CN104569281B - Judge Al3+The method that the lime stone slurry that causes is poisoning - Google Patents

Judge Al3+The method that the lime stone slurry that causes is poisoning Download PDF

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CN104569281B
CN104569281B CN201510005279.7A CN201510005279A CN104569281B CN 104569281 B CN104569281 B CN 104569281B CN 201510005279 A CN201510005279 A CN 201510005279A CN 104569281 B CN104569281 B CN 104569281B
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lime stone
poisoning
hco
formula
stone slurry
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CN104569281A (en
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华晓宇
施浩勋
陈统钱
滕敏华
裘立春
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TAIZHOU POWER-STATION
ZHEJIANG CLEAN COAL TECHNOLOGY RESEARCH DEVELOPMENT CENTER
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TAIZHOU POWER-STATION
ZHEJIANG CLEAN COAL TECHNOLOGY RESEARCH DEVELOPMENT CENTER
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Abstract

Disclosure one judges Al3+The method that the lime stone slurry that causes is poisoning, it is characterised in that the method step comprises: (1) first measures the pH value of lime stone slurry; (2) temperature of lime stone slurry is then measured; (3) calculate obtain [HCO in serosity according to the chemical equilibrium in serosity, charge balance relational expression- 3] and [CO2- 3] concentration; (4) according to [HCO drawn in step (3)- 3] and [CO2- 3] concentration result of calculation, calculate the Al causing lime stone slurry poisoning3+Concentration range. The present invention has can accurately detect Al3+The concentration limit that the lime stone slurry that causes is poisoning, thus the advantage that forewarning function is successfully provided.

