Background technology
China is the energy resource consumption big country based on coal, simultaneously Ye Shi iron and steel big producing country.The end of the year 2006, China's coal fired power generation installed capacity reaches 4.84 hundred million kilowatts, coal-fired 1,200,000,000 tons, smoke discharge amount about 3,000,000 tons, and wherein the ultra tiny dust of nearly 2,700,000 tons of PM10 is in atmosphere floating for a long time, particularly PM2.5 is present in air with aerosol form, has a strong impact on atmospheric visibility and air quality.Steel industry dust discharge amount accounts for 25% of China's industrial dust discharged total amount, and sinter that industrial soot emissions account for steel manufacture process total release 40% more than.
Owing to recognizing the harm of flue dust, China has made more strict discharge standard, start on July 1st, 2014 " fossil-fuel power plant atmospheric pollutant emission standard (the GB 13223-2011) " that perform, define existing thermal power generation coal-burning boiler chimney breast soot emissions limit value, the whole nation is 30mg/m
3, the special emission limit in key area is 20mg/m
3; " steel sintering, pelletizing industrial air pollution thing discharge standard (GB 28662-2012) " specifies existing sintering machine ball, and the granular material discharged limit value of group's roasting apparatus is 50mg/m
3, rear of sintering machine emission limit is 30mg/m
3.
For the flue gas that coal-burning boiler and sintering machine are got rid of, usually need just can enter air after the process such as dedusting, desulfurization.In a kind of coal-burning boiler of extensive use or the smoke processing system of sintering machine, flue gas is first through cleaner, and mainly sack cleaner or electrostatic precipitator complete dedusting; Then enter desulphurization plant and carry out desulfurization process.
Sack cleaner utilizes solid or liquid particle in porous filter medium separation and collection gas, and its dust removal process is the dust bonding layer formed after relying on filter medium to run a period of time is main filtration layer, and filter material layer own plays the skeleton function of dust bonding layer.Its principle comprises: sieving, inertial collision, interception, diffusion, electrostatic and gravitational settling.Sack cleaner good dedusting effect, no matter but how high its efficiency is, and the particle major part of discharge is all less than 2.5 μm.
Electrostatic precipitator operation principle utilizes high voltage electric field to make particle charged, under the effect of Coulomb force, make particle and flow separation sedimentation.Electrostatic precipitation drag losses is little, permission operating temperature is high, and process air range amount is large, but has certain selective to dust, to the particle being greater than 10 μm, ESP Efficiency is very high, but when particle diameter is less than 2 μm, efficiency of dust collection will significantly decline, efficiency of dust collection can lower than 90%, in extreme circumstances, efficiency even can drop to less than 50%, from electric cleaner emit quantity maximum be exactly the subparticle of 0.2 ~ 2 μm.
Due to the high-effective dust-removing equipment of routine, as sack cleaner or electrostatic precipitator can not effectively trap for the minuteness particle of particle diameter lower than 2.5 μm, in the flue gas therefore after bag-type dusting or electrostatic precipitation, the content of particle is still at 100 ~ 200mg/m
3, do not meet discharge standard.
Can not one of the new technology of qualified discharge be at present wet static dedusting for making up the two, its operation principle is: metal discharge line is under high direct voltage effect, ambient gas is ionized, dust is charged in power plant, move to dust collecting electrode under electric field force effect, when reaching dust collecting electrode surface, flow down with liquid film and be removed.Wet electrical dust precipitator is to acid mist, and toxic heavy metal and PM10, especially the fine dust of PM2.5 has good removal effect.Therefore, when being applied to coal-burning power plant, sintering machine, wet electrical dust precipitator removes SO for after wet desulphurization
3, water droplet and flue dust effect clearly.
But, after wet cottrell must be placed in desulphurization plant, namely the flue gas that coal-burning boiler or sintering machine are got rid of needs first to carry out desulfurization through desulphurization plant, then just can enter wet cottrell and carry out dedusting, thus can increase the running resistance of desulphurization plant.Further, it adopts closing circulation irrigating water, need constantly fill into former water, discharges waste water, increases desulphurization system water balance difficulty.In addition, the technical costs of wet electrical dust precipitator single product is high, equipment investment expense is higher than common electrostatic duster, and in running except the power consumption of deduster own, auxiliary water circulating pump etc. also can consume part electricity, in flushing water, additive also increases a part of operating cost, and therefore it drops into and operating cost all too costliness.
CN104014210A discloses a kind of method adopting liquid membrane emulsion technology to remove dust in flue gas, but emulsion liquid film complicated process of preparation, and be not suitable for using with other slurry combination, range of application is narrower.
