[0001] The use of an electrostatic precipitator for removing particles from gas is indeed
well known. Typically, this type of device utilizes the corona discharge effect, i.e.,
the charging of the particles by passing them through an ionization field established
by a plurality of discharge electrodes. The charged particles are then attracted to
a grounded collecting electrode plate from which they are removed by vibration or
rapping.
[0002] This type of precipitator is exemplified in U.S. 3,109,720 to Cummings and 3,030,753
to Pennington.
[0003] A common problem associated with electrostatic precipitators is maximizing the efficiency
of particle removal. For example, in the utility industry, failure to meet particle
emission standards may necessitate reduction in power output (derating). Gas conditioning
is an important method for accomplishing this goal as described in a book entitled
"Industrial Electrostatic Precipitation" by Harry J. White, Addison-Wesley Publishing
Company, Inc. (Reading, Massachusetts, 1963), p. 309. This book is incorporated herein
by reference to the extent necessary to complete this disclosure.
[0004] An early patent disclosing a gas conditioning method for improving electrostatic
precipitator performance is U.S. 2,381,879 to Chittum according to which the efficiency
of removal of "acidic" particulates is increased by adding organic amine to the gas,
specifically, primary amines such as methylamine, ethylamine, n-propylamine and sec-butylamine;
secondary amines such as dimethylamine, diethylamine, dipropylamine and diisobutylamine;
tertiary amines such as trimethylamine, triethylamine, tripropylamine and triisobutylamine;
polyamines such as ethylenediamine and cyclic amines such as piperidine.
[0005] Chittum does not disclose the use of alkanolamines as gas conditioners for electrostatic
precipitators. However U.S. 4,123,234 to Vossos does disclose the use of what he alleges
to be alkanolamine phosphate esters for that purpose and has been patented over Chittum.
[0006] The Vossos patent allegedly demonstrates the operability of the alkanolamine phosphate
esters as electrostatic precipitator efficiency enhancers through a fly ash bulk electrical
resistivity test according to which resistivity of a treated sample in a conductivity
cell was determined by applying an electrode to the sample, applying voltages to the
cell and measuring voltages across and current through the fly ash. The patent fails
to disclose that the additives were ever tested in an electrostatic precipitator.
It is doubted by the present inventors that aqueous solution chemistry as utilized
in Vossos can be used to predict behaviour of chemicals in the gas system found in
electrostatic precipitators. In fact, when tested for efficiency enhancement in an
electrostatic precipitator system, it was discovered that these compounds demonstrated
little, if any, efficacy. In the tests conducted, the alkanolamine phosphate ester
actually decreased efficiency.
[0007] Upon further investigation it was unexpectedly discovered that, as compared to the
alkanolamine phosphate esters touted by Vossos, tested free base unneutralized amino
alcohols were far superior as electrostatic precipitation efficiency enhancers. These
compounds will hereinafter be referred to as free base amino alcohols, and any such
reference is intended to include mixtures of such compounds.
[0008] According to the present invention therefore there is provided a method for removing
particles from a particle-laden gas stream using an electrostatic precipitator, characterised
by adding to said gas stream from 1 to 200 parts of effective free base amino alcohol
additive, per million parts of gas.
[0009] Free base amino alcohols consist of molecules containing primary, secondary, or tertiary
amines which are unneutralized, that is, they are in the basic form with an unbonded
pair of electrons available for reaction. These compounds also have free hydroxyl
functionalities and could, accordingly, be subjected to those reactions involving
hydroxyl groups.
[0010] Quite distinctively from the above-described free base amino alcohols, the alkanolamine
phosphate esters of Vossos are prepared by the reaction of alkanolamine with phosphoric
acid. As a result, the amine functionality is neutralized making it no longer available
to react as an amine. Also, the reaction of alkanolamine with phosphoric acid causes
reaction of the alcohol functionality to form the phosphate esters, thus, reducing
or eliminating the alcohol functionality present in the molecules.
