Language selection

Search

Patent 1229780 Summary

Third-party information liability

Some of the information on this Web page has been provided by external sources. The Government of Canada is not responsible for the accuracy, reliability or currency of the information supplied by external sources. Users wishing to rely upon this information should consult directly with the source of the information. Content provided by external sources is not subject to official languages, privacy and accessibility requirements.

Claims and Abstract availability

Any discrepancies in the text and image of the Claims and Abstract are due to differing posting times. Text of the Claims and Abstract are posted:

  • At the time the application is open to public inspection;
  • At the time of issue of the patent (grant).
(12) Patent: (11) CA 1229780
(21) Application Number: 1229780
(54) English Title: IRON REMOVAL FROM EDTA SOLUTIONS
(54) French Title: ELIMINATION DU FER DANS DES SOLUTIONS D'EDTA
Status: Term Expired - Post Grant
Bibliographic Data
(51) International Patent Classification (IPC):
  • C23G 01/36 (2006.01)
  • G21F 09/00 (2006.01)
(72) Inventors :
  • WEISBERG, SHARON L. (United States of America)
  • MURRAY, ALEXANDER P. (United States of America)
  • BECKER, LAWRENCE F., JR. (United States of America)
(73) Owners :
  • WESTINGHOUSE ELECTRIC CORPORATION
(71) Applicants :
  • WESTINGHOUSE ELECTRIC CORPORATION (United States of America)
(74) Agent: OLDHAM AND COMPANYOLDHAM AND COMPANY,
(74) Associate agent:
(45) Issued: 1987-12-01
(22) Filed Date: 1984-06-28
Availability of licence: N/A
Dedicated to the Public: N/A
(25) Language of filing: English

Patent Cooperation Treaty (PCT): No

(30) Application Priority Data:
Application No. Country/Territory Date
513,567 (United States of America) 1983-07-14

Abstracts

English Abstract


ABSTRACT OF THE DISCLOSURE
Disclosed is a method of removing transition
metals from a decontamination solution containing a com-
plexing agent having an equilibrium constant for the
ferric ion complex formation reaction of greater than
1022, such as ethylenediaminetetraacetic acid. An anion
exchange resin is loaded with the complexing agent or one
of its salts, and the solution is passed through the anion
exchange resin. The process is applied to decontamination
solutions which are used to clean cooling systems of
nuclear reactors.


Claims

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


CLAIMS:
1. A method of removing ferric ion from a solution
containing a complexing agent selected from the group consisting
of ethylenediaminetetraacetic acid, trans, 1,2-diaminocyclohex-
anetetraacetic acid, oxybis (ethylenediaminetetraacetic acid),
and mixtures thereof, comprising loading an anion exchange resin
with said complexing agent or a salt thereof and circulating
said solution through said anion exchange resin.
2. A method according to Claim 1 wherein said com-
plexing agent is ethylenediaminetetraacetic acid.
3. A method according to Claim 2 wherein said anion
exchange resin is loaded with an alkali metal salt of ethylene-
diaminetetraacetic acid.
4. A method according to Claim 1 wherein said anion
exchange resin is loaded by passing a solution of said salt
through said resin until the pH of said solution as it leaves
said resin is less than 6.
5. A method according to Claim 1 wherein the temper-
ature of said decontamination solution is maintained at about
40 to about 100°C.
6. A method according to Claim 1 wherein said de-
contamination solution also contains citric acid and oxalic
acid.
7. In a method of decontaminating a steam generator
of a pressurized water nuclear reactor wherein a decontamination
solution containing ethylenediaminetetraacetic acid is circu-
lated through said generator to solubilize ferric ion in deposits
therein by forming a complex therewith, an improved method of