CN104355386A discloses a kind of composite flocculation agent be made up of polyacrylamide and polyacrylamide sodium, but it effectively can not remove the fine particulates of particle diameter below 2.5 μm.
CN103721550A discloses a kind of flue gas and desulfurizing and denitrifying and takes off VOCs absorbent, comprises ammonium salt (ammonium chloride, ammonium carbonate, triethanolamine and urea) 5 ~ 10%, surfactant (castor oil sodium sulfonate, aliphatic alcohol polyethenoxy polypropylene ether, Tween-20 and Si Ban-20) 0.01 ~ 0.50%, complexing agent (ethylenediamine tetra-acetic acid ferrous complex, aminotriacetic acid ferrous complex and six cobaltammines) 1 ‰ ~ 2% and excess water.SO in high-efficient purification flue gas while that this absorbent can be implemented in a set of equipment
2, NO
xwith VOCs etc., but dust removing effects still awaits improving.
Summary of the invention
The first object of the present invention is to provide a kind of dedusting composition, and this dedusting composition is used for the particle removed in flue gas, dust removing effects is excellent.If be blended in the desulfurization slurry of wet desulphurization equipment by preferred for the present invention dedusting composition, while wet type desulfurizing operation, effectively can remove particle diameter lower than 10 μm, the particularly fine particulates of 2.5 μm, realizes flue dust qualified discharge.
The second object of the present invention is to provide a kind of desulfurization compositions, and said composition has desulfurization and dustproof function simultaneously.
The third object of the present invention is the purposes providing a kind of dedusting composition, uses this dedusting composition in fume treatment process, without the need to using wet cottrell, can realize flue dust qualified discharge simultaneously.
The invention provides a kind of dedusting composition, comprise following component:
Sulfonate surfactant;
Carboxylate surfactant;
Sulfuric ester salt form surfactant;
Non-ionic antistatic agent; With
PAMA.
According to dedusting composition of the present invention, preferably, in 100 weight portion dedusting compositions, the component of following weight portion is comprised:
Sulfonate surfactant 30 ~ 70 weight portion;
Carboxylate surfactant 3 ~ 25 weight portion;
Sulfuric ester salt form surfactant 3 ~ 20 weight portion;
Non-ionic antistatic agent 3 ~ 18 weight portion;
PAMA 10 ~ 30 weight portion.
According to dedusting composition of the present invention, preferably, described sulfonate surfactant be selected from following material one or more: alkylsulfonate, alkylbenzenesulfonate, alkylnaphthalene sulfonate, alpha-alkene sulfonate, alpha-sulfo monocarboxylate, the sulfoalkyl ester of aliphatic acid, sulphosuccinates, lignosulfonates, alkyl glyceryl ether sulfonate, alkyl diphenyl ether disulfonate.
According to dedusting composition of the present invention, preferably, described carboxylate surfactant comprises amino acid type surfactant or soap.
According to dedusting composition of the present invention; preferably, described amino acid type surfactant be selected from following material one or more: fatty acyl group NaAsp, fatty acyl group-N-beta-hydroxyethyl-Sodium Glycinate, N-fatty acyl group sodium sarcosinate, N-fatty acyl group polypeptide.
According to dedusting composition of the present invention, preferably, described sulfuric ester salt form surfactant be selected from following material one or more: saturated fatty alcohol sulfuric acid, unsaturated fatty alcohol sulfuric ester, secondary alkyl sulphate salt.
According to dedusting composition of the present invention, preferably, described non-ionic antistatic agent is selected from ethylene oxide adduct, the ethylene oxide adduct of fatty alcohol, the ethylene oxide adduct of alkyl phenol, ethoxylated fatty amine, ethoxylated fatty amides, the monoethanolamine-glycidol ether of aliphatic acid.
According to dedusting composition of the present invention, preferably, described ethoxylated fatty amine is selected from ethoxylated fat kiber alkyl amine, ethoxylated fat alkyl secondary amine, ethoxylation N-fatty alkyl-1,3-trimethylene diamines.
The present invention also provides a kind of desulfurization compositions, and described desulfurization compositions comprises following component:
Desulfurization slurry; With
Dedusting composition as above;
Wherein, this dedusting composition accounts for the 0.01wt% ~ 0.1wt% of desulfurization slurry.
