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Patent 2565750 Summary

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(12) Patent Application: (11) CA 2565750
(54) English Title: METHOD AND APPARATUS UTILISING HYDROGEN PEROXYDE TO REDUCE SOX, NOX AND HEAVY METAL EMISSIONS
(54) French Title: PROCEDE ET APPAREIL UTILISANT DU PEROXYDE D'HYDROGENE POUR REDUIRE LES EMISSIONS DE SOX, NOX ET DE METAUX LOURDS
Status: Deemed Abandoned and Beyond the Period of Reinstatement - Pending Response to Notice of Disregarded Communication
Bibliographic Data
(51) International Patent Classification (IPC):
  • B01D 53/60 (2006.01)
  • B01D 53/56 (2006.01)
  • B01D 53/64 (2006.01)
  • B01D 53/75 (2006.01)
  • C01B 17/05 (2006.01)
  • C01B 17/50 (2006.01)
  • C01B 21/40 (2006.01)
(72) Inventors :
  • PARRISH, CLYDE F. (United States of America)
  • CHUNG, LANDY (United States of America)
(73) Owners :
  • NATIONAL AERONAUTICS AND SPACE ADMINISTRATION
(71) Applicants :
  • NATIONAL AERONAUTICS AND SPACE ADMINISTRATION (United States of America)
(74) Agent: GOWLING WLG (CANADA) LLP
(74) Associate agent:
(45) Issued:
(86) PCT Filing Date: 2005-04-08
(87) Open to Public Inspection: 2005-12-01
Examination requested: 2010-03-09
Availability of licence: N/A
Dedicated to the Public: N/A
(25) Language of filing: English

Patent Cooperation Treaty (PCT): Yes
(86) PCT Filing Number: PCT/US2005/011864
(87) International Publication Number: US2005011864
(85) National Entry: 2006-11-03

(30) Application Priority Data:
Application No. Country/Territory Date
10/845,418 (United States of America) 2004-05-11
11/040,294 (United States of America) 2005-01-14
PCT/US2004/027778 (United States of America) 2004-08-26

Abstracts

English Abstract


Methods and apparatus utilizing hydrogen peroxide are useful to reduce SOx and
mercury (or other heavy metal) emissions from combustion flue gas streams. The
methods and apparatus may further be modified to reduce NOx emissions.
Continuous concentration of hydrogen peroxide to levels approaching or
exceeding propellant-grade hydrogen peroxide facilitates increased system
efficiency. In this manner, combustion flue gas streams can be treated for the
removal of SOx and heavy metals, while isolating useful by-products streams of
sulfuric acid as well as solids for the recovery of the heavy metals. Where
removal of NOx emissions is included, nitric acid may also be isolated for use
in fertilizer or other industrial applications.


French Abstract

Des procédés et un appareil utilisant le peroxyde d'hydrogène sont utiles pour réduire les émissions de SO¿x? et de mercure (ou d'autres métaux lourds) provenant de fumées de combustion. Les procédés et l~appareil peuvent de plus être modifiés pour réduire les émissions de NO¿x?. Une concentration continue de peroxyde d'hydrogène à des niveaux approchant ou excédant le peroxyde d~hydrogène de niveau propulseur facilite l'efficacité améliorée du système. De cette façon, les courants de fumée de combustion peuvent être traités pour extraire les SO¿x? et les métaux lourds, tout en isolant les courants de sous-produits utiles d'acide sulfurique ainsi que de solides pour récupérer les métaux lourds. Lorsque l~extraction des émissions de NO¿x? est incluse, l'acide nitrique peut aussi être isolé pour être utilisé dans les engrais ou d~autres applications industrielles.

Claims

Note: Claims are shown in the official language in which they were submitted.


