CN111477286A - Method for measuring and calculating content of chlorine in fly ash in desulfurization wastewater zero-discharge system - Google Patents
Method for measuring and calculating content of chlorine in fly ash in desulfurization wastewater zero-discharge system Download PDFInfo
- Publication number
- CN111477286A CN111477286A CN202010196178.3A CN202010196178A CN111477286A CN 111477286 A CN111477286 A CN 111477286A CN 202010196178 A CN202010196178 A CN 202010196178A CN 111477286 A CN111477286 A CN 111477286A
- Authority
- CN
- China
- Prior art keywords
- fly ash
- content
- coal
- ash
- desulfurization wastewater
- 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.)
- Withdrawn
Links
- 239000010881 fly ash Substances 0.000 title claims abstract description 105
- 239000000460 chlorine Substances 0.000 title claims abstract description 97
- 238000006477 desulfuration reaction Methods 0.000 title claims abstract description 50
- 230000023556 desulfurization Effects 0.000 title claims abstract description 50
- 239000002351 wastewater Substances 0.000 title claims abstract description 48
- 229910052801 chlorine Inorganic materials 0.000 title claims abstract description 38
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 title claims abstract description 37
- 238000000034 method Methods 0.000 title claims abstract description 34
- 239000003245 coal Substances 0.000 claims abstract description 55
- 239000002956 ash Substances 0.000 claims abstract description 27
- 239000003546 flue gas Substances 0.000 claims abstract description 21
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 20
- 238000002485 combustion reaction Methods 0.000 claims description 9
- 238000004364 calculation method Methods 0.000 claims description 5
- 238000012544 monitoring process Methods 0.000 claims description 4
- 238000002156 mixing Methods 0.000 abstract description 3
- 239000000428 dust Substances 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical class O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- 235000019738 Limestone Nutrition 0.000 description 4
- 239000010440 gypsum Substances 0.000 description 4
- 229910052602 gypsum Inorganic materials 0.000 description 4
- 239000006028 limestone Substances 0.000 description 4
- 238000005259 measurement Methods 0.000 description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 3
- 239000004568 cement Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 230000002745 absorbent Effects 0.000 description 2
- 239000002250 absorbent Substances 0.000 description 2
- 239000010883 coal ash Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- 102220505380 Ubiquitin thioesterase ZRANB1_M26A_mutation Human genes 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- 150000001804 chlorine Chemical class 0.000 description 1
- -1 chlorine ions Chemical class 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 238000010561 standard procedure Methods 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
Images
Classifications
-
- G—PHYSICS
- G16—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR SPECIFIC APPLICATION FIELDS
- G16C—COMPUTATIONAL CHEMISTRY; CHEMOINFORMATICS; COMPUTATIONAL MATERIALS SCIENCE
- G16C20/00—Chemoinformatics, i.e. ICT specially adapted for the handling of physicochemical or structural data of chemical particles, elements, compounds or mixtures
- G16C20/20—Identification of molecular entities, parts thereof or of chemical compositions
-
- G—PHYSICS
- G16—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR SPECIFIC APPLICATION FIELDS
- G16C—COMPUTATIONAL CHEMISTRY; CHEMOINFORMATICS; COMPUTATIONAL MATERIALS SCIENCE
- G16C20/00—Chemoinformatics, i.e. ICT specially adapted for the handling of physicochemical or structural data of chemical particles, elements, compounds or mixtures
- G16C20/70—Machine learning, data mining or chemometrics
Landscapes
- Engineering & Computer Science (AREA)
- Computing Systems (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Theoretical Computer Science (AREA)
- Bioinformatics & Computational Biology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Crystallography & Structural Chemistry (AREA)
- Evolutionary Computation (AREA)
- Computer Vision & Pattern Recognition (AREA)
- Treating Waste Gases (AREA)
- Medical Informatics (AREA)
- General Health & Medical Sciences (AREA)
- Artificial Intelligence (AREA)
- Databases & Information Systems (AREA)
- Health & Medical Sciences (AREA)
- Data Mining & Analysis (AREA)
- Physics & Mathematics (AREA)
- Spectroscopy & Molecular Physics (AREA)
- Software Systems (AREA)
Abstract
A method for measuring and calculating the content of chlorine in fly ash in a desulfurization wastewater zero-discharge system specifically comprises the following steps: the method comprises the following steps: measuring the Cl content; step two: determining daily consumption of coal, daily output of fly ash, daily output of desulfurization wastewater and daily output of fly ash; step three: measuring the ash content in the fire coal; step four: calculating the Cl ratio of each component; step five: calculating the daily yield coefficient of the fly ash; step six: establishing a fly ash content measuring and calculating model of a flue gas treatment system; the method integrates and simplifies the working conditions of the coal-fired power plant to a certain extent in the measuring and calculating process, so that when the coal quality changes, the chlorine content of the fly ash can be predicted in advance only by detecting the Cl content and the ash content of the coal, the coal blending is guided, the chlorine source head input is controlled, and the Cl standard exceeding of the fly ash is avoided.