The present invention also provides the purposes of above-mentioned dedusting composition, and it is for removing the particle entered in the flue gas of wet desulphurization equipment
Dedusting composition of the present invention is used for the particle removed in flue gas, its dust removing effects is good.According to the preferred technical scheme of the present invention, dedusting composition of the present invention is added in the desulfurization slurry of desulphurization plant, sack cleaner or the inexpungible particle diameter of the electrostatic precipitator particle that is less than 10 μm in early stage effectively can be removed while desulfurization process is carried out to flue gas, the particularly particle diameter fine particulates that is less than 2.5 μm, thus realize flue dust qualified discharge, therefore the present invention can substitute wet cottrell, save owing to adopting the equipment investment needed for this equipment, supporting flushing water system, saved water power energy consumption.And dedusting composition of the present invention is cheap, easy to use.
Detailed description of the invention
Below the specific embodiment of the present invention is described in further details, but therefore protection scope of the present invention is not subject to any restriction.
Dedusting composition of the present invention, comprises following component: sulfonate surfactant; Carboxylate surfactant; Sulfuric ester salt form surfactant; Non-ionic antistatic agent; And PAMA.
As preferably, dedusting composition of the present invention is composed of the following components: sulfonate surfactant; Carboxylate surfactant; Sulfuric ester salt form surfactant; Non-ionic antistatic agent; And PAMA.
According to dedusting composition of the present invention, in 100 weight portion dedusting compositions, preferably, the component of following weight portion can be comprised: sulfonate surfactant 30 ~ 70 weight portion; Carboxylate surfactant 3 ~ 25 weight portion; Sulfuric ester salt form surfactant 3 ~ 20 weight portion; Non-ionic antistatic agent 3 ~ 18 weight portion; PAMA 10 ~ 30 weight portion.In dedusting composition of the present invention, sulfonate surfactant consumption is preferably 35 ~ 65 weight portions, is more preferably 40 ~ 60 weight portions.In dedusting composition of the present invention, carboxylate surfactant's consumption is preferably 5 ~ 23 weight portions, is more preferably 6 ~ 20 weight portions.In dedusting composition of the present invention, sulfuric ester salt form dosage of surfactant is preferably 3.1 ~ 18 weight portions, is more preferably 3.3 ~ 15 weight portions.In dedusting composition of the present invention, non-ionic antistatic agent consumption is preferably 5 ~ 16 weight portions, is more preferably 8 ~ 15 weight portions.In dedusting composition of the present invention, PAMA consumption is preferably 12 ~ 28 weight portions, is more preferably 13 ~ 25 weight portions.
At dedusting composition of the present invention, preferably, described sulfonate surfactant be selected from following material one or more: alkylsulfonate, alkylbenzenesulfonate, alkylnaphthalene sulfonate, alpha-alkene sulfonate, alpha-sulfo monocarboxylate, the sulfoalkyl ester of aliphatic acid, sulphosuccinates, lignosulfonates, alkyl glyceryl ether sulfonate, alkyl diphenyl ether disulfonate." alkyl " in above-mentioned surfactant is known in the art those.Such as, the carbon number of " alkyl " in above-mentioned substance can be C
9~ C
25, be preferably C
12~ C
20, be more preferably C
13~ C
17.More preferably, sulfonate surfactant of the present invention is selected from one or more in following material: alkylsulfonate, alkylbenzenesulfonate, alkylnaphthalene sulfonate, sulphosuccinates.More preferably, sulfonate surfactant of the present invention is selected from alkylsulfonate and/or alkylbenzenesulfonate.The example of alkylsulfonate includes but not limited to dodecyl sodium sulfate, myristyl sodium sulfonate, sodium cetanesulfonate, sodium stearyl sulfonate.The example of alkylbenzenesulfonate includes but not limited to neopelex, myristyl benzene sulfonic acid sodium salt, cetyl benzenesulfonic acid sodium, octadecyl benzenesulfonic acid sodium.Sulfonate surfactant of the present invention is preferably neopelex or sodium cetanesulfonate.
At dedusting composition of the present invention, preferably, described carboxylate surfactant comprises amino acid type surfactant or soap.Soap of the present invention comprises fatty acid metal salts or fatty acid ammonium salt.The aliphatic chain of aliphatic acid is known in the art those.Such as, the carbon number of " aliphatic chain " in above-mentioned aliphatic acid can be C
9~ C
25, be preferably C
12~ C
20, be more preferably C
13~ C
17.Soap example of the present invention includes but not limited to sodium laurate, tetradecanoic acid sodium, hexadecanoic acid sodium, odium stearate.