removing said ferric ion from said decontamination solution
and of regenerating said ethylenediaminetetraacetic acid in
said solution, comprising circulating said decontamination
solution through an anion exchange resin loaded with the anion
of ethylenediaminetetraacetic acid.
8. A method according to Claim 7 wherein said anion
exchange resin is loaded by treating a basic anion exchange
resin in hydroxyl form with an alkali metal salt of ethylene-
diaminetetraacetic acid.
9. A method according to Claim 8 wherein said anion
exchange resin is loaded by passing a solution of said salt
through said basic anion exchange resin until the pH of said
solution as it leaves said resin falls below 6.
10. A method according to Claim 7 wherein said
decontamination solution is circulated between said generator
and said anion exchange resin until the concentration of said
metals in said solution as it leaves said generator is not
substantially greater than the concentration of said metals
in said solution as it enters said generator.
11. A method according to Claim 7 wherein the
temperature of said decontamination solution is maintained
at about 40 to about 100°C.
12. A method according to Claim 7 wherein said
decontamination solution also contains citric acid and
oxalic acid.
13. A method according to Claim 1 wherein said anion
exchange resin is loaded with a salt of said complexing agent.
14. A method according to Claim 7 wherein said anion
exchange resin is loaded with an alkali metal salt of ethylene-
diaminetetraacetic acid.

Description

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


~ ~29 ~
1 51,129
IRON REMOVAL FROM ~DTA SOLIJTIONS
BACKGROUND OF THE INVENTION
Deposits that contain radioactive elements often
form in the cooling systems of nuclear reactors. In order
- to safely maintain and repair the cooling system, it is
necessary to remove these radioactive deposits. This can be
accomplished, for example, by using an oxidizing solution of
alkali permanganate followed by a decontamination solution
of oxalic acid, citric acid, and ethylenediaminetetraacetic
acid (EDTA). The ~DTA forms a complex with the radioactive
metal ions in the deposits, which solubilizes them. The
decontamination solution is circulated between the cooling
system and a cation exchange resin which exchanges the metal
ions on the resin and frees the EDTA to solubilize
additional metal ions.
s

1.~2~ 7~
2 51,129
~ major difficulty with this process, however,
is that EDTA does not readily yield up metal ions, par-
ticularly the ferric ion, to the cation exchanye resin.
Thus, the concentration of the metal ion-EDTA complex
builds up in the decontamination solution until it is no
longer effective in solubilizing the metal ions in the
deposits. When this happens, it is necessary to add fresh
EDTA to the solution. This means that the solution must
be constantly monitored to determine if the EDTA has been
depleted so that more can be added. Also, great care must
be taken not to add excess EDTA since EDTA is not very
soluble unless it has fcrmc~ a complex with metal ions,
and precipitated EDTA can itself be difficult to remove
from the cooling system. Moreover, if excess EDTA is
added, not only is the reagent wasted, but the additional
EDTA must be removed from the solutisn at a later stage
which adds to the volume of radioactive waste.
SUMMARY OF THE INVENTION
We have discovered a process for removing tran-
-ition metal ions from a decontamination solution contain-
ing EDTA while regenerating the EDTA. Unlike the prior
process which used a cation exchange resin, our process
uses an anion exchange resin. The anion exchange resin is
preloaded with EDTA anion so that the entire metal ion-EDTA
complex deposits on the ion exchange resin, releasing
fresh EDTA from the anion exchange resin into the solution.
Thus, the concentration of uncomplexed EDTA in the solution
remains fairly constant and it is not necessary to monitor
the solution for the EDTA concentration or to add fresh
EDTA.
DESCRIPTION OF THE INVENTION
The process of this invention can be applied to
any solution containing a complex of a transition metal
with a complexing agent having an equilibrium constant for
the ferric ion complex formation reaction of greater than
1022. Examples of such complexing agents include ethylene-
diaminetetraacetic acid, trans, 1, 2-diaminocyclohexane-