8
What is claimed is:
1. A method of treating a gas stream for removal of at least oxides of sulfur,
the method
comprising:
scrubbing the gas stream with a first hydrogen peroxide solution, thereby
producing a
first scrubber liquor;
maintaining a desired hydrogen peroxide concentration in the first scrubber
liquor by
regulating a flow of the first hydrogen peroxide solution; and
removing a by-product stream containing sulfuric acid after attaining a
desired
sulfuric acid concentration in the first scrubber liquor.
2. The method of claim 1, further comprising:
after scrubbing the gas stream with the first hydrogen peroxide solution,
oxidizing the
gas stream using a second hydrogen peroxide solution in an oxidation process
adapted to convert nitric oxide to nitrogen dioxide; and
after oxidizing the gas stream, scrubbing the gas stream with a third hydrogen
peroxide solution and removing a by-product stream containing nitric acid;
wherein the second hydrogen peroxide solution is concentrated to a level of
approximately 75% or more by volume prior to use in oxidizing the gas
stream.
3. The method of claim 1, wherein scrubbing the gas stream with the first
hydrogen
peroxide solution further comprises:
feeding the gas stream into a scrubber;
feeding the first hydrogen peroxide solution into the scrubber;
removing solids from the first scrubber liquor; and
recycling the first scrubber liquor into the scrubber with the first hydrogen
peroxide
solution.
4. The method of claim 3, further comprising:
sampling a mixture of the first hydrogen peroxide solution and the recycled
first
scrubber liquor for a level of hydrogen peroxide; and

9
controlling the level of hydrogen peroxide in the mixture to be at least a
predetermined level.
5. The method of claim 3, wherein removing solids comprises centrifuging the
resulting
scrubber liquor.
6. The method of claim 2, wherein scrubbing the gas stream with the third
hydrogen
peroxide solution further comprises:
feeding the gas stream into a scrubber;
feeding the third hydrogen peroxide solution into the scrubber;
removing solids from a resulting second scrubber liquor; and
recycling the second scrubber liquor into the scrubber with the third hydrogen
peroxide solution.
7. The method of claim 6, further comprising:
sampling a mixture of the third hydrogen peroxide solution and the recycled
second
scrubber liquor for a level of hydrogen peroxide; and
controlling the level of hydrogen peroxide in the mixture to be at least a
predetermined level.
8. The method of claim 7, wherein the predetermined level of hydrogen peroxide
is an
amount necessary to provide a stoichiometric excess of hydrogen peroxide for
reaction with the gas stream.
9. A process for converting vapor streams containing at least one oxide of
sulfur therein
to a liquid of oxy-acid(s) of sulfur composition comprising:
directing a vapor stream containing at least one oxide of sulfur to a first
contact zone;
contacting the vapor stream with water to form oxy-acid(s) of sulfur from the
at least
one oxide of sulfur;
directing the acid(s) as a second stream to a second contact zone;
exposing the second stream to hydrogen peroxide which is present within the
second
contact zone to convert at least some of any oxy-acid(s) of sulfur other than
in
the sulfuric form present within the second stream to a sulfate ion;

10
sampling the stream within the second contact zone to determine the relative
amount
of hydrogen peroxide within the second contact zone; and
adding hydrogen peroxide to the second contact zone when the sampling
determines
there is less than excess of hydrogen peroxide in the second stream.
10. The process of claim 9, wherein samples are removed from the second
contact zone,
the pH of the samples is determined, and the pH of materials within the second
contact zone is adjusted within the range of 7.0 to < 0.1.
11. The process of claim 9, wherein the predetermined excess of hydrogen
peroxide is at
least 0.1% by weight of the second stream.
12. A process for converting an aqueous stream containing sulfur oxide
products to a
useful chemical liquid composition comprising:
directing the stream to a first contact zone;
exposing the stream to hydrogen peroxide which is present within the first
contact
zone to convert at least some of any oxy-acid(s) of sulfur other than in the
sulfuric acid form present to sulfate ions;
adding hydrogen peroxide to the first contact zone when the sampling
determines
there is less than an excess of hydrogen peroxide in the solution; and
adding a solution comprising potassium hydroxide or other base to the first
contact
zone to maintain a pH between 7.0 and < 0.1 within the first contact zone and
to form a solution of a salt of sulfuric acid.
13. A process for converting vapor streams containing at least one oxide of
sulfur therein
to a useful chemical liquid composition comprising:
directing a vapor stream containing at least one oxide of sulfur to a first
contact zone;
contacting the vapor stream with water to form oxy-acid(s) of sulfur from the
at least
one oxide of sulfur;
directing the acid(s) as a second stream to a second contact zone;
exposing the second stream to hydrogen peroxide which is present within the
second
contact zone to convert at least some of any oxy-acid(s) of sulfur other than
in
the sulfuric acid form present within the second stream to a sulfate ion;