Amino acid type surfactant of the present invention can be selected from following material one or more: fatty acyl group NaAsp, fatty acyl group-N-beta-hydroxyethyl-Sodium Glycinate, N-fatty acyl group sodium sarcosinate, N-fatty acyl group polypeptide." fatty acyl group " of above-mentioned amino acid type surfactant is known in the art those, comprises saturated fat acyl group (such as alkanoyl), unsaturated fatty acyl group (such as enoyl-).Such as, the carbon number of " fatty acyl group " of above-mentioned amino acid type surfactant can be C
10~ C
26, be preferably C
13~ C
21, be more preferably C
14~ C
19.Preferably, amino acid type surfactant of the present invention can be selected from alkanoyl NaAsp, N-fatty acyl group polypeptide, is more preferably N-fatty acyl group polypeptide.The example of N-fatty acyl group sodium sarcosinate comprises Mei Dilan (Medialan); N-fatty acyl group polypeptide comprises Lei meter Bang (Lamepon).The structural formula of N-fatty acyl group polypeptide is RCONHR ' (CONHR ')
xcOOM, in formula, R represents C
9~ C
25fat-based, is preferably C
12~ C
20fat-based, is more preferably C
13~ C
17fat-based; R ' such as, for determining the substituting group of amino kind, H, methyl etc.; M is metal ion, such as Na.The example of N-fatty acyl group polypeptide comprises Lamepon A, is also called oleoyl amino acid sodium or oleoyl many contractings amino acid sodium.
According to dedusting composition of the present invention, preferably, described sulfuric ester salt form surfactant be selected from following material one or more: saturated fatty alcohol sulfuric acid, unsaturated fatty alcohol sulfuric ester, secondary alkyl sulphate salt.Saturated fatty alcohol contains saturated aliphatic chain (such as alkyl), and unsaturated fatty alcohol is the aliphatic chain (such as thiazolinyl) containing unsaturated groups such as double bonds.The secondary alkyl of the aliphatic chain of above-mentioned saturated fatty alcohol sulfuric acid, the aliphatic chain of unsaturated fatty alcohol sulfuric ester and secondary alkyl sulphate salt is known in the art those, and such as, the carbon number of above-mentioned " aliphatic chain " and " secondary alkyl " can be C
9~ C
25, be preferably C
12~ C
20, be more preferably C
13~ C
17.The example of saturated fatty alcohol sulfuric acid of the present invention includes but not limited to laruyl alcohol sodium sulfovinate, tetradecanol sodium sulphate, sodium cetyl alcohol sulfate, stearyl alcohol sodium sulfovinate.The example of unsaturated fatty alcohol sulfuric acid of the present invention includes but not limited to lanolin alcohol sodium sulfovinate, tetradecene alcohol sodium sulphate, hexadecenol sodium sulphate, oleyl sulfate sodium.Secondary alkyl sulphate salt of the present invention is alpha-olefin sulfating product, such as terraced ripple (Teepol).Preferably, sulfuric ester salt form surfactant of the present invention is selected from saturated fatty alcohol sulfuric acid, unsaturated fatty alcohol sulfuric ester; Be more preferably saturated fatty alcohol sulfuric acid.
The anion surfactant synergies such as sulfonate surfactant of the present invention, carboxylate surfactant, sulfuric ester salt form surfactant, by the solids that absorption suspends, make build bridge between particle or make particle coacervation form large flocculate by charging neutrality, accelerate the sedimentation of particle in suspension, thus adsorb the fine particulates such as PM10, PM2.5 in desulphurization plant.The organic matters such as the polycyclic aromatic hydrocarbon , bioxin that above-mentioned anion surfactant can also be carried secretly in adsorption particle thing simultaneously.