Description
Technical Field
The invention belongs to the field of flue gas treatment, and particularly relates to a method for measuring and calculating the content of chlorine in fly ash in a desulfurization wastewater zero-discharge system.
Background
Limestone-gypsum wet desulphurization is the most widely used and technically mature desulphurization process in the world and is widely applied to SO in coal-fired flue gas2And (5) treating. The desulfurization waste water produced by the process has pH of 4-6 and contains a large amount of suspended substances (gypsum particles, SiO)2Hydroxides of A1 and Fe), chloride ions and trace heavy metals such As As, Cd, Cr, Hg and the like, the salt content and suspended matters of the desulfurization wastewater reach tens of thousands mg/L, the desulfurization wastewater is typical high-salt wastewater, the desulfurization wastewater is seriously harmful to the environment due to direct discharge, the desulfurization wastewater must be treated to be discharged, and the zero discharge of the desulfurization wastewater is a necessary trend of environmental standard development.
The waste heat flue gas evaporation process is one of main technical routes for realizing zero emission of desulfurization wastewater, a large amount of miscellaneous salts are separated out from the desulfurization wastewater after evaporation and concentration, the separated particles containing chlorine salts are carried into an electrostatic dust collector and finally mixed into fly ash, however, the quality of the fly ash is changed due to the increase of the content of chlorine ions in the fly ash, and the product production of downstream users of the fly ash is influenced. For example, in the cement manufacturing industry, too high a chloride ion level will affect the performance of the cement, and industry standards place clear demands on the maximum chloride ion level in the cement. Therefore, the chlorine balance model of the flue gas treatment system is analyzed, the chlorine content of each material in the system is detected, the fly ash chlorine content measuring and calculating method is established, the chlorine content of the fly ash is accurately predicted, the coal blending is guided, the chlorine source head input is controlled, the over-high chlorine content of the fly ash is avoided, and the method has important innovation and practical significance.
Disclosure of Invention
The invention aims to provide a method for measuring and calculating the content of chlorine in fly ash in a desulfurization wastewater zero-discharge system, which aims to solve the problem of measuring and calculating the content of chlorine in fly ash from the source in the desulfurization wastewater zero-discharge system in the prior art, simplify the measuring and calculating method and improve the working efficiency. Measurement and calculation
In order to achieve the purpose, the invention adopts the following technical scheme:
a method for measuring and calculating the content of chlorine in fly ash in a desulfurization wastewater zero-discharge system is characterized by comprising the following steps:
the method mainly comprises the following steps of (1) in a flue gas treatment system, wherein Cl is mainly from fire coal, the Cl in the fire coal is combusted and then enters fly ash, desulfurization wastewater, furnace slag, desulfurization gypsum and clean flue gas according to a certain proportion, in a wastewater zero discharge system, Cl is mainly from fly ash and desulfurization wastewater, meanwhile, part of ash in the fire coal is converted into fly ash after combustion, and according to the principle of material conservation, a measuring and calculating model of Cl content in the fly ash can be established by detecting Cl content of each component in the fire coal flue gas treatment system, and the method specifically comprises the following steps:
the method comprises the following steps: and (3) determining the Cl content: measuring Cl content in fire coal, fly ash and desulfurization wastewater under the same working condition, and respectively using C1、C2、C3Expressed in units of. mu.g/g,. mu.g/g and mg/L, respectively;
step two: determining the daily consumption of the coal, the daily output of the fly ash, the daily output of the desulfurization wastewater and the daily output of the fly ash: collecting daily consumption of coal, daily output of fly ash, daily output of desulfurization wastewater and daily output of fly ash by using a monitoring system of a coal-fired power plant, and respectively using M1、M2、M3、M4The expression is that the units are t/d;
step three: determining the ash content in the fire coal: the ash content percentage in the fire coal is represented by A;
step four: calculating the Cl ratio of each component: calculating the ratio K of Cl content in fly ash to Cl content in fire coal1=(C2×M2)/(C1×M1) And the ratio K of the Cl content in the desulfurization wastewater to the Cl content in the fire coal2=(C3×M3)/(C1×M1)；
Step five: calculating the daily yield coefficient of the fly ash: most of ash generated after coal combustion is converted into fly ash, so the daily yield coefficient K of the fly ash3=M4/(A×M1)；