Description

Judge Al3+The method that the lime stone slurry that causes is poisoning
Technical field
Invention Announce a kind of judgement Al3+The method that the lime stone slurry that causes is poisoning, calculates the HCO in serosity by chemical equilibrium, charge balance- 3And CO2- 3Concentration, thus calculating and drawing the Al causing lime stone slurry poisoning3+Concentration limit. This determination methods is mainly used in thermal power plant's wet desulfurization of flue gas by limestone-gypsum method technique.
Background technology
Coal occupies absolutely essential status in the primary energy structure of consumer demand of China, is also the main fuel of power plants. Along with the development of power industry, coal-fired produced SO2Pollute day by day serious. For controlling SO2Pollute; 2011; Environmental Protection Department and national quality supervision and inspection general bureau combine issue " fossil-fuel power plant atmospheric pollutant emission standard " (GB11223-2011); the Thermal Power Plant Construction project of different times has been respectively provided corresponding Air Pollutant Emission control requirement; under these circumstances; thermal power plant in all parts of the country carries out the construction of flue-gas desulfurizing engineering one after another, thus significantly alleviating the discharge pollution on the environment of sulfur dioxide.
In various flue gas desulfurization techniques, wet desulfurization of flue gas by limestone-gypsum method technique becomes present stage most widely used flue gas desulfurization technique with its plurality of advantages. In this technical process, the dissolving of limestone is one of important rate determining step. But, come from the Al of institute's dissolution in the flying dust of flue gas3+Often suppress the dissolving of limestone so that lime stone slurry neutral and alkali material concentration reduces, to SO2Absorbability declines, and namely lime stone slurry is poisoning, thus being substantially reduced smoke desulfurization efficiency. And how to detect Al3+The concentration limit that the lime stone slurry that causes is poisoning, sets up concentration warning value for units such as power plant facilitating, for successfully solving the poisoning offer important references meaning of lime stone slurry.
Summary of the invention:
The present invention is directed to the above-mentioned deficiency of prior art, it is provided that one can accurately detect Al3+The concentration limit that the lime stone slurry that causes is poisoning, thus successfully providing the judgement Al of forewarning function3+The method that the lime stone slurry that causes is poisoning.
In order to solve above-mentioned technical problem, the technical solution used in the present invention is: one judges Al3+The method that the lime stone slurry that causes is poisoning, the method step comprises:
(1) pH value of lime stone slurry is first measured;
(2) temperature of lime stone slurry is then measured;
(3) calculate obtain HCO in serosity according to the chemical equilibrium in serosity, charge balance relational expression- 3And CO2- 3Concentration;
(4) according to step (3) HCO- 3And CO2- 3Concentration result of calculation, it is judged that cause the Al that lime stone slurry is poisoning3+Concentration range.
Al3+The principles of chemistry causing lime stone slurry poisoning are in that, on the one hand, Al3+With HCO- 3��CO2- 3Between there is double; two hydrolysis, generate Al (OH)3Precipitation covers limestone particle surface, the serious dissolving suppressing limestone; On the other hand, owing to limestone cannot dissolve, it is impossible to provide the HCO with alkalescence- 3��CO2- 3, therefore to SO2Absorbability decline to a great extent, desulfuration efficiency significantly reduces, and aggregate performance is that lime stone slurry is poisoning. The chemical equation of this pair of hydrolysis is as follows:
Al3++3HCO- 3=Al (OH)3+3CO2(1)
2Al3++3CO2- 3+3H2O=2Al (OH)3+3CO2(2)
So, the equilibrium concentration of various ion can just be calculated according to the chemical equilibrium between ions various in lime stone slurry, charge balance relational expression, thus extrapolating the Al causing lime stone slurry poisoning3+Concentration limit.
In lime stone slurry, there is following chemical reaction:
The dissolving of limestone:
CaCO3=Ca2++CO3 2-(3)
H2CO3Single order ionization:
CO2(aq)+H2O=H++HCO3 -(4)
H2CO3Second order ionization:
HCO- 3=H++CO3 2-(5)
The ionization equilibrium of water:
H2O=H++OH-(6)
Charge balance:
2[Ca2+]+[H+]=[OH-]+[HCO- 3]+2[CO3 2-](7)
So, there is following relational expression between the various ion concentrations in serosity:
[H+] * [OH-]=Kw(8)
In formula, KwIt is the ionic product of water, is the function of temperature.
[Ca2+]*[CO3 2-]=Kcp(9)
In formula, KcpIt is CaCO3Solubility product, be the function of temperature.
[ H + ] * [ HCO 3 - ] [ CO 2 ( aq ) ] = K c 1 - - - ( 10 )
In formula, Kc1It is H2CO3Single order ionization constant, be the function of temperature.
[ H + ] * [ CO 3 2 - ] [ H C O 3 - ] = K c 2 - - - ( 11 )
In formula, Kc2It is H2CO3Second order ionization constant, be the function of temperature;
2 [ Ca 2 + ] + [ H + ] = [ OH - ] + [ HCO 3 - ] + 2 [ CO 3 2 - ] - - - ( 12 )
[H+]=10-5.5(13)