At dedusting composition of the present invention, preferably, described non-ionic antistatic agent is selected from ethylene oxide adduct, the ethylene oxide adduct of fatty alcohol, the ethylene oxide adduct of alkyl phenol, ethoxylated fatty amine, ethoxylated fatty amides, the monoethanolamine-glycidol ether of aliphatic acid.Wherein, the carbon number of the aliphatic chain in aliphatic acid, fatty alcohol, fatty amine, fatty acid amide can be C
9~ C
25, be preferably C
12~ C
20, be more preferably C
13~ C
17; The carbon number of the alkyl chain of alkyl phenol can be C
9~ C
25, be preferably C
12~ C
20, be more preferably C
13~ C
17.The quantity of the oxygen ethylene repeating unit of above-mentioned ethylene oxide adduct or ethoxylate can be 1 ~ 8, is preferably 2 ~ 6, is more preferably 3 ~ 5.According to dedusting composition of the present invention, preferably, described non-ionic antistatic agent is selected from ethylene oxide adduct (fatty acid ester polyethylene glycol oxide ether), the ethylene oxide adduct (poly alkyl alcohol ethylene oxide ether) of fatty alcohol, the ethylene oxide adduct (alkyl phenol polyethylene glycol oxide ether) of alkyl phenol, ethoxylated fatty amine (fatty amine polyethylene glycol oxide ether), the ethoxylated fatty amides (fatty acid amide polyethylene glycol oxide ether) of aliphatic acid; Be more preferably ethoxylated fatty amine.The quantity of the oxygen ethylene repeating unit of above-mentioned ethoxylated fatty amine can be 1 ~ 5, is preferably 1 ~ 3.According to dedusting composition of the present invention, preferably, described ethoxylated fatty amine is selected from ethoxylated fat kiber alkyl amine, ethoxylated fat alkyl secondary amine, ethoxylation N-fatty alkyl-1,3-trimethylene diamines.The carbon number of above-mentioned fatty alkyl can be C
9~ C
25, be preferably C
12~ C
20, be more preferably C
13~ C
17.The example of ethoxylated fatty amine of the present invention includes but not limited to polyoxyethylene dodecyl amine, polyoxyethylene tetradecylamine, polyoxyethylene cetyl base amine, polyoxyethylene octadecyl amine, polyoxyethylene tallow base amine, polyethylene glycol hydrogenated tallow base amine, polyoxyethylene cocoalkyl amines, polyoxyethylene oil base amine, polyoxyethylene soya oil base amine, polyoxyethylene N-tallow base-1,3-trimethylene diamines.Polyethylene glycol hydrogenated tallow base amine of the present invention includes but not limited to polyoxyethylene (2) hydrogenated-tallow group amine, polyoxyethylene (5) hydrogenated-tallow group amine, polyoxyethylene (10) hydrogenated-tallow group amine, polyoxyethylene (15) hydrogenated-tallow group amine, polyoxyethylene (50) hydrogenated-tallow group amine.
In dedusting composition of the present invention, add non-ionic antistatic agent, in and flue gas in finely ground particles institute electrically charged, be conducive to the further gathering of particle, increase, thus effectively remove these finely ground particles.
At dedusting composition of the present invention, preferably, described PAMA can be the copolymer of PAA and acrylamide, and manufacturing enterprise comprises Daqing oil field chemical assistant factory, chemical experimental factory of University Of Tianjin.The example of described PAMA is as APAA8701.Dedusting composition of the present invention adds PAMA can improve slurries toughness, improves dust removing effects.
At dedusting composition of the present invention, can also comprise other anionic surfactant, other anionic surfactant include but not limited to alkyl phosphate monoester salt, alkyl phosphoric acid dibasic acid esters salt etc.
Above-mentioned each component mixes by conventional method and obtains by dedusting composition of the present invention, repeats no more here.
The present invention also provides a kind of desulfurization compositions, and described desulfurization compositions comprises desulfurization slurry and dedusting composition as above.Wherein, this dedusting composition accounts for the 0.01wt% ~ 0.1wt% of desulfurization slurry, is preferably 0.011wt% ~ 0.03wt%, is more preferably 0.012wt% ~ 0.019wt%.Now, the dust removing effects of this dedusting composition is outstanding.Desulfurization slurry of the present invention is preferably magnesium hydroxide slurry, also can be the desulfurization slurry of other types, repeat no more here.
The present invention also provides the purposes of above-mentioned dedusting composition, and it is for removing the particle entered in the flue gas of wet desulphurization equipment.Removing further of fine solid particle (particle diameter lower than 10 μm, the particularly particle diameter fine particulates that is less than 2.5 μm) is remained after dedusting composition of the present invention is particularly useful for bag-type dusting or electrostatic precipitation.Described dedusting composition of the present invention is (i.e. dedusting liquid) use in fluid form preferably, uses step as follows:
Dedusting composition preparation process: mix three kinds of anionic surfactant, antistatic additive and PAMAs, preparation dedusting composition;
Dedusting composition storing step: this dedusting composition is stored in special dedusting composition storage tank or is stored in wet desulphurization circulating water pool (groove);
Dedusting delivery of composition step: this dedusting composition is sent in desulfurizing tower with special dedusting delivery of composition pump or water circulating pump;
Dedusting composition and desulfurization slurry blend step: dedusting composition to be delivered in desulfurizing tower with desulfurization slurry through being uniformly mixed;
Dust removal step: run wet desulphurization equipment, remove the flue dust of boiler of power plant, sintering machine or pelletizing equipment exiting flue gas.