Step six: fly ash for establishing flue gas treatment systemThe content measurement model comprises: chlorine content percentage C in fly ash4The chlorine content in the fly ash and the desulfurization wastewater can be calculated, and the daily yield of the fly ash can be calculated from the yield of the ash, so that the calculation formula of the chlorine content of the fly ash is as follows:
C4=(C2×M2+C3×M3)/M4=(K1+K2)×(C1×M1)/K3×(A×M1)=[(K1+K2)×C1]/(K3×A)；
a fly ash content measuring and calculating model of the flue gas treatment system is established through the formula, and the chlorine content of the fly ash can be measured and calculated only by detecting the Cl content and the ash content of the fire coal.
Compared with the prior art, the invention has the following characteristics and beneficial effects:
the method integrates and simplifies the working conditions of the coal-fired power plant to a certain extent in the measuring and calculating process, can predict the chlorine content of the fly ash in advance only by detecting the Cl content and the ash content of the coal when the coal quality changes, avoids the Cl content of the fly ash exceeding the standard, has strong operability and extremely low cost, greatly improves the coal blending efficiency of the coal-fired power plant, and has practical application and popularization values.
Drawings
Fig. 1 is a flow chart of measurement and calculation according to the present invention.
Detailed Description
In order to make the technical means, innovative features, objectives and functions realized by the present invention easy to understand, the present invention is further described below.
The examples described herein are specific embodiments of the present invention, are intended to be illustrative and exemplary in nature, and are not to be construed as limiting the scope of the invention. In addition to the embodiments described herein, those skilled in the art will be able to employ other technical solutions which are obvious based on the disclosure of the claims and the specification of the present application, and these technical solutions include technical solutions which make any obvious replacement or modification for the embodiments described herein.
In the waste water zero discharge system, the Cl in the fly ash is mainly the fly ash and the desulfurization waste water, and simultaneously, part of ash content in the coal ash is converted into the fly ash after combustion, and the Cl in the coal is supposed to be completely released under the boiler combustion condition and enter a subsequent flue gas treatment system; because the content and the dosage of chlorine in the limestone of the desulfurization absorbent and the desulfurization process water are low, the influence on the Cl balance of the system is small, and the source of Cl ions in the coal-fired flue gas system ignores the limestone and the process water; assuming that all Cl in the desulfurization wastewater enters the fly ash, and neglecting the mass of the fly ash; assuming that all fly ash is derived from ash content of coal, and the dust removal efficiency of dust removal equipment is 100%; on the basis of the principle of conservation of substances, a model for measuring and calculating the Cl content in the fly ash can be established by detecting the Cl content of each component in a coal-fired flue gas treatment system, and the method comprises the following steps:
the method comprises the following steps: and (3) determining the Cl content: measuring Cl content in fire coal, fly ash and desulfurization wastewater under the same working condition, and respectively using C1、C2、C3Represents;
step two: determining the daily consumption of the coal, the daily output of the fly ash, the daily output of the desulfurization wastewater and the daily output of the fly ash: collecting daily consumption of coal, daily output of fly ash, daily output of desulfurization wastewater and daily output of fly ash by using a monitoring system of a coal-fired power plant, and respectively using M1、M2、M3、M4Represents;
step three: determining the ash content in the fire coal: the ash content percentage in the fire coal is represented by A;
step four: calculating the Cl ratio of each component: calculating the ratio K of Cl content in fly ash to Cl content in fire coal1=(C2×M2)/(C1×M1) And the ratio K of the Cl content in the desulfurization wastewater to the Cl content in the fire coal2=(C3×M3)/(C1×M1)；
Step five: calculating the daily yield coefficient of the fly ash: produced by combustion of coalAsh, most of which is converted to fly ash, so the coefficient of daily yield of fly ash, K3=M4/(A×M1)；
Step six: establishing a fly ash content measuring and calculating model of a flue gas treatment system: chlorine content C in fly ash4The chlorine content in the fly ash and the desulfurization wastewater can be calculated, and the daily yield of the fly ash can be calculated from the yield of the ash, so that the calculation formula of the chlorine content of the fly ash is as follows:
C4=(C2×M2+C3×M3)/M4=(K1+K2)×(C1×M1)/K3×(A×M1)=[(K1+K2)×C1]/(K3×A)；
a fly ash content measuring and calculating model of the flue gas treatment system is established through the formula, and the chlorine content of the fly ash can be measured and calculated only by detecting the Cl content and the ash content of the fire coal.