[0011] Amino alcohols can be categorized as aliphatic, aromatic and cycloaliphatic. Illustrative
examples of aliphatic amino alcohols are as follows:
ethanolamine
diethanolamine
triethanolamine
propanolamine
dipropanolamine
tripropanolamine
isopropanolamine
diisopropanolamine
triisopropanolamine
diethylaminoethanol
2-amino-2-methylpropanol-1
1-dimethylaminopropanol-2
2-aminopropanol-1
N-methylethanolamine
dimethylethanolamine
N,N-diisopropylethanolamine
N-aminoethylethanolamine
N-methyldiethanolamine
N-ethyldiethanolamine
N-2-hydroxypropylethylenediamine
N-2-hydroxypropyldiethylenetriamine
aminoethoxyethanol
N-methylaminoethoxyethanol
N-ethylaminoethoxyethanol
1-amino-2-butanol
di-sec-butanolamine
tri-sec-butanolamine
2-butylaminoethanol
dibutylethanolamine
1-amino-2-hydroxypropane
2-amino-1,3-propanediol
aminoethylene glycol
dimethylaminoethylene glycol
methylaminoethylene glycol
aminopropylene glycol
3-aminopropylene glycol
3-methylaminopropylene glycol
3-dimethylaminopropylene glycol
3-amino-2-butanol
[0012] Illustrative examples of aromatic amino alcohols are as follows:
p-aminophenylethanol
o-aminophenylethanol
phenylethanolamine
phenylethylethanolamine
p-aminophenol
p-methylaminophenol
p-dimethylaminophenol
o-aminophenol
p-aminobenzyl alcohol
p-dimethylaminobenzyl alcohol
p-aminoethylphenol
p-dimethylaminoethylphenol
p-dimethylaminoethylbenzyl alcohol
1-phenyl-1,3-dihydroxy-2-aminopropane
1-phenyl-1-hydroxy-2-aminopropane
1-phenyl-1-hydroxy-2-methylaminopropane
[0013] Illustrative examples of cycloaliphatic amino alcohols are as follows:
cyclohexylaminoethanol
dicyclohexylaminoethanol
4,4'-di(2-hydroxyethylamino)-di-cyclohexylmethane
2-aminocyclohexanol
3-aminocyclohexanol
4-aminocyclohexanol
2-methylaminocyclohexanol
2-ethylaminocyclohexanol
dimethylaminocyclohexanol
diethylaminocyclohexanol
aminocyclopentanol
aminomethylcyclohexanol
[0014] Of course, the aliphatic and cycloaliphatic amino alcohols can be grouped together
under the category alkanolamines.
[0015] The amount of free base amino alcohol required for effectiveness as an electrostatic
precipitator efficiency enhancer (EPEE) may vary between the limits of 1 and 200 parts
of active amino alcohol per million parts of gas being treated (ppm). The optimum
amount will, of course, depend on known factors such as the nature of the problem
being treated, however, 5 ppm is a preferred lower limit and 100 ppm represents a
preferred upper limit. Since the systems tested required at least about 20 ppm active
amino alcohol, that dosage rate represents the most preferred lower limit. Furthermore,
since it is believed that about 75 ppm active amino alcohol will be the highest dosage
most commonly experienced in actual precipitator systems, that represents the most
preferred upper limit.
[0016] While the treatment could be fed neat, it is preferably fed as an aqueous solution.
Any well known feeding system could be used, provided good distribution across the
gas stream duct is ensured. For example, a bank of air-atomized spray nozzles upstream
of the precipitator proper has proven to be quite effective.
[0017] If the gas temperature in the electrostatic precipitator exceeds the decomposition
point of a particular amino alcohol being considered, a higher homolog with a higher
decomposition point should be used. For example, in certain tests conducted, diethanolamine
was not effective as an EPEE at about 620°F (327°C), but a higher homolog, such as
triethanolamine, should be suitable at such temperature.
Examples
[0018] A series of tests were conducted to determine the efficacy of various amino alcohols
using a pilot electrostatic precipitator system comprised of four sections: (1) a
heater section, (2) a particulate feeding section, (3) a precipitator proper and (4)
an exhaust section.
[0019] The heater section consists of an electric heater in series with an air-aspirated
oil burner. It is fitted with several injection ports permitting the addition of a
chemical and/or the formulation of synthetic flue gas. Contained within the heater
section is a damper used to control the amount of air flow into the system.
[0020] Following the heater section is the particulate feeding section which consists of
a 10 foot (304.8 cm) length of insulated duct work leading into the precipitator proper.
Fly ash is added to the air stream and enters the flue gas stream after passing through
a venturi throat. The fly ash used was obtained from industrial sources.