In the present invention, the top in described desulphurization plant is provided with and absorbs spray district, sprays out the desulfurization slurry containing dedusting composition, thus the sulfur dioxide absorbed in flue gas and fine particulates.In order to reach good dust removing effects, preferably, smoke content in the flue gas in described desulphurization plant is entered at 35 ~ 500mg/Nm
3, be preferably 50 ~ 400mg/Nm
3, be preferably 100 ~ 350mg/Nm
3.
In order to make smoke content in above-mentioned scope, flue gas can first through cleaner before entering desulphurization plant, such as sack cleaner or electrostatic precipitator, thus removes the larger particle of most particle diameter, the particle of such as more than PM10.
In the present invention, described flue gas is that coal-burning boiler, sintering machine and pelletizing equipment produce, and the flue gas after cleaner such as sack cleaner or electrostatic precipitator dedusting.Described dedusting composition of the present invention, by sending in desulphurization plant with delivery pump or water circulating pump, is uniformly mixed with desulfurization slurry.
At dedusting composition of the present invention and slurries blend step, the temperature of desulfurization compositions is remained on 35 ~ 65 DEG C, be preferably 40 ~ 55 DEG C.
The concrete operations of dedusting composition of the present invention are adopted to be: first flue gas through sack cleaner or the larger particle of electrostatic precipitator removing particle diameter, such as, is greater than the particle of 10 μm; Flue gas after dust removal process enters desulphurization plant, adopts desulfurization slurry to carry out desulfurization process, due in desulfurization slurry also containing dedusting composition component, thus effectively can remove particle diameter and be less than 10 μm, particularly the particle diameter fine particulates that is less than 2.5 μm.By the flue gas after the method for the invention process, flue dust qualified discharge can be realized.The exiting flue gas soot emissions content of the desulphurization plants such as coal-burning boiler, sintering machine and pelletizing equipment all can be reduced to 30mg/Nm
3, reach dust emission standard.
embodiment 1
The dedusting composite formula that the present embodiment adopts is as shown in table 1.
Table 1 dedusting composite formula
Sequence number |
Title |
Consumption (kg) |
1 |
Sodium n-alkylbenzenesulfonate (neopelex) |
20 |
2 |
Lamepon A (Wuhan milky way Chemical Co., Ltd.) |
5 |
3 |
Tetradecanol sodium sulphate |
2 |
4 |
Polyoxyethylene dodecyl amine |
5 |
5 |
PAMA |
8 |
Dedusting composition is applied in 1,500,000 tons of pelletizing desulfuring and denitrifying dedust apparatus by the present embodiment.This project operation parameter is as shown in table 2.
Table 2 1,500,000 tons of pelletizing desulfuring and denitrifying dedust apparatus operational factor tables
Sequence number |
Parameter |
Unit |
Numerical value |
1 |
Exhaust gas volumn (operating mode) |
m
3/h
|
780000 |
2 |
Entrance sulfur dioxide concentration |
mg/Nm
3 |
1600 |
3 |
Outlet sulfur dioxide concentration |
mg/Nm
3 |
60 |
4 |
Inlet nitrogen oxides concentration |
mg/Nm
3 |
650 |
5 |
Outlet nitrous oxides concentration |
mg/Nm
3 |
65 |
6 |
Inlet dust |
mg/Nm
3 |
115 |
7 |
Outlet dust |
mg/Nm
3 |
12 |
8 |
Flue-gas temperature |
℃ |
110-160 |
9 |
Operating cost |
Yuan/ton pellet |
4.4 |
Containing 250m
3drop into this dedusting composition 40kg in the desulfurizing tower of magnesium hydroxide slurries liquid measure, before dropping into, inlet flue gas dust content is 115mg/Nm
3, drop into this dedusting composition after 8 minutes, exiting flue gas dust content is down to 12mg/Nm
3, and stablize maintenance 10 hours, average dust removal efficiency up to 89.6%, higher than design load, lower than emission limit.The technical indicators such as this project desulfur denitrate dust collecting efficiency are as shown in table 3.
Table 3 1,500,000 tons of pelletizing desulfuring and denitrifying dedust apparatus running technology indexs
Sequence number |
Project |
Unit |
Mean value |
Design load |
1 |
Desulfuration efficiency |
% |
98.2 |
97.3 |
2 |
Denitration efficiency |
% |
75.6 |
60 |
3 |
Efficiency of dust collection |
% |
89.6 |
80 |
4 |
Power consumption |
kW˙h |
420 |
≤620 |
5 |
Water consumption |
t/h |
26 |
30 |
6 |
Desulphurization denitration intermixture |
t/h |
0.95 |
1.2 |
7 |
SR |
Pa |
600 |
≤800 |
Conclusion: dedusting composition and desulfurization slurry weight ratio are 0.016wt%, under this addition, this dedusting composition dust removing effects is remarkable, and stable, exhaust gas dust content is lower than discharge standard.
embodiment 2
The dedusting composite formula that the present embodiment adopts is as shown in table 4.