11
adding hydrogen peroxide to the second contact zone when the sampling
determines
there is less than an excess of hydrogen peroxide in the second stream; and
adding a solution comprising potassium hydroxide or other base to the second
stream
to maintain a pH between 7.0 and < 0.1 within the second stream within the
second contact zone to form a solution of a salt of sulfuric acid.
14. A system for the removal of at least oxides of sulfur from a combustion
flue gas, the
system comprising:
a water wash coupled to receive a raw flue gas stream;
a first scrubber coupled to receive an exit gas stream from the water wash and
coupled
to receive a first hydrogen peroxide solution;
a centrifuge coupled to receive a first scrubber liquor from the first
scrubber and to
provide a recycled scrubber liquor to the first scrubber after removal of
solids
from the first scrubber liquor;
a control system to maintain a desired hydrogen peroxide concentration in the
recycled scrubber liquor and to maintain a desired sulfuric acid concentration
in the recycled scrubber liquor;
a demister coupled to receive an exit gas stream from the first scrubber; and
a neutralizer coupled to receive an exit gas stream from the demister.
15. The system of claim 14, further comprising:
an oxidation tower coupled to receive an exit gas stream from the demister or
the
neutralizer, and to receive a second hydrogen peroxide solution from a
hydrogen peroxide concentrator;
a second scrubber coupled to receive an exit gas stream from the oxidation
tower and
coupled to receive a third hydrogen peroxide solution and a recycled liquor
from the second scrubber; and
a neutralizer coupled to receive an exit gas stream from the second scrubber.
16. A method of treating a gas stream for removal of heavy metal components
and at least
oxides of sulfur, the method comprising:
feeding the gas stream into a scrubber;
feeding a first hydrogen peroxide solution into the scrubber;

12
scrubbing the gas stream with the first hydrogen peroxide solution, thereby
producing
a first scrubber liquor containing sulfuric acid and insoluble oxides of the
heavy metal components;
recycling the first scrubber liquor to the scrubber to attain a desired
concentration of
sulfuric acid; and
removing solids from the first scrubber liquor, wherein the solids contain at
least a
portion of the insoluble oxides of the heavy metal components.
17. The method of claim 16, further comprising:
neutralizing a portion of the first scrubber liquor after removing solids,
wherein the
first scrubber liquor further contains soluble forms of the heavy metal
components and/or soluble oxides of the heavy metal components and wherein
neutralizing the portion of the first scrubber liquor forms second solids from
the soluble forms of the heavy metal components and/or the soluble oxides of
the heavy metal components; and
removing the second solids from the neutralized first scrubber liquor.
18. The method of claim 16, further comprising:
maintaining a desired hydrogen peroxide concentration in the first scrubber
liquor by
regulating a flow of the first hydrogen peroxide solution; and
removing a by-product stream containing sulfuric acid after attaining the
desired
sulfuric acid concentration in the first scrubber liquor.
19. The method of claim 18, further comprising:
sampling a mixture of the first hydrogen peroxide solution and the recycled
first
scrubber liquor for a level of hydrogen peroxide; and
controlling the level of hydrogen peroxide in the mixture to be at least a
predetermined level.
20. The method of claim 16, wherein removing solids comprises centrifuging the
resulting scrubber liquor.