[0021] The precipitator proper consists of two duct-type precipitators, referred to as inlet
and outlet fields, placed in series. Particulate collected by the unit is deposited
in hoppers located directly below the precipitator fields and is protected from reentrainment
by suitably located baffles.
[0022] The exhaust section contains a variable speed, induced-draft fan which provides the
air flow through the precipitator. Sampling ports are located in the duct-work to
allow efficiency determinations to be made by standard stack sampling methods.
[0023] Optical density, O.D., is a measure of the amount of light absorbed over a specific
distance. Optical density is proportional to particulate concentration, C, and optical
path length, L, according to:

where K is a constant and is a function of the particle size distribution and other
physical properties of the particle.
[0024] Since optical density is directly proportional to particulate concentration it may
be used to monitor emissions. Accordingly, an optical density monitor located in an
exit duct of an electrostatic precipitator would monitor particulate emissions with
and without the addition of chemical treatments to the gases. Treatments which increase
the efficiency of a unit would result in decreased dust loadings in the exit gas.
This would be reflected by a decrease in O.D. To ensure reproducibility of results,
particulate size distribution and other particulate properties, such as density and
refractive index, should not change significantly with time.
[0025] Accordingly, in the tests conducted, a Lear Siegler RM-41 optical density monitor
located in the exit duct-work was used to evaluate precipitator collection performance.
[0026] The use of the pilot electrostatic precipitator and optical density monitor for evaluating
the efficacy of a chemical treatment as an EPEE is illustrated below in Example 1.
Example 1
[0027] Fly ash produced as the combustion by-product of an approximately 1 % sulfur coal
was found to have a resistivity of 1011 ohm-cm at 300°F( 149°C). Utilizing this ash
type and a flue gas similar to that of an industrial utility plant, pilot electrostatic
precipitator studies were performed to determine whether or not a gas conditioning
agent could enhance the collection efficiency. The results of the trial are presented
in Table 1.

[0028] As seen in Table 1, the chemical additive at 66 ppm effected an increase in precipitator
efficiency of from 94.44% to 99.49%. The significantly enhanced efficiency is also
reflected by the 84.3% reduction in optical density.
Example 2
[0029] The amino alcohols were tested for EPEE activity using several different industrial
fly ashes. The various fly ashes were characterized by known standard slurry analysis,
and x-ray fluorescence and optical emission spectra with the following results as
reported in Table 2.

[0030] The results of the tests evaluating the efficacy of various amino alcohols are reported
below in Table 3 in terms of % decrease in optical density (% d.O.D.). The column
headed "Fly Ash Content" is the amount of fly ash in the gas in grains per actual
cubic foot (gr/ACF) and grains per actual cubic metre (gr/ACM). Gas flow rates in
the pilot precipitator are reported as actual cubic feet per minute (ACFM) and actual
cubic metre per minute (ACMM) at 310°F (154°C) and the SO
z and S0
3 reported are the respective amounts contained in the gas in terms of parts per million
parts of gas. The H
2O is approximate volume % in the gas. The chemical feed rates are parts of active
treatment per million parts of gas.

[0031] As can be seen from Table 3, the amino alcohols were effective as electrostatic precipitator
efficiency enhancers. While the compounds tested were alkanolamines, it is believed
that amino alcohols as a class would be effective for the purpose. Also, while the
test gas contained fly ash and S0
2, which are conditions typically found in coal-fired boilers, it is believed that
the EPEE's according to the present invention would be effective in other gas systems
where particulate matter is to be removed by an electrostatic precipitator.
[0032] As a result of these tests, diethanolamine, being the most active compound, is considered
to be the most preferred additive.
Example 3
[0033] To provide a comparison with a phosphate ester according to the above-noted Vossos
Patent, diethanolamine was tested for EPEE efficacy as was diethanolamine phosphate
ester made according to the patent.
[0034] In preparing the alleged ester, 0.435 mole of phosphoric acid was reacted with 0.435
mole of diethanolamine to yield an equimolar mixture. After allowing approximately
1.35 hours of reaction time, the material was tested.
[0035] The results of these tests are reported below in Table 4 in terms of reduction in
O.D. (% d.O.D.). The fly ash used was fly ash IV from Table 2.