9`-7~30
3 51,129
tetraacetic acid (DCTA), and oxybis (ethylenediaminetetra-
acetic acid) (EEDTA). Common transition metals found in
nuclear reactor decontamination solutions include iron,
cobalt, nickel, and chromium. The temperature of the solution
should be at least about 40C in order to keep the EDTA in
solution and prevent it from precipitating. The temperature
of the solution should be below about 100C, however, as anion
exchange resins and the reagents used in the solution may de-
compose above that temperature. The pH of the solution is not
critical but it is typically about 2 to about 2 1/2 for most
decontamination solutions due to the acidity of reagents which
are present.
In the first step of the process of this invention,
an anion exchange resin is loaded with EDTA, DCTA, or EEDTA.
Any anion exchange resin is suitable and may be used in this
invention. The resin should be loaded with only EDTA, DCTA, or
EEDTA and not with any other complexing agents because as the
metal EDTA, DCTA, or EEDTA complex is absorbed by the resin,
another anion (i.e., NTA, citric, or oxalic) would be released,
diluting the concentration of EDTA, DTCA, or EEDTA in the solu-
tion. Other complexing agents, such as NTA, or organic acids,
such as citric acid and oxalic acid form much weaker transition
metal complexes compared to those formed with EDTA, DTCA, or
EEDTA and metals complexed with these other agents can be removed
from solution by cation exchanges. This is not the case for
EDTA, DCTA, or EEDTA metal complexes, and as a result, the metal
remains in solution using conventional removal methods.
The anion exchange resin is most conveniently loaded
with the EDTA, DCTA, or EETA anion by preparing a solution of
the EDTA, DCTA, or EEDTA and passing the solution tnrough the
anion exchange resin. It is preferable to use a solution of an
EDTA, DCTA, or EEDTA salt, preferably an alkali metal salt, such
as sodium EDTA, DCTA, or EEDTA to load the anion exchange resin
with the EDTA, DCTA, or EEDTA anion, or this releases sodium
hydroxide rather than just water into the solution. Since NaOH
is highly alkaline, (pH~12-14) the pH of the solution exiting
the colurnn, after an initial rise, will fall back down to the
pH of

1212~
4 51,129
the sodium EDTA, DCTA, or EEDTA (pH~4-5) as fewer hydroxide
groups of the preferred strong base anion exchange resin are
replaced by the EDTA, DCTA, or EEDTA anion. Thus, by monitoring
the pH of the solution leaving the resin, one can then determine
when the resin has been fully loaded. After the pH falls to
below abou-t 6, the resin should be considered to be fully loaded
with EDTA, DCTA, or EEDTA anion. While the acid form of EDTA,
DCTA, or EEDTA can be used, it is more difficult to determine
when the resin has been loaded because, without the presence of
the sodium ion, the solution leaving the columns will be at
approximately a neutral pH value (~7). Thus, the difference in
pH values of the column feed (about 4.5) and the column effluent
(about 7) is significantly less than when the sodium salt is
used. Also, the acid form of EDTA, D~TA, or EEDTA is not very
soluble in water, which means that the solution must be more
dilute.
In the next step of the precess of this invention,
the decontamination solution containing the metal ion-EDTA, DCTA,
or EEDTA complex is circulated between the EDTA, DCTA, or EEDTA
loaded anion exchange resin and the reactor cooling system, or
the portion thereof that is being decontaminated, such as the
steam generator of a pressurized water reactor or a boiling
water reactor. As the metal ion-EDTA, DCTA, or EEDTA complex
is absorbed onto the EDTA, DCTA, or EEDTA anion exchange resin,
fresh EDTA, DCTA, or EEDTA is released into the contamination
solution. The solution is circulated until the concentration of
metal ions in the solution leaving the cooling system is not
substantially greater than the concentration of metal ions in
the solution entering the cooling system.
After the metal ion-EDTA, DCTA, or EEDTA complex has
been removed, the EDTA and any remaining ions in the solution
can be removed by passing the solution through a fresh anion
exchange resin or a mixed anion-cation exchange resin, which
results in relatively pure water. When the preloaded anion
exchange resin has been saturated with -the metal ion-EDTA, DCTA,
or EEDTA complex, it is disposed of as radioactive waste.

~p~
51,129
The following examples further illustrate this
invention.
, !EXAMPLE
e f ~
A 1 inch ~m~~glass column 18 inches long was
partially filled with 100 ml of an anion exchange resin
sold by Rohm and Haas under the trade designation "IRA-
400," a strong-based polystyrene resin having a particle
size between 16 and 50 mesh. A solution was prepared of
100 grams/liter of the di~odium salt of EDTA. The solu-
tion, which had a pH of 4.38, was fed through the top ofthe column at 1-3 bed volumes/hr. and the pH of the solu-
tion leaving the bottom of the column was measured. The
following table gives the pH of the solution leaving the
column after various bed volumes of the solution had
flowed through the column.
BED VOL~ME pH
0.5 11.85
1.0 12.86
1.5 12.94
2.0 12.36
2.5 6.56
3.0 5.90
3.5 5.64
4.0 5.47
4.5 5.29
5.0* 5.15
6.0 5.07
*A new solution was prepared having a pH of 4.49.
The above table shows that, after an initial
start-up time, the pH of the solution leaving the resin
fell to close to the pH of the solution entering the
resin. This indicated that the column was almost satur-
ated with EDTA.