Table 4 dedusting composite formula
Sequence number |
Title |
Consumption (kg) |
1 |
Neopelex |
90 |
2 |
Lamepon A (Wuhan milky way Chemical Co., Ltd.) |
20 |
3 |
Tetradecanol sodium sulphate |
8 |
4 |
Polyoxyethylene octadecyl amine |
12 |
5 |
PAMA |
20 |
This dedusting composition is applied in 3 × 380t/h boiler desulfurization denitration dust collecting project, and its project operation parameter is as shown in table 5.
Table 53 × 380t/h boiler desulfurization denitration dust collecting operational factor table
Sequence number |
Parameter |
Unit |
Numerical value |
1 |
Exhaust gas volumn (operating mode) |
m
3/h
|
1780000 |
2 |
Entrance sulfur dioxide concentration |
mg/Nm
3 |
2600 |
3 |
Outlet sulfur dioxide concentration |
mg/Nm
3 |
60 |
4 |
Inlet nitrogen oxides concentration |
mg/Nm
3 |
450 |
5 |
Outlet nitrous oxides concentration |
mg/Nm
3 |
70 |
6 |
Inlet dust |
mg/Nm
3 |
175 |
7 |
Outlet dust |
mg/Nm
3 |
12.6 |
8 |
Flue-gas temperature |
℃ |
110-160 |
9 |
Operating cost |
Yuan/ton pellet |
4.2 |
Be 800m in magnesium hydroxide slurries liquid measure
3absorption tower in add this dedusting composition 150kg, before dropping into, inlet flue gas dust content is 175mg/Nm
3, drop into this dedusting composition after 12 minutes, exiting flue gas dust content is down to 12.6mg/Nm
3, and stablize maintenance 12 hours, efficiency of dust collection is up to 92.8%, and higher than design load, exhaust gas dust content is lower than discharge standard.The technical indicators such as this project desulfur denitrate dust collecting efficiency are as shown in table 6.
Table 63 × 380t/h boiler desulfurization denitrifying dedust apparatus running technology index
Sequence number |
Project |
Unit |
Mean value |
Design load |
1 |
Desulfuration efficiency |
% |
98.9 |
97.3 |
2 |
Denitration efficiency |
% |
80.2 |
70 |
3 |
Efficiency of dust collection |
% |
92.8 |
90 |
4 |
Power consumption |
kW˙h |
3280 |
≤3500 |
5 |
Water consumption |
t/h |
68 |
85 |
6 |
Desulphurization denitration intermixture |
t/h |
5.87 |
6.9 |
7 |
SR |
Pa |
850 |
≤1000 |
Conclusion: dedusting composition and desulfurization slurry weight ratio are 0.019wt%, under this dedusting composition addition, this dedusting composition dust removing effects is stablized, and exhaust gas dust content is lower than discharge standard.
embodiment 3
The dedusting composite formula that the present embodiment adopts is as shown in table 7.
Table 7 dedusting composite formula
Sequence number |
Title |
Consumption (kg) |
1 |
Neopelex |
55 |
2 |
Lamepon A |
6 |
3 |
Tetradecanol sodium sulphate |
15 |
4 |
Polyoxyethylene octadecyl amine |
10 |
5 |
PAMA |
14 |
This dedusting composition is applied to 265m
2in sintering machine desulfuration project, this project operation parameter is as shown in table 8.
Table 8 265m
2sintering machine desulfuration operational factor table
Sequence number |
Parameter |
Unit |
Numerical value |
1 |
Exhaust gas volumn (operating mode) |
m
3/h
|
1620000 |
2 |
Entrance sulfur dioxide concentration |
mg/Nm
3 |
2500 |
3 |
Outlet sulfur dioxide concentration |
mg/Nm
3 |
45 |
4 |
Inlet dust |
mg/Nm
3 |
105 |
5 |
Outlet dust |
mg/Nm
3 |
11.4 |
6 |
Flue-gas temperature |
℃ |
120-160 |
7 |
Sintering deposit annual production |
Ten thousand tons |
265 |
8 |
Ton sintering deposit running cost (agreement) |
Yuan/ton |
4.5 |
9 |
System footprint area |
m
3 |
1000 |
In the present embodiment, before dropping into, inlet flue gas dust content is 105mg/Nm
3, in absorption tower, magnesium hydroxide slurries liquid measure is 600m
3, add this dedusting composition 100kg, drop into this dedusting composition after 15 minutes, exiting flue gas dust content is down to 11.4mg/Nm
3, and stablize maintenance 17 hours, average dust removal efficiency is up to 93.6%, and higher than design load, exhaust gas dust content is lower than emission limit.The technical indicators such as this project desulfur denitrate dust collecting efficiency are as shown in table 9.