[0036] As can be seen from Table 4, the diethanolamine was far superior to the diethanolamine
phosphate ester as an EPEE. The negative % d.O.D. value for the phosphate ester run
meant that the particle collection efficiency of the pilot precipitator was actually
decreased by this compound.
[0037] Preliminary results of field trials presently being conducted at a utility plant
confirm the above- reported EPEE efficacy studies.
[0038] Industrial boiler systems commonly include the boiler proper and heat exchanger means
to receive hot combustion gas from the boiler. The heat exchanger can be either an
economizer, which uses the combustion gas to heat boiler feedwater, or an air preheater,
used to heat air fed to the boiler. In either case, the heat exchanger acts to cool
the combustion gas.
[0039] The most widely used boiler fuels are oil or coal, both of which contain sulfur.
Accordingly, the combustion gas can contain sulfur trioxide which reacts with moisture
in the combustion gas to produce the very corrosive sulfuric acid. Since the corrosive
effects are, indeed, quite evident on metal surfaces in the heat exchanger equipment,
cold-end additive treatments are injected into the combustion gas upstream of the
economizer or air preheater to reduce corrosion.
[0040] If a boiler is coal-fired, electrostatic precipitator equipment is sometimes provided
downstream of the heat exchanger to remove fly ash and other particles from the combustion
gas. To improve the efficiency of particle collection, electrostatic precipitation
efficiency enhancers are typically added to the combustion gas at a location between
the heat exchanger means and the precipitator, that is, downstream of the heat exchanger
means.
[0041] Based on economic and/or efficacy considerations, it may be desirable to blend various
amino alcohols for optimization purposes.
[0042] It is understood that the amino alcohol can be fed directly or formed in the gas
stream, e.g., a decomposition product.
1. A method for removing particles from a particle-laden gas stream using an electrostatic
precipitator, characterised by adding to said gas stream from 1 to 200 parts of effective
free base amino alcohol additive, per million parts of gas.
2. A method as claimed in claim 1, characterised in that said additive is added as
an aqueous solution.
3. A method as claimed in claim 1 or 2, characterised in that said additive is free
base alkanolamine.
4. A method as claimed in claim 3, characterised in that said additive is water-soluble,
aliphatic alkanolamine.
5. A method as claimed in any one of the preceding claims, characterised in that said
additive is at least one member selected from the group consisting of monoethanolamine,
diethanolamine, triethanolamine, methylethanolamine, N-aminoethylethanolamine, and
N,N diethylethanolamine.
6. A method as claimed in claim 5, characterised in that said additive is diethanolamine.
7. A method as claimed in any one of the preceding claims, characterised in that said
additive is added in an amount of from 5 to 100 parts of active additive per million
parts of gas.
8. A method as claimed in claim 7, characterised in that said additive is added in
an amount of from 20 to 75 parts of active additive per million parts of gas.
9. A method as claimed in any one of the preceding claims, characterised in that said
additive is sprayed into said gas stream.
10. A method as claimed in any one of the preceding claims, characterised in that
said gas stream is the combustion gas of a boiler system fired by sulfur-containing
coal.
11. A method as claimed in any one of the preceding claims, characterised in that
said gas stream contains fly ash.
12. A method as claimed in any one of the preceding claims, characterised in that
said gas stream contains sulfur dioxide.
13. A method as claimed in any one of the preceding claims, characterised by use of
a precipitator system comprising heat exchanger means for cooling said gas stream
and electrostatic precipitator means connected to said heat exchanger means for receiving
said cooled gas stream, and characterised in that said amino alcohol is added to said
gas stream at a location between said heat exchanger means and said electrostatic
precipitator.
1. Procédé pour éliminer des particules d'un courant de gaz au moyen d'un dispositif
de précipitation électrostatique, procédé caractérisé en ce que l'on ajoute au courant
gazeux 1 à 200 parties d'un amino-alcool, à l'état de base libre efficace, par million
de parties du gaz.
2. Procédé selon la revendication 1 caractérisé en ce que l'additif est ajouté en
solution aqueuse.
3. Procédé selon la revendication 1 ou 2 caractérisé en ce que l'additif est une alcanolamine
à l'état de base libre.
4. Procédé selon la revendication 3 caractérisé en ce que l'additif est une alcanolamine
aliphatique soluble dans l'eau.