The invention relates to a method for measuring and calculating the content of chlorine in fly ash in a desulfurization wastewater zero-discharge system, which is characterized in that the Cl in a flue gas treatment system is mainly coal, Cl in the coal is combusted and then enters fly ash, desulfurization wastewater, furnace slag, desulfurization gypsum and clean flue gas in a certain proportion, and in the wastewater zero-discharge system, Cl in the fly ash is mainly fly ash and desulfurization wastewater, and meanwhile, part of ash in the coal is converted into fly ash after combustion, so that on the basis of the principle of conservation of substances, a measuring and calculating model of the content of Cl in the fly ash can be established by detecting the Cl content of each component in the coal-fired flue gas treatment system, and the method comprises the following specific steps:
a) measuring Cl content of fire coal, fly ash and desulfurization wastewater under the same working condition (respectively using C)1、C2、C3Represents); in the step, the Cl content of various samples is detected by adopting a standard method M26A recommended by the national environmental protection agency of America to obtain C1=123.20 μg/g，C2=67.80 μg/g，C3=2515.40 mg/L；
b) Collecting daily consumption of coal, daily output of fly ash, daily output of desulfurization wastewater and daily output of fly ash (respectively using M) by monitoring system of coal-fired power plant1、M2、M3、M4Represents); in this step, M is obtained1=7000 t/d，M2=1200 t/d，M3=260 t/d，M4=1195 t/d；
c) Measuring the ash content (A) in the fire coal; in the step, the ash content in the fire coal sample is detected by using the national standard GB/T212-plus 2008 & ltIndustrial analysis method for coal & gt, and A =18.38% is obtained;
d) calculating the ratio K of Cl content in fly ash to Cl content in fire coal1=(C2×M2)/(C1×M1) And the ratio K of the Cl content in the desulfurization wastewater to the Cl content in the fire coal2=(C3×M3)/(C1×M1) (ii) a In this step, K is obtained1=0.094，K2=0.758；
e) Most of ash generated after coal combustion is converted into fly ash, so the daily yield coefficient K of the fly ash3=M4/(A×M1) (ii) a In this step, K is obtained3=0.929；
f) Chlorine content (C) in fly ash4) The method is contributed by fly ash and desulfurization wastewater, and the daily yield of fly ash is contributed by ash, so the formula for measuring and calculating the chlorine content of fly ash is as follows:
C4=(C2×M2+C3×M3)/M4=(K1+K2)×(C1×M1)/K3×(A×M1)=[(K1+K2)×C1]/(K3×A)；
in this step, a measurement model is obtained: the chlorine content (%) =0.061 of the fly ash.
In the steps, the Cl in the fire coal is supposed to be completely released under the combustion condition of the boiler and enter a subsequent flue gas treatment system; because the content and the dosage of chlorine in the limestone of the desulfurization absorbent and the desulfurization process water are low, the influence on the Cl balance of the system is small, and the source of Cl ions in the coal-fired flue gas system ignores the limestone and the process water; assuming that all Cl in the desulfurization wastewater enters the fly ash, and neglecting the mass of the fly ash; the fly ash is assumed to be totally derived from the ash content of the coal, and the dust removal efficiency of the dust removal equipment is 100%.
