increases and increases;
(4) Establishing NaH at t moment 2 PO 4 Adding quantity mathematical function model to calculate furnace water NaH at time t 2 PO 4 The addition amount is as follows: according to the phosphate radical concentration of the steam system, the phosphate radical concentration of the control point, the furnace water R and the control point R Control device NaH (sodium hydrogen carbonate) 2 PO 4 Solution concentration, naH at t moment is established 2 PO 4 The addition quantity mathematical function model is input into a system at the time t of the phosphate concentration, the phosphate concentration at the control point, the furnace water R at the time t and the control point R Control device NaH (sodium hydrogen carbonate) 2 PO 4 Solution concentration, and solving furnace water NaH at time t 2 PO 4 The addition amount is calculated;
the NaH is 2 PO 4 The concentration of the independent aqueous solution is 1 to 10 percent, and the adding amount of the independent aqueous solution is NaH 2 PO 4 Dosage G 1 Molar ratio R of sodium to phosphorus with furnace water R and control point at time t Control device Phosphate concentration C at time t and phosphate concentration C at control point Control device Obtaining a mathematical function model through calculation; naH (NaH) 2 PO 4 Dosage G 1 The mathematical function model expression of (2) is as follows:
Figure QLYQS_3
g in 1 And R, R Control device 、C、C Control device In linear function relation, G 1 Value with R Control device The C value increases and decreases, the G value increases with R, C Control device The value increases and increases, and decreases.
2. The on-line regulation method of low-pressure boiler water quality according to claim 1, wherein the pH value of the boiler water in the step (2) is generated by phosphate hydrolysis, and the range is as follows: the pH value is more than or equal to 9 and less than or equal to 11.
CN202111184258.8A 2021-10-11 2021-10-11 Online adjusting method for water quality of low-pressure boiler water Active CN113880155B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111184258.8A CN113880155B (en) 2021-10-11 2021-10-11 Online adjusting method for water quality of low-pressure boiler water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111184258.8A CN113880155B (en) 2021-10-11 2021-10-11 Online adjusting method for water quality of low-pressure boiler water

Publications (2)

Publication Number Publication Date
CN113880155A CN113880155A (en) 2022-01-04
CN113880155B true CN113880155B (en) 2023-05-05

Family

ID=79006198

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111184258.8A Active CN113880155B (en) 2021-10-11 2021-10-11 Online adjusting method for water quality of low-pressure boiler water

Country Status (1)

Country Link
CN (1) CN113880155B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114853142B (en) * 2022-05-25 2023-08-08 九江七所精密机电科技有限公司 Marine low-pressure boiler water free NaOH regulation and control method and system

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2078001U (en) * 1990-09-15 1991-05-29 大同第二发电厂科学技术协会 Boiler water mole-ratio monitoring instrument
US5132916A (en) * 1990-05-21 1992-07-21 Elsag International B.V. Methodology for ph titration curve estimation for adaptive control
EP0640747A1 (en) * 1993-08-20 1995-03-01 Nalco Chemical Company Boiler system pH/phosphate program control method
CN103159347A (en) * 2013-03-28 2013-06-19 鞍钢股份有限公司 Method for quickly eliminating acid phosphate hiding of coke dry quenching waste heat boiler
CN107601632A (en) * 2017-10-30 2018-01-19 清华大学深圳研究生院 A kind of coagulation Automatic Dosing control method and system
CN108217987A (en) * 2018-01-08 2018-06-29 中国恩菲工程技术有限公司 Waste heat boiler dosing blowdown control method
CN113418184A (en) * 2021-07-10 2021-09-21 湖南华菱湘钢节能发电有限公司 Treatment method for steam drum furnace phosphate hiding phenomenon

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5132916A (en) * 1990-05-21 1992-07-21 Elsag International B.V. Methodology for ph titration curve estimation for adaptive control
CN2078001U (en) * 1990-09-15 1991-05-29 大同第二发电厂科学技术协会 Boiler water mole-ratio monitoring instrument
EP0640747A1 (en) * 1993-08-20 1995-03-01 Nalco Chemical Company Boiler system pH/phosphate program control method
CN103159347A (en) * 2013-03-28 2013-06-19 鞍钢股份有限公司 Method for quickly eliminating acid phosphate hiding of coke dry quenching waste heat boiler
CN107601632A (en) * 2017-10-30 2018-01-19 清华大学深圳研究生院 A kind of coagulation Automatic Dosing control method and system
CN108217987A (en) * 2018-01-08 2018-06-29 中国恩菲工程技术有限公司 Waste heat boiler dosing blowdown control method
CN113418184A (en) * 2021-07-10 2021-09-21 湖南华菱湘钢节能发电有限公司 Treatment method for steam drum furnace phosphate hiding phenomenon

Also Published As

Publication number Publication date
CN113880155A (en) 2022-01-04

Similar Documents

Publication Publication Date Title
Rossum et al. An evaluation of the calcium carbonate saturation indexes
WO2021212777A1 (en) Automatic dosing control system and method for wastewater softening pretreatment system
CN113880155B (en) Online adjusting method for water quality of low-pressure boiler water
CN105759712B (en) The precise control device and method of condensation water Automatic Ammonia adding
CN103771553B (en) The adaptive fuzzy control method of wet flue gas desulfurization waste water evaporation process
CN109521813B (en) A system and method for stabilizing the concentration ratio of circulating water in a thermal power plant
CN102080820A (en) An Optimum Energy Saving Control Method for Steam Boiler Surface Blowdown
CN103880230A (en) Segmental oxidation treatment system and treatment method of thermodynamic system of novel coal-fired power plant
CN103159347B (en) Method for quickly eliminating acid phosphate hiding of coke dry quenching waste heat boiler
CN110564442A (en) Automatic regulating and controlling system for corrosion prevention of distillation tower top process
CN212833139U (en) An automatic dosing control system for a waste water softening pretreatment system
CN112361322A (en) Boiler feed water automatic ammonia adding device and gray prediction feedforward PID control method
CN111396856A (en) A low-level deaerator system
CN111623339A (en) Method for recycling sewage discharged by steam boiler in operation of hot water boiler
CN217007985U (en) A circuit board etching detection and feeding control device with precise feeding function
CN207313319U (en) Recirculated water Intelligent medicine adding device
CN206145657U (en) Exhaust -heat boiler flue gas discharge system
CN112125359B (en) Automatic dosing control system and control method suitable for electric furnace water system
CN204440183U (en) A kind of decarburization hard-off water is the recirculated water concentration rate control system of moisturizing
CN212057244U (en) Low-level deaerator system
CN110777373B (en) Sodium hydroxide treatment device and method for high-pressure-increasing drainage system of power plant
CN206881494U (en) A kind of lime stone slurry supply system of wide Load Regulation
CN115078670A (en) Water vapor simulation test device and method for power plant
CN114853142B (en) Marine low-pressure boiler water free NaOH regulation and control method and system
CN202415287U (en) Quality adjusting device of water produced by desalination of seawater

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