Table 9 265m
2sintering machine desulfuration plant running technical indicator
Sequence number |
Project |
Unit |
Mean value |
Design load |
1 |
Desulfuration efficiency |
% |
98.2 |
97.5 |
2 |
Magnesia utilization rate |
% |
99.2 |
98 |
3 |
Efficiency of dust collection |
% |
93.6 |
85 |
4 |
Power consumption |
kW˙h |
529 |
≤667 |
5 |
Water consumption |
t/h |
42 |
55 |
6 |
Magnesia consumption |
t/h |
1.98 |
2 |
7 |
SR |
Pa |
600 |
≤800 |
Conclusion: dedusting composition and desulfurization slurry weight ratio are 0.017wt%, under this ratio, this dedusting composition dust removing effects is stablized, and exhaust gas dust content is lower than discharge standard.
embodiment 4
The dedusting composite formula that the present embodiment adopts is as shown in table 10.
Table 10 dedusting composite formula
Sequence number |
Title |
Consumption (kg) |
1 |
Neopelex |
12 |
2 |
Lamepon A |
6 |
3 |
Tetradecanol sodium sulphate |
1 |
4 |
Polyoxyethylene (5) hydrogenated-tallow group amine |
4 |
5 |
PAMA |
7 |
This dedusting composition is applied to 132m
2in sintering machine desulfuration project, this project operation parameter is as shown in table 11.
Table 11 132m
2sintering machine desulfuration island suction parameter table
Sequence number |
Parameter |
Unit |
Numerical value |
1 |
Exhaust gas volumn (operating mode) |
m
3/h
|
810000 |
2 |
Entrance sulfur dioxide concentration |
mg/Nm
3 |
1600 |
3 |
Outlet sulfur dioxide concentration |
mg/Nm
3 |
25 |
5 |
Inlet dust |
mg/Nm
3 |
180 |
6 |
Outlet dust |
mg/Nm
3 |
9.5 |
7 |
Flue-gas temperature |
℃ |
150 |
8 |
Sintering deposit annual production |
Ten thousand tons |
90 |
9 |
Ton sintering deposit running cost (agreement) |
Yuan/ton |
4.23 |
10 |
System footprint area |
m
3 |
600 |
In the present embodiment, before adding this dedusting composition, inlet flue gas dust content is 180mg/Nm
3, adding this dedusting composition of 30kg to magnesium hydroxide slurries liquid measure is 250m
3absorption tower in, after 5 minutes, exiting flue gas dust content is down to 10mg/Nm
3, and stablize maintenance 20 hours, average dust removal efficiency, up to 94.7%, higher than design load 88%, and meets emission limit.The technical indicators such as this project desulfurization dust-removing efficiency are as shown in table 12.
Table 12 132m
2sintering machine desulfuration island technical indicator
Sequence number |
Project |
Unit |
Mean value |
Design load |
1 |
Desulfuration efficiency |
% |
98.8 |
98.5 |
2 |
Magnesia profit |
% |
99.9 |
98 |
3 |
Efficiency of dust collection |
% |
94.7 |
88 |
4 |
Power consumption |
kW˙h |
529 |
≤667 |
5 |
Water consumption |
t/h |
42 |
55 |
6 |
Magnesia consumes |
t/h |
0.64 |
2 |
7 |
SR |
Pa |
600 |
≤700 |
Conclusion: dedusting composition and desulfurization slurry weight ratio are 0.012wt%, under this ratio, this dedusting composition dust removing effects is stablized, and exhaust gas dust content is lower than discharge standard.
According to the embodiment of four in the present invention, this dedusting composition is remarkable to the removal effect of fine solid particle remaining after dedusting, for exhaust gas dust content at 30 ~ 500mg/Nm
3coal-burning boiler, sintering machine/pelletizing flue gas has good dust removing effects, and the exhaust gas dust content after process is all lower than state emission standard.
The present invention is not limited to above-mentioned embodiment, and when not deviating from flesh and blood of the present invention, any distortion that it may occur to persons skilled in the art that, improvement, replacement all fall into scope of the present invention.