5. Procédé selon l'une quelconque des revendications précédentes, caractérisé en ce
que l'additif est constitué par une ou plusieurs substances choisies parmi la monoéthanolamine,
la diéthanolamine, la triéthanotamine, la méthyléthanolamine, la N-aminoéthyléthanolamine,
et la N,N-diéthyléthanol- amine.
6. Procédé selon la revendication 5 caractérisé en ce que l'additif est la diéthanolamine.
7. Procédé selon l'une quelconque des revendications précédentes, caractérisé en ce
que l'additif est ajouté dans une proportion de 5 à 100 parties d'additif actif par
million de parties du gaz.
8. Procédé selon la revendication 7 caractérisé en ce que l'additif est ajouté dans
une proportion de 20 à 75 parties d'additif actif par million de parties du gaz.
9. Procédé selon l'une quelconque des revendications précédentes, caractérisé en ce
que l'additif est pulvérisé dans le courant gazeux.
10. Procédé selon l'une quelconque des revendications précédentes, caractérisé en
ce que le courant gazeux est le gaz de combustion d'un système de chaudière chauffé
par un charbon contenant du soufre.
11. Procédé selon l'une quelconque des revendications précédentes, caractérisé en
ce que le courant de gaz contient des cendres volantes.
12. Procédé selon l'une quelconque des revendications précédentes, caractérisé en
ce que le courant de gaz contient du dioxyde de soufre.
13. Procédé selon l'une quelconque des revendications précédentes, caractérisé en
ce que l'on opère avec un dispositif de précipitation comprenant un échangeur de chaleur
pour refroidir le courant gazeux et un système de précipitation électrostatique relié
à l'échangeur de chaleur et qui reçoit le courant gazeux refroidi, et en ce que l'amino-alcool
est ajouté au courant de gas en un point situé entre l'échangeur de chaleur et le
système de précipitation électrostatique.
1. Verfahren zur elektrostatischen Abscheidung von Schwebstoffen aus einem Gasstrom,
dadurch gekennzeichnet, daß man dem Gasstrom 1 bis 20 ppm Aminoalkohol als freie Base
zusetzt.
2. Verfahren nach Anspruch 1, dadurch gekennzeichnet, daß man den Aminoalkohol als
wässrige Lösung zusetzt.
3. Verfahren nach Anspruch 1 oder 2, dadurch gekennzeichnet, daß man als Aminoalkohol
ein Alkanolamin zusetzt.
4. Verfahren nach Anspruch 3, dadurch gekennzeichnet, daß man ein wasserlösliches
aliphatisches Alkanolamin zusetzt.
5. Verfahren nach Anspruch 1 bis 4, dadurch gekennzeichnet, daß man als Aminoalkohol
Monoethanolamin, Diethanolamin, Triethanolamin, Methylethanolamin, N-Aminoethylethanolamin
und/oder N,N-Diethylethanolamin zusetzt.
6. Verfahren nach Anspruch 5, dadurch gekennzeichnet, daß man Diethanolamin verwendet.
7. Verfahren nach Anspruch 1 bis 6, dadurch gekennzeichnet, daß man 5 bis 100 ppm
Aminoalkohol dem Gas zusetzt.
8. Verfahren nach Anspruch 7, dadurch gekennzeichnet, daß man 20 bis 75 ppm Aminoalkohol
dem Gas zusetzt.
9. Verfahren nach Anspruch 1 bis 8, dadurch gekennzeichnet, daß man den Aminoalkohol
in den Gasstrom einspritzt.
10. Verfahren nach Anspruch 1 bis 9, dadurch gekennzeichnet, daß der Gasstrom ein
Abgas aus einer Kesselanlage ist, in der schwefelhaltige Kohle verfeuert wird.
11. Verfahren nach Anspruch 1 bis 10, dadurch gekennzeichnet, daß der Gasstrom Flugasche
enthält.
12. Verfahren nach Anspruch 1 bis 11, dadurch gekennzeichnet, daß der Gasstrom Schwefeldioxid
enthält.
13. Verfahren nach Anspruch 1 bis 12, dadurch gekennzeichnet, daß man in einem Wärmeaustauscher
den Gasstrom abkühlt, den abgekulilten Gasstrom in einen elektrostatischen Abscheider leitet und den Aminoalkohol
in den Gasstrom zwischen Wärmeaustauscher und elektrostatischem Abscheider einbringt.