Solve by the equation group of formula (8)-Shi (13) simultaneous, just can obtain HCO in serosity- 3��CO2 -3The concentration of two kinds of ions, further according to the stoichiometric relationship of formula (1) and formula (2), just can draw the Al causing lime stone slurry poisoning3+The theoretical value of concentration limit, for 3.83mmol/L.
Dependent constant value under different temperatures can be calculated according to the following formula:
Kcp=10^ (-171.9065-0.077993*T+2839.319/T+71.595*log10 (T))
(14)
Kc1=exp (-12092.1/T-36.7816*log (T)+235.482) (15)
Kc2=exp (-12431.7/T-35.4819*log (T)+220.067) (16)
Kw=exp (-13445.9/T-22.4773*log (T)+140.932) (17).
According to above-mentioned formula, calculating can obtain pH=5.5, and temperature causes the Al that serosity is poisoning at 55 DEG C3+Concentration limit be 3.83mmol/L.
Al3+The determination methods that the lime stone slurry that causes is poisoning: on the basis that above-mentioned theory calculates, by Al in wet method fume desulfurizing system slurry pool3+The rate of rise of concentration and minimizing speed, just can determine whether out Al3+Whether it is likely to result in lime stone slurry poisoning.
Al in slurry pool3+Rate of rise:
M1=Vfg*Ffa*Fal*Fd*54/102*/27(18)
In formula (18), M1It is Al in slurry pool3+Concentration rate of rise, mmol/h;
VfaIt is the fly ash content in flue gas, mg/m3,
FalIt is the alumina content in flying dust,
FdIt is the dissolution number of aluminum in flying dust,
54/102, Al2O3In Al content,
27 is the atomic weight of Al;
Al in slurry pool3+Rate of discharge:
M2=3.83*Vww*1000(19)
In formula, 3.83 (lower limit at 55 DEG C should be 3.83mmol/L) are the Al causing lime stone slurry poisoning3+Concentration limit value, VwwIt is desulphurization system discharge of wastewater speed, unit m3/h��
Utilize formula (18) and formula (19), it is possible to calculate M1And M2Numerical value, if M1<M2, serosity will not be poisoning, if M1>M2, there is very big poisoning possibility in serosity.
The * related in the present invention represents the multiplication sign "��" in multiplication and division.
Accompanying drawing explanation
When Fig. 1 slurry temperature is 55 DEG C, [HCO in serosity under different pH value- 3] and [CO2- 3] Al corresponding to equilibrium concentration3 +Concentration limit graph of relation.
Detailed description of the invention
The present invention is described in further detail by the examples below, but the present invention is not limited solely to following example.
Embodiment 1:
According to formula (8)-Shi (13) when slurry temperature is 25 DEG C, calculate [the HCO in serosity under different pH value- 3] and [CO2- 3] equilibrium concentration, Al3+Concentration limit calculated by the stoichiometric relationship of formula (1) and formula (2), result is as shown in table 1.
[HCO in serosity during 1.25 DEG C of table- 3] and [CO2- 3] equilibrium concentration
PH value [HCO- 3](mmol/L) [CO2- 3](mmol/L) [Al3+](mmol/L)
3.5 194.5 2.88��10-5 64.83
4 109.3 5.13��10-5 36.43
4.5 61.47 9.11��10-5 20.49
5 34.56 1.62��10-4 11.52
5.5 19.43 2.88��10-4 6.48
6 10.92 5.12��10-4 3.64
6.5 6.14 9.11��10-4 2.05
As can be seen from Table 1, with HCO- 3Compare, CO2- 3Concentration only small, it is possible to ignore, therefore calculate Al3+The concentration simply considered during concentration, the Al calculated3+Concentration limit as shown in table 1. From table 1 it follows that in temperature one timing, along with the rising of pH value, Al3+Concentration limit be gradually lowered. It is to say, when pH value is higher, Al3+The inhibition that limestone is dissolved is more notable. This is consistent with result of the test, it was demonstrated that the correctness of these computational methods.
When slurry temperature is 55 DEG C, calculate under different pH value in serosity and equilibrium concentration, Al3+Concentration limit calculated by the stoichiometric relationship of formula (1) and formula (2), result is as shown in Figure 1. From figure 1 it appears that along with the rising of slurry pH value, it is suppressed that the Al3+ concentration that limestone dissolves is gradually lowered, and this is consistent with the rule in embodiment 1. It addition, for single pH value: when pH=5.5, along with slurry temperature is increased to 55 DEG C from 25 DEG C, Al3+Concentration limit be reduced to 3.83mmol/L from 6.48mmol/L, this has promoted CO mainly due to the rising of temperature2From liquid phase to the release of gas phase, caused by causing in serosity that concentration reduces, determine pH value burette test result and also indicate that, when reaction temperature is 55 DEG C, in lime stone slurry, add the Al of 3.83mmol/L3+, the dissolving of limestone cannot be carried out completely, and this all describes the correctness of this method.
For certain desulphurization system, relevant parameter is as shown in table 2:
The relevant parameter of table 2. desulphurization system 1
Can be calculated according to formula (18), (19), M1=10165.27mmol/h, M2=22980mmol/h, M1<M2, therefore serosity will not be poisoning.
Embodiment 2:
For another desulphurization system, relevant parameter is as shown in table 3.
The relevant parameter of table 3. desulphurization system 3
Can be calculated according to formula (18), (19), M1=23916.3mmol/h, M2=22980mmol/h, M1>M2, serosity will be poisoning.

