Background of the Invention
Field of the Invention
[0001] The present invention is directed to a microbiologically stable corrosion inhibitor
and a method of preventing yellow metal corrosion in aqueous systems. The composition
and method provide superior corrosion performance. More particularly, the invention
provides a composition including 4-methylbenzotriazole (4-MBT) which is used as a
yellow metal corrosion inhibitor in aqueous systems.
Description of the Prior Art
[0002] Tolyltriazole has two isomers, 4-methylbenzotriazole (4-MBT) and 5-methylbenzotriazole
(5-MBT). Tolyltriazole, as the mixture of the two isomers, has traditionally been
one of the most effective corrosion inhibitors for copper and its alloys in a wide
variety of cooling water environments. A commercially available preparation of the
mixed tolyltriazole isomers is COBRATEC@ TT-100, available from PMC Specialties, Cincinnati,
Ohio. Mixed tolyltriazole isomer preparations used as corrosion inhibitors include
at least 60% by weight of the 5-MBT isomer. Generally, the tolyltriazole isomers are
added to cooling water to inhibit corrosion. The tolyltriazole isomers prevent corrosion
by adsorbing to metal surfaces to produce a protective surface film which inhibits
corrosion. It is believed that the surface film is a monolayer film.
[0003] The present invention advantageously provides a tolyltriazole composition which is
not biodegradable and, therefore, will provide a corrosion inhibitor which is easier
to dose, more economical and not wasted in systems which have microbiological contamination.
Unexpectedly, the novel composition and method of the present invention significantly
and unexpectedly provide excellent corrosion inhibition while being microbiologically
stable.
Summary of the Invention
[0004] One aspect of the invention provides a method of preventing the corrosion of the
yellow metal surfaces of a cooling system in contact with water. The method comprises
the step of adding to the water a tolyltriazole composition including at least 45
% by weight 4-methylbenzotriazole. Preferably, the 4-methylbenzotriazole is added
to the water in a final concentration of from about 0,01 to about 100 parts per million.
[0005] The 4-methylbenzotriazole is added to the water either intermittently or continuously.
Other known non-tolyltriazole corrosion inhibitors may also be added to the water.
[0006] According to another aspect the invention provides a microbiologically stable corrosion
inhibitor preferably for use of preventing the corrosion of cooling system surfaces
in contact with water, in particular water containing microorganisms, and especially
for use of preventing the corrosion of cooling system yellow metal surfaces in contact
with water, in particular water containing microorganisms, which corrosion inhibitor
comprises a tolyltriazole composition containing at least 45 % by weight of 4-methylbenzotriazole
and less than 55 % by weight of 5-methylbenzotriazole, optionally in admixture with
a non-tolyltriazole corrosion inhibitor.
[0007] According to preferred embodiments of the present invention the tolyltriazole composition
includes at least 60 % by weight, preferably at least 80 % by weight, and most preferably
at least 95 % by weight of 4-methylbenzotriazole, and less than 40 % by weight, preferably
less than 20 % by weight, and most preferably less than 5 % by weight of 5-methylbenzotriazole.
Brief Description of the Drawings
[0008]
FIG. 1 graphically represents the biodegradation of 5-MBT after tolyltrizoles spike.
FIG. 2 graphically represents bacterial populations as a function of dosage of 5-MBT,
4-MBT and distilled water.
FIG. 3 graphically represents the data obtained from a respirometry experiment demonstrating
the aerobic biodegradation of 5-MBT.
Description of the Preferred Embodiments
[0009] The present invention provides a composition and a method of preventing the corrosion
of cooling system yellow metal surfaces in contact with water. Although the invention
is not limited to any particular source of water, preferably, cooling water systems,
such as cooling water towers, once-through cooling systems, cooling lake or pond systems,
and spray ponds, are treated by the method and compositions of the invention. These
cooling water systems are described in detail in the Nalco Water Handbook, 2nd ed.,
Ch. 34 (1988). The term yellow metal is intended to include copper, bronze, and copper
alloys.