13
21. A method of treating a gas stream for removal of mercury and at least
oxides of
sulfur, the method comprising:
feeding the gas stream into a scrubber;
feeding a first hydrogen peroxide solution into the scrubber;
scrubbing the gas stream with the first hydrogen peroxide solution, thereby
producing
a first scrubber liquor containing sulfuric acid and insoluble oxides of
mercury;
recycling the first scrubber liquor to the scrubber to attain a desired
concentration of
sulfuric acid; and
centrifuging the first scrubber liquor to remove at least a portion of the
insoluble
oxides of mercury.
22. The method of claim 21, further comprising:
neutralizing a portion of the first scrubber liquor after centrifuging,
wherein the first
scrubber liquor further contains soluble forms of mercury and/or soluble
oxides of mercury and wherein neutralizing the portion of the first scrubber
liquor forms second solids from the soluble forms of mercury and/or soluble
oxides of mercury; and
removing the second solids from the neutralized first scrubber liquor.
23. The method of claim 21, further comprising:
maintaining a desired hydrogen peroxide concentration in the first scrubber
liquor by
regulating a flow of the first hydrogen peroxide solution; and
removing a by-product stream containing sulfuric acid after attaining the
desired
sulfuric acid concentration in the first scrubber liquor.
24. The method of claim 23, further comprising:
sampling a mixture of the first hydrogen peroxide solution and the recycled
first
scrubber liquor for a level of hydrogen peroxide; and
controlling the level of hydrogen peroxide in the mixture to be at least a
predetermined level.

Description

Note: Descriptions are shown in the official language in which they were submitted.


CA 02565750 2006-11-03
WO 2005/113116 PCT/US2005/011864
METHOD AND APPARATUS UTILISING HYDROGEN PEROXYDE
TO REDUCE SOX, NOX AND HEAVY METAL EMISSIONS
TECHNICAL FIELD OF THE INVENTION
The present invention relates generally to emission control and in particular
to the
control of emissions from combustion sources.
BACKGROUND OF THE INVENTION
Control of emissions from fossil fuel combustions sources addresses a major
environmental problem. The Environmental Protection Agency (EPA) through the
Clean Air
Act regulates the emissions from fossil fuel-fire power plants. Initial
regulations were
focused on oxides-of-nitrogen (NOx) and oxides-of-sulfur (SOx) emissions, but
newer
regulations will include provisions to control heavy metals (Hg, etc.) and
carbon dioxide.
Gas streams from combustion processes are often scrubbed, i.e., contacted with
water or water solutions, to remove many of their contaminants. However, these
scrubbing
processes often produce hazardous waste streams that must be dealt with.
For the reasons stated above, and for other reasons stated below that will
become
apparent to those skilled in the art upon reading and understanding the
present specification,
there is a need in the art for alternative methods and apparatus for treating
combustion gas
streams.
SUMMARY
Methods and apparatus utilizing hydrogen peroxide to reduce SOx, NOx and
mercury or other oxides-of-metal emissions are described herein. Continuous
concentration
of hydrogen peroxide (H202) to levels approaching or exceeding propellant-
grade hydrogen
peroxide facilitates increased system efficiency. By utilizing methods and
apparatus in
accordance with the invention, combustion flue gas streams can be treated for
the removal of
SOX, NOx and heavy metals, while isolating useful by-products streams of
sulfuric acid and
nitric acid as well as solids for the recovery of the heavy metals. The
apparatus is modular
and components can be added or removed depending upon the specific
requirements for a
given removal operation.