In order to verify the application effect of the method, a certain coal-fired power plant is randomly selected to be sampled and detected in the normal operation period, according to the implementation steps of the method, a measured value of the chlorine content of the fly ash is obtained, meanwhile, the fly ash is sampled and detected to obtain an actual measured value of the chlorine content of the fly ash, and the measured value and the actual measured value are compared. The result shows that the measured value of 0.064 percent is close to the measured value of 0.061 percent of the invention, and the feasibility of measuring the Cl content in the fly ash by detecting the Cl content in the fire coal and the ash content is shown.
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents, improvements and the like that fall within the spirit and principle of the present invention are intended to be included therein.
Claims (1)
1. A method for measuring and calculating the content of chlorine in fly ash in a desulfurization wastewater zero-discharge system is characterized by comprising the following steps:
the method specifically comprises the following steps:
the method comprises the following steps: and (3) determining the Cl content: measuring Cl content in fire coal, fly ash and desulfurization wastewater under the same working condition, and respectively using C1、C2、C3Expressed in units of. mu.g/g,. mu.g/g and mg/L, respectively;
step two: determining the daily consumption of the coal, the daily output of the fly ash, the daily output of the desulfurization wastewater and the daily output of the fly ash: collecting daily consumption of coal, daily output of fly ash, daily output of desulfurization wastewater and daily output of fly ash by using a monitoring system of a coal-fired power plant, and respectively using M1、M2、M3、M4The expression is that the units are t/d;
step three: determining the ash content in the fire coal: the ash content percentage in the fire coal is represented by A;
step four: calculating the Cl ratio of each component: calculating the ratio K of Cl content in fly ash to Cl content in fire coal1=(C2×M2)/(C1×M1) And the ratio K of the Cl content in the desulfurization wastewater to the Cl content in the fire coal2=(C3×M3)/(C1×M1)；
Step five: calculating the daily yield coefficient of the fly ash: most of ash generated after coal combustion is converted into fly ash, so the daily yield coefficient K of the fly ash3=M4/(A×M1)；
Step six: establishing a fly ash content calculation model of a flue gas treatment system: the chlorine content percentage C4 in the fly ash can be calculated from the chlorine content in the fly ash and the desulfurization wastewater, and the daily yield of the fly ash can be calculated from the yield of the ash, so that the estimation formula of the chlorine content in the fly ash is as follows:
C4=(C2×M2+C3×M3)/M4=(K1+K2)×(C1×M1)/K3×(A×M1)=[(K1+K2)×C1]/(K3×A)；
the chlorine content of the fly ash can be calculated only by detecting the Cl content and the ash content of the fire coal.
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010196178.3A CN111477286A (en) | 2020-03-19 | 2020-03-19 | Method for measuring and calculating content of chlorine in fly ash in desulfurization wastewater zero-discharge system |
| CN202011483205.1A CN112309507B (en) | 2020-03-19 | 2020-12-16 | Method for measuring and calculating content of fly ash chlorine in desulfurization wastewater zero-emission system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010196178.3A CN111477286A (en) | 2020-03-19 | 2020-03-19 | Method for measuring and calculating content of chlorine in fly ash in desulfurization wastewater zero-discharge system |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN111477286A true CN111477286A (en) | 2020-07-31 |
Family
ID=71747748
Family Applications (2)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202010196178.3A Withdrawn CN111477286A (en) | 2020-03-19 | 2020-03-19 | Method for measuring and calculating content of chlorine in fly ash in desulfurization wastewater zero-discharge system |
| CN202011483205.1A Active CN112309507B (en) | 2020-03-19 | 2020-12-16 | Method for measuring and calculating content of fly ash chlorine in desulfurization wastewater zero-emission system |
Family Applications After (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202011483205.1A Active CN112309507B (en) | 2020-03-19 | 2020-12-16 | Method for measuring and calculating content of fly ash chlorine in desulfurization wastewater zero-emission system |
Country Status (1)
| Country | Link |