[0010] According to the method of the invention, an amount of a tolyltriazole composition
sufficient to prevent the corrosion of the yellow metal surfaces in contact with cooling
water is added to the water. According to one embodiment of the invention, the tolyltriazole
composition of the invention includes at least 45% by weight of the 4-methylbenzotriazole
(4-MBT) isomer of tolyltriazole. As will be described below in more detail, the present
inventor has discovered that the 4-MBT isomer of tolyltriazole is biologically stable
whereas the 5-methylbenzotriazole (4-MBT) isomer is not. The 4-MBT is stable in cooling
water including naturally occurring or added micro-organisms. Thus, with the present
invention, since 4-MBT is not biodegraded, the level of corrosion inhibition is maintained
in the presence of microbiological contamination. More preferably, the tolyltriazole
compositions of the invention include at least 60%, and more preferably, 80% by weight
of the 4-MBT isomer. Most preferably, the tolyltriazole composition of the invention
includes from about 90 to about 99% by weight of the 4-MBT isomer.
[0011] According to one preferred embodiment of the invention, a tolyltriazole composition
consisting essentially of the 4-MBT isomer is added to an industrial or commercial
cooling system in an electric utility to prevent yellow metal corrosion. The 4-MBT
isomer is preferably added in a dosage of from 0.01 to about 100 parts per million
(ppm). More preferably, the 4-MBT is added to the cooling water in a final concentration
of from 0.1 to about 20 ppm. The dosage of 4-MBT in the cooling water will depend
on how corrosive the cooling water is, and on whether the yellow metal surfaces of
the cooling water tower have been previously treated with corrosion inhibitors. In
one embodiment of the invention, 4-MBT is added to the cooling water continuously
at a controlled rate to maintain a concentration of from 0.01 - 100 ppm. Since 4-MBT
is biostable, 4-MBT is preferably added intermittently to achieve a concentration
of 4-MBT in the water from 0.05 to about 20 ppm. The cooling water may also contain
non-tolyltriazole corrosion inhibitors, such as biocides, phosphates, benzotriazole,
napthatriazole, molybdates, and polymer treatment programs. These other non-tolyltriazole
corrosion inhibitors may be added with the 4-MBT or separately.
[0012] As shown in the Examples below, surprisingly and unexpectedly, 5-MBT is biodegraded;
however, 4-MBT is not effected. Thus, over time 4-MBT adsorbs to yellow metal surfaces
more effectively. Thus, treatment with 4-MBT provides a better protective film over
yellow metal surfaces; and therefore, provides a superior protective barrier against
the corrosive cooling water. Furthermore, since 4-MBT is not biodegraded, the task
of maintaining a constant protective concentration of 4-MBT in the cooling water is
significantly simplified. Also, chemical is not wasted through biodegradation. Thus,
the treatment of the invention is more economical to the operator.
[0013] The Examples below further show that unadsorbed 4-MBT is not biodegraded by microbes
in a cooling tower or other cooling system. Therefore, the 4-MBT which is not biodegraded
remains in the cooling water and continues to prevent corrosion. The present invention
prevents the loss of chemical seen using the mixed isomer preparations currently being
used while providing superior protection against corrosion. Furthermore, the use of
the present invention provides a constant concentration of corrosion inhibition in
the water. Thus, cooling system operators are better able to control corrosion.
[0014] The following examples are presented to describe preferred embodiments and utilities
of the invention and are not meant to limit the invention unless otherwise stated
in the claims appended hereto.
Example 1
[0015] Three copper electrodes were polished with 600 grit sanding paper (Buehler) and rinsed
with water. These electrodes were immersed in three separate Greene cells containing
four cycles Chicago Tap Water (360 Ca, 200 Mg, and 440 "M" alkalinity, all as CaC0
3). After a half hour immersion period, the initial corrosion rate was obtained using
electrochemical measurements (Linear Polarization Resistance). One of the Greene cells
was then spiked with 2 ppm of 5-MBT. The second cell was spiked with 2 ppm of 4-MBT.
The third cell was left as is. After an 18 hour immersion period, the corrosion rates
were measured again. It was found that the corrosion rate of copper in the flask spiked
with 5-MBT had decreased from an initial value of 0.36 mpy to 0.0033 mpy (a 100 fold
decrease). Similarly, for the 4-MBT spiked sample, the corrosion rate had decreased
from