6 51,129
XAMPLE 2
Simulated spent decontamination solutions were
prepared by dissolving 50, lO0, and 200 ppm of iron (from
magnetite, Fe304) in three 0.5 weight percent solutions of
a commercially available decontamination agent believed to
be 30% citric acid, 30% oxalic acid, 40% EDTA, and contain-
ing an inhibitor believed to be thiourea. The three
solutions were mixed in beakers with the preloaded anion
exchange resin prepared in Example 1 at 54C. After 5
hours the solutions were tested and were found to contain
3, 11, and 46 ppm of iron, respectively. This established
that the EDTA-loaded anio.. exchange resin successfully
removed iron from the solutions.
EXAMPLE 3
A 100-ml sample of the EDTA-loaded anion exchange
resin prepared as in Example 1 was placed in a 1 inch
glass column 18 inches long. A 0.5% solution of the
commercially available decontamination agent (described in
Example 2) which contained 80 ppm of iron was passed
through the column at 12 bed volumes/hr. from top to
bottomJand the iron, oxalate, citrate, and EDTA concentra-
tions in the solution leaving the column were measured.
The following table gives their concentrations.

3~
7 51,129
IRON OXALATE CITRATE EDTA
~ED VOLUME ~ppm) (mg/ml) ~ mi) (ppm,
Feed 80 1080 1000 1384
10 to 11 39 10 290 4100
5 20 to 21 35 - 10 760 4366
40 to 41 37 10 1370 3352
60 to 61 14 78 1340 2521
83
80 to 81 8.8 430 1130 1783
430
90 to 91 3.8 500 910 984
100 to 101 1.0 830 970 1332
The above table shows that, after an initial
start-up period, the EDTA-loaded column successfully
removed iron in the solution to levels below lO ppm.

Representative Drawing

Sorry, the representative drawing for patent document number 1229780 was not found.

Administrative Status

2024-08-01:As part of the Next Generation Patents (NGP) transition, the Canadian Patents Database (CPD) now contains a more detailed Event History, which replicates the Event Log of our new back-office solution.

Please note that "Inactive:" events refers to events no longer in use in our new back-office solution.

For a clearer understanding of the status of the application/patent presented on this page, the site Disclaimer , as well as the definitions for Patent , Event History , Maintenance Fee  and Payment History  should be consulted.

Event History

Description Date
Inactive: IPC from MCD 2006-03-11
Inactive: Expired (old Act Patent) latest possible expiry date 2004-12-01
Grant by Issuance 1987-12-01

Abandonment History

There is no abandonment history.

Owners on Record

Note: Records showing the ownership history in alphabetical order.

Current Owners on Record
WESTINGHOUSE ELECTRIC CORPORATION
Past Owners on Record
ALEXANDER P. MURRAY
LAWRENCE F., JR. BECKER
SHARON L. WEISBERG
Past Owners that do not appear in the "Owners on Record" listing will appear in other documentation within the application.
Documents

To view selected files, please enter reCAPTCHA code :



To view images, click a link in the Document Description column (Temporarily unavailable). To download the documents, select one or more checkboxes in the first column and then click the "Download Selected in PDF format (Zip Archive)" or the "Download Selected as Single PDF" button.

List of published and non-published patent-specific documents on the CPD .

If you have any difficulty accessing content, you can call the Client Service Centre at 1-866-997-1936 or send them an e-mail at CIPO Client Service Centre.

({010=All Documents, 020=As Filed, 030=As Open to Public Inspection, 040=At Issuance, 050=Examination, 060=Incoming Correspondence, 070=Miscellaneous, 080=Outgoing Correspondence, 090=Payment})


Document
Description 
Date
(yyyy-mm-dd) 
Number of pages   Size of Image (KB) 
Claims 1993-09-10 2 63
Abstract 1993-09-10 1 13
Drawings 1993-09-10 1 7
Descriptions 1993-09-10 7 209