|---|---|
| CN (2) | CN111477286A (en) |
Family Cites Families (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH08109017A (en) * | 1994-10-11 | 1996-04-30 | Tanaka Sekkai Kogyo Kk | Slaked lime and its production |
| KR100330255B1 (en) * | 2000-02-26 | 2002-03-25 | 서현숙 | Composition of inorganic coagulant for water treatment |
| CN102500208A (en) * | 2011-11-18 | 2012-06-20 | 山东大学 | Utilization method and device for wet flue gas desulfurization wastewater |
| CN106650068B (en) * | 2016-12-12 | 2019-12-10 | 华南理工大学 | calculation method for predicting carbon emission of coal-fired power plant |
| CN109400084B (en) * | 2018-12-07 | 2021-09-28 | 西南科技大学 | High-solid waste alkali-activated titanium slag extraction stabilized soil and preparation method thereof |
| CN110420548B (en) * | 2019-09-03 | 2024-03-26 | 亚太环保股份有限公司 | Device and method for ultralow emission of flue gas through ammonia method in cooperation with denitration, desulfurization and demercuration |
-
2020
- 2020-03-19 CN CN202010196178.3A patent/CN111477286A/en not_active Withdrawn
- 2020-12-16 CN CN202011483205.1A patent/CN112309507B/en active Active
Also Published As
| Publication number | Publication date |
|---|---|
| CN112309507B (en) | 2024-07-05 |
| CN112309507A (en) | 2021-02-02 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Yao et al. | Effect of wet flue gas desulfurization (WFGD) on fine particle (PM2. 5) emission from coal-fired boilers | |
| Wang et al. | Characteristics of condensable particulate matter before and after wet flue gas desulfurization and wet electrostatic precipitator from ultra-low emission coal-fired power plants in China | |
| Zhang et al. | Emission characteristics of heavy metals from a typical copper smelting plant | |
| CN101839900B (en) | Detection method of mercury content in burning coal | |
| Wu et al. | Coordinated effects of air pollution control devices on PAH emissions in coal-fired power plants and industrial boilers | |
| CN105354358B (en) | Wet electrical dust precipitator performance on-site verification method and system | |
| Pan et al. | Formation and removal characteristics of sulfuric acid mist in a wet flue gas desulfurization system | |
| CN109342284A (en) | A kind of detection system and detection method for harmful substances from flue gases | |
| CN108800433A (en) | New blower fan screen net life detecting method | |
| CN208860147U (en) | Use the energy-saving control system field instrument of the heating furnace of mixed gas | |
| Wang et al. | The state of the art of condensable particulate matter | |
| Shin et al. | Continuous measurement of PM10 and PM2. 5 concentration in coal-fired power plant stacks using a newly developed diluter and optical particle counter | |
| CN103977763B (en) | A kind of preparation method of the high-efficiency adsorbent for gaseous mercury sampling | |
| CN115171798A (en) | Method for predicting low-temperature desulfurization and/or denitration performance of activated carbon based on Na content in coal | |
| CN111564184A (en) | Limestone-gypsum wet desulphurization SO of coal-fired power plant3Collaborative removal efficiency prediction method | |
| CN110849679A (en) | Synchronous sampling device for condensable particles and sulfur trioxide in coal-fired flue gas and working method thereof | |
| CN112309507B (en) | Method for measuring and calculating content of fly ash chlorine in desulfurization wastewater zero-emission system | |
| WO2023061248A1 (en) | Form-based test method and apparatus for mercury in flue gas from stationary pollution source in whole process | |
| Bing et al. | Effect of wet flue gas desulfurization facilities of coal-fired power plants on mercury emission | |
| Noda et al. | Mercury partitioning in coal-fired power plants in Japan | |
| CN111467934B (en) | Wet electrostatic dust collector SO of coal-fired power plant3Collaborative removal efficiency prediction method | |
| CN212134237U (en) | Synchronous sampling device of condensable particles and sulfur trioxide in coal-fired flue gas | |
| CN112834705B (en) | Pulverized coal fired boiler furnace and gas online monitoring and early warning system thereof | |
| CN101865905A (en) | Mercury concentration on-line detection method in smoke gas | |
| CN109181646B (en) | Dust suppressant for coal-fired power plant for promoting fine particle agglomeration |
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 | ||
| WW01 | Invention patent application withdrawn after publication | ||
| WW01 | Invention patent application withdrawn after publication |
Application publication date: 20200731 |