CA 02565750 2006-11-03
WO 2005/113116 PCT/US2005/011864
2
The invention further includes methods and apparatus of varying scope.
BRIEF DESCRIPTION OF TBE DRAWINGS
Figure 1 is a block schematic of an eniission control system in accordance
with an
embodiment of the invention.
Figure 2 is a schematic of a hydrogen peroxide concentration control system
for
use in accordance with one embodiment of the invention.
FIG. 3 is a hydrogen peroxide reaction vessel subsystem for use in accordance
with one embodiment of the invention.
DETAILED DESCRIPTION OF THE INVENTION
In the following detailed description of the preferred embodiments, reference
is
made to the accompanying drawings that .form a part hereof, and in which is
shown by way of
illustration specific preferred embodiments in which the inventions may be
practiced. These
embodiments are described in sufficie t detail to enable those skilled in the
art to practice the
invention, and it is to be understood that other embodiments may be utilized
and that logical,
/
mechanical and chemical change,s/may be made without departing from the spirit
and scope
of the present invention. It is noted that the drawings are not to scale
unless a scale is
provided thereon. The following detailed description is, therefore, not to be
taken in a
limiting sense, and the scope of the present invention is defined only by the
appended claims
and equivalents thereof.
Emission control systems in accordance with the invention address
environmental
pollutants SOx, NOx, and heavy metals. Such systems are designed to control
emissions of
these environmental pollutants to the levels established by the EPA. This
emission control
system provides a method based on hydrogen peroxide to reduce the SOx, NOx,
and metal
and metal oxide emissions from combustion sources to acceptable levels as
established by the
Environmental Production Agency. In addition, useful by-product streams of
sulfuric acid,
nitric acid, salts of these acids, and feedstock for oxides-of-metal
production may be isolated.
Figure 1 is a block schematic of an emission control system in accordance with
an
embodiment of the invention. The process starts with a gas stream, such as raw
flue gas 150

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3
after the particulates have been removed. There are several options for this
design and steps
can be omitted or alternate unit operations may be substituted for the general
processes
depending on the requirements of the installation. These alternate steps are
noted during the
description of the process.
The first step of the process is to use a cooling and wash chamber 102 to cool
and
remove some of the particulates in the entering flue gas 150. Process water
from chamber
103 is provided to chamber 102. Particulates, wash water and heat are sent
from chamber
102 to the sedimentation and cooling Pond 104. Water is then re-circulated
from pond 104
back to water chamber 103.
The washed flue gas is fed from wash chamber 102 to a scrubber tower 105 for
the removal of SOx and/or heavy metals. Scrubber tower 105 uses hydrogen
peroxide from
hydrogen peroxide storage 112 to oxidize sulfurous acid (H2S03) to sulfuric
acid (H2SO4) to
prevent reemission of SO2. Hydrogen peroxide storage 112 preferably provides
aqueous
hydrogen peroxide of approximately 50% to 70% by volume, and more preferably
at
approximately 70% by volume. As the scrubber liquor pH decreases due to the
formation of
sulfuric acid, most of the heavy metal oxides, including Hg, etc., are
dispersed as metal
oxides and/or dissolved hydroxides are converted to sulfates. The remaining un-
dissolved
particulates and insoluble sulfates are removed with centrifuge 106, e.g., a
solid-bowl
centrifuge. Centrifuge 106 continuously removes the solids and circulates the
scrubber liquor
through value 109 back to scrubber tower 105 for continuous scrubbing and
cleaning the flue
gas. When the scrubber liquor (sulfuric acid) reaches the desired
concentration, the cleaned
scrubber liquor is discharged from the centrifuge 106 through valve 110 then
drained to
sulfuric acid storage 111, which can then be utilized for fertilizer or
industrial uses. The
solids from centrifuge 106 are discharged to the recycle solids container 107.
Soluble metals
and metal oxides present in the cleaned scrubber liquor may further be removed
as insoluble
solids upon neutralization of the sulfuric acid as may be performed, for
example, during the
production of fertilizer.
The concentration of hydrogen peroxide in the first scrubbing mixture is
maintained at a predetermined level, e.g., 0.1 to 5 percent by volume.
Concentration of the
first scrubbing mixture may be maintained using a hydrogen peroxide controller
of the type
described below. Additional detail of such a controller may be found in U. S.
Patent No.