Claims (1)

1. one kind judges Al3+The method that the lime stone slurry that causes is poisoning, it is characterised in that the method step comprises:
(1) pH value of lime stone slurry is first measured;
(2) temperature of lime stone slurry is then measured;
(3) calculate obtain [HCO in serosity according to the chemical equilibrium in serosity, charge balance relational expression- 3] and [CO2- 3] concentration;
(4) according to [HCO drawn in step (3)- 3] and [CO2- 3] concentration result of calculation, calculate the Al causing lime stone slurry poisoning3+Concentration range;
Al3+The principles of chemistry causing lime stone slurry poisoning are in that, on the one hand, Al3+With HCO- 3��CO2- 3Between there is double; two hydrolysis, generate Al (OH)3Precipitation covers limestone particle surface, the serious dissolving suppressing limestone; On the other hand, owing to limestone cannot dissolve, it is impossible to provide the HCO with alkalescence- 3��CO2- 3, therefore to SO2Absorbability decline to a great extent, desulfuration efficiency significantly reduces, and aggregate performance is that lime stone slurry is poisoning;The chemical equation of this pair of hydrolysis is as follows:
Al3++3HCO- 3=Al (OH)3+3CO2(1)
2Al3++3CO2- 3+3H2O=2Al (OH)3+3CO2(2);
In described lime stone slurry, there is following chemical reaction:
The dissolving of limestone:
CaCO3=Ca2++CO3 2-(3)
H2CO3Single order ionization:
CO2(aq)+H2O=H++HCO3 -(4)
H2CO3Second order ionization:
HCO- 3=H++CO3 2-(5)
The ionization equilibrium of water:
H2O=H++OH-(6)
Charge balance:
2[Ca2+]+[H+]=[OH-]+[HCO- 3]+2[CO3 2-] (7);
Following relational expression is there is between various ion concentrations in serosity:
[H+]*[OH-]=Kw(8)
In formula, KwIt is the ionic product of water, is the function of temperature;
[Ca2+]*[CO3 2-]=Kcp(9)
In formula, KcpIt is the solubility product of CaCO3, is the function of temperature;
&lsqb; H + &rsqb; * &lsqb; HCO 3 - &rsqb; &lsqb; CO 2 ( a q ) &rsqb; = K c 1 - - - ( 10 )
In formula, Kc1It is H2CO3Single order ionization constant, be the function of temperature;
&lsqb; H + &rsqb; * &lsqb; CO 3 2 - &rsqb; &lsqb; HCO 3 - &rsqb; = K c 2 - - - ( 11 )
In formula, Kc2It is H2CO3Second order ionization constant, be the function of temperature;
2 &lsqb; Ca 2 + &rsqb; + &lsqb; H + &rsqb; = &lsqb; OH - &rsqb; + &lsqb; HCO 3 - &rsqb; + 2 &lsqb; CO 3 2 - &rsqb; - - - ( 12 )
[H+]=10-5.5(13)
Solve by the equation group of formula (8)-Shi (13) simultaneous, obtain HCO in serosity- 3��CO2 -3The concentration of two kinds of ions, further according to the stoichiometric relationship of formula (1) and formula (2), draws the Al causing lime stone slurry poisoning3+The theoretical value of concentration limit;
Dependent constant value under different temperatures is calculated according to the following formula:
Kcp=10^ (-171.9065-0.077993*T+2839.319/T+71.595*log10 (T)) (14)
Kc1=exp (-12092.1/T-36.7816*log (T)+235.482) (15)
Kc2=exp (-12431.7/T-35.4819*log (T)+220.067) (16)
Kw=exp (-13445.9/T-22.4773*log (T)+140.932) (17);
By Al in wet method fume desulfurizing system slurry pool3+The rate of rise of concentration and minimizing speed, just can judge Al3+Whether it is likely to result in lime stone slurry poisoning, particularly as follows:
Al in slurry pool3+Rate of rise:
M1=Vfg*Ffa*Fal*Fd*54/102*/27(18)
In formula (18), M1It is Al in slurry pool3+Concentration rate of rise, mmol/h;
VfaIt is the fly ash content in flue gas, mg/m3;
Fal is the alumina content in flying dust;
Fd is the dissolution number of aluminum in flying dust
54/102, Al2O3In Al content;
27 is the atomic weight of Al
Al in slurry pool3+Rate of discharge:
M2=3.83*Vww*1000(19)
In formula, 3.83 is the Al causing lime stone slurry poisoning3+Concentration limit value, Vww is desulphurization system discharge of wastewater speed, m3/ h;
Utilize formula (18) and formula (19), calculate M1And M2Numerical value, if M1<M2, serosity will not be poisoning, if M1>M2, serosity exists poisoning.
CN201510005279.7A 2015-01-05 2015-01-05 Judge Al3+The method that the lime stone slurry that causes is poisoning Active CN104569281B (en)

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