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4
6,039,783 issued March 21, 2000 to Lueck et al. and U.S. Patent No. 6,641,638
issued
November 4, 2003 to Lueck et al.
When the flue gas exits the scrubber 105 it contacts the demister 108, where
the
mist that contains sulfuric acid coalesces. The coalesced mist is returned to
the scrubber 105
and the desulfurized flue gas flows to the neutralizer 118. Residual acid
gases are neutralized
with a base in neutralizer 118, and then the cleaned and neutralized flue gas
exits through the
exhaust stack. Alternately, an exhaust fan could be used in place at the
outlet of the
neutralizer 118, if desired, to boost the clean and neutralized flue gas out
of the exhaust stack
as processed flue gas 152.
When or if removal of NOx emissions is also desired, the neutralized flue gas
from neutralizer 118 flows to NO oxidation tower 113, where nitric oxide (NO)
is oxidized to
nitrogen dioxide (NO2). Alternatively, the flue gas may be passed directly
from the demister
108 to the NO oxidation tower 113 for later neutralization, eliminating
neutralizer 118.
Hydrogen peroxide (1I202) from the peroxide storage 112 may be concentrated in
hydrogen
peroxide concentrator 114 or pumped directly into NO oxidation tower 113. The
concentrator 114 is used to increase the concentration of H202 from 70 percent
to as high as
85 percent or more as required by the process. While a variety of methods are
known for the
concentration of hydrogen peroxide, examples particularly suited for use with
embodiments
of the invention may be found in U.S. Patent Application Serial No.
10/845,607, entitled
"CONCENTRATION OF HYDROGEN PERO)(IDE" and filed May 11, 2004.
Oxidation tower 113 decomposes hydrogen peroxide into oxidative species that
convert NO into NO2. One example of this process, the catalytic decomposition
of hydrogen
peroxide, is described in U. S. Patent No. 6,793,903. The oxidized NO in the
flue gas flows
from the oxidation tower 113 to the NOx scrubber tower 115 where it is
captured in an acidic
hydrogen peroxide scrubber liquor. The concentration of hydrogen peroxide in
the second
scrubbing mixture ranges from 0.1 to 5 percent by volume and is controlled by
a second
hydrogen peroxide controller. The cleaned flue gas that exits from scrubber
tower 115 passes
into neutralizer 119, where base is added to neutralize any residual acid
gases. Once
neutralized, the cleaned flue gas exits through the exhaust stack as processed
flue gas 152.
Alternately, an exhaust fan could be used in place at the outlet of the
Neutralizer 119, if
desired, to boost the clean and neutralized flue gas out of the exhaust stack
as processed flue
gas 152.

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ASTM methods D-1608 and D-1609 have been used to measure the concentration
of NOx in the gas streams in early field tests of the emission control system.
These methods
were later modified to measure the nitrite and nitrate ions directly by ion
chromatography.
However, these methods required off-line analysis that was not practical to
use in a
5 continuous process. One optical method (Fourier transform infrared, FTIR)
was used to
measure the hydrogen peroxide concentration directly. The FTIR analytical
method,
developed to analyze scrubber liquor samples, measured the hydrogen peroxide
concentrations continuously with an attenuated total-reflectance (ATR) cell. A
zinc sulfide
ATR crystal was used for the alkaline solutions and an AMTIR ATR crystal was
used for the
acid solutions. Although this analytical method was useful for laboratory
samples, it was not
selected for the hydrogen peroxide controller.
The analytical system used for the control system, as initially described in
US
Patent No. 6,039,783, contains a unique process that controls the
concentration of hydrogen
peroxide. The process is controlled by a programmable logic controller (PLC)
designed to
measure the concentration of hydrogen peroxide and to add additional hydrogen
peroxide as
required to maintain the preset concentration. In addition to the hydrogen
peroxide
controller, the control system contains two commercial controllers, one for pH
and the other
to measure the concentration of sulfuric acid, nitric acid, or salts of these
acids. These
commercial controllers are used to maintain a target pH or concentration and
to add reagents
as required. Details of the design and operation of the control system are
given in the
following section.
The block flow diagram for a hydrogen peroxide controller suited for use with
embodiments of the invention is shown in Figure 2. The hydrogen peroxide PLC
that
controls the operations starts the first sequence by pulling a sample into the
system from
sample point 231 with pump 232 and pumping it through valve 233. The pH probe
247 and
conductivity probe 248 are exposed to the sample before passing the sample
into metallic
filter 234 where a portion of the sample passes through the filter 234 and the
remainder
bypasses the filter 234 and washes the residues back to sample return 245. The
filtrate that
passed through filter 234 continues through valve 235, multiport valve 236,
and sample loop
237. From sample loop 237 the sample returns to multiport valve 236, and then
exits and
returns back to sample return 245. The sequence of events described above
serves to collect
a sample from the sample point 231, filter the sample, fill the sample loop
that has a known

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6
volume, and returns the unused sample to sample return 245. While the sample
loop 237 is
being filled, the metering pump 238 is pulls sodium hypochlorite from
container 239 and
injects a known volume into reaction cel1240 through multiport valve 236. The
second
sequence is triggered by the PLC, which sends a signal to rotate multiport
valve 236 and
pump a second quantity of sodium hypochlorite, but this time it is used to
displace the sample
from the sample loop 237, which is pumped into the reaction cell 240. The
reaction of
sodium hypochlorite with hydrogen peroxide produces water, sodium chloride,
and oxygen,
which causes an increase in pressure in the reaction cell that is sensed by
the pressure
transducer 241. Calibration data programmed into the PLC for pressure change
as a function
of hydrogen peroxide concentration is used to control the concentration of
hydrogen peroxide
in the system. If the measured concentration is below the set concentration, a
pump is
activated to transfer hydrogen peroxide from storage. The hydrogen peroxide
pump stops,
when the measured concentration is greater than the set concentration. This
cycle is repeated
continuously to maintain the set concentration of hydrogen peroxide. While the
concentration is being measured, the filter 234 is back-flushed with water 243
through valve
244 to remove particulates captured by the filter 234. When the back-flush
starts, valve 233
closes and pump 232 stops and the water 243 pushes through the filter 234 and
back to the
sample return 245. In addition, the contents of the reaction cell may be
expelled through
valve 242 to sample waste 246 at this time. Once the back-flush is complete,
the PLC returns
the process to the first sequence and sampling process start over again.
Figure 3 shows the details of the reaction ce11240. The reaction cell body 351
has
an internal chamber 352 that is attached to a gauge guard 353 that protects
the pressure
transducer 241. Sodium hypochlorite and the sample are pulled through sodium
hypochlorite
inlet 355 by metering pump 238. Once the reaction in the pressure cell is
complete, it is
discharged through valve 242 to sample waste 246. The reaction cell is
fabricated preferably
from a machinable corrosion-resistant polymer. While the foregoing brief
description of the
control of hydrogen peroxide concentration is included to aid the reader, a
more detailed
description is provided in U.S. Patent No. 6,039,783 and U.S. Patent No.
6,641,638 as noted
previously.
The pH may be controlled with commercially-recognized devices, such as
Rosemont's model 0054pH/ORP-08 pH controller and a model 306P-02010055 pH
probe.
The pH probe is item 247 in Figure 2 and it is used to continuously measure
the pH. The pH

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7
controller system has proportional algorithms that adjust the pump feed rate
as the pH set-
point is approached. For one embodiment, the pH is controlled to a level of
between 7.0 and
<0.1 by adding a base, e.g., potassium hydroxide. The concentration of
sulfuric acid, nitric
acid, or salts of these acids, is controlled with the Rosemont model 1054B%1-
99 controller.
The conductivity probe model 228-02-21-54-61 is item 248 in Figure 2. Once
calibrated for
the specific ion used in the system, the proportional control algorithms
adjust pumping rate
for the base used to form the salts.
CONCLUSION
Methods and apparatus for controlling emissions have been described. The
methods utilize hydrogen peroxide to reduce SOx and mercury (or other oxides-
of-metal)
emissions. Continuous concentration of hydrogen peroxide to levels approaching
or
exceeding propellant-grade hydrogen peroxide facilitates increased system
efficiency. By
utilizing methods and apparatus in accordance with the invention, combustion
flue gas
streams can be treated for the removal of SOx and oxides-of-metal, while
isolating useful by-
products streams of sulfuric acid and as well as solids for the recovery of
the heavy metals.
The methods and apparatus may also be extended to reduce NOx emissions. One of
the
significant advantages of the present invention is the fact that the process
can be run
continuously, with measuring and adjustments made in real time while the
process is being
performed. Computer monitoring can initiate flow changes of reagents in
response to
automatic measurements to maintain desired process conditions.
Although specific embodiments have been illustrated and described herein, it
will
be appreciated by those of ordinary skill in the art that any arrangement that
is calculated to
achieve the same purpose may be substituted for the specific embodiment shown.
This
application is intended to cover any adaptations or variations of the present
invention.
Therefore, it is manifestly intended that this invention be limited only by
the claims and the
equivalents thereof.

Representative Drawing

Sorry, the representative drawing for patent document number 2565750 was not found.

Administrative Status

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Event History

Description Date
Application Not Reinstated by Deadline 2012-04-10
Time Limit for Reversal Expired 2012-04-10
Deemed Abandoned - Failure to Respond to Maintenance Fee Notice 2011-04-08
Amendment Received - Voluntary Amendment 2010-06-16
Letter Sent 2010-03-24
All Requirements for Examination Determined Compliant 2010-03-09
Request for Examination Requirements Determined Compliant 2010-03-09
Request for Examination Received 2010-03-09
Letter Sent 2007-11-26
Letter Sent 2007-11-26
Inactive: Single transfer 2007-10-22
Inactive: Courtesy letter - Evidence 2007-01-16
Inactive: Cover page published 2007-01-15
Inactive: Notice - National entry - No RFE 2007-01-12
Application Received - PCT 2006-11-28
National Entry Requirements Determined Compliant 2006-11-03
Application Published (Open to Public Inspection) 2005-12-01

Abandonment History

Abandonment Date Reason Reinstatement Date
2011-04-08

Maintenance Fee

The last payment was received on 2010-03-18

Note : If the full payment has not been received on or before the date indicated, a further fee may be required which may be one of the following

  • the reinstatement fee;
  • the late payment fee; or
  • additional fee to reverse deemed expiry.

Patent fees are adjusted on the 1st of January every year. The amounts above are the current amounts if received by December 31 of the current year.
Please refer to the CIPO Patent Fees web page to see all current fee amounts.

Fee History

Fee Type Anniversary Year Due Date Paid Date
Basic national fee - standard 2006-11-03
MF (application, 2nd anniv.) - standard 02 2007-04-10 2007-03-26
Registration of a document 2007-10-22
MF (application, 3rd anniv.) - standard 03 2008-04-08 2008-03-26
MF (application, 4th anniv.) - standard 04 2009-04-08 2009-03-23
Request for examination - standard 2010-03-09
MF (application, 5th anniv.) - standard 05 2010-04-08 2010-03-18
Owners on Record

Note: Records showing the ownership history in alphabetical order.

Current Owners on Record
NATIONAL AERONAUTICS AND SPACE ADMINISTRATION
Past Owners on Record
CLYDE F. PARRISH
LANDY CHUNG
Past Owners that do not appear in the "Owners on Record" listing will appear in other documentation within the application.
Documents

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Document
Description 
Date
(yyyy-mm-dd) 
Number of pages   Size of Image (KB) 
Abstract 2006-11-02 1 62
Claims 2006-11-02 6 296
Description 2006-11-02 7 477
Drawings 2006-11-02 3 54
Reminder of maintenance fee due 2007-01-14 1 111
Notice of National Entry 2007-01-11 1 205
Courtesy - Certificate of registration (related document(s)) 2007-11-25 1 104
Courtesy - Certificate of registration (related document(s)) 2007-11-25 1 104
Reminder - Request for Examination 2009-12-08 1 117
Acknowledgement of Request for Examination 2010-03-23 1 179
Courtesy - Abandonment Letter (Maintenance Fee) 2011-06-02 1 172
PCT 2006-11-02 3 123
Correspondence 2007-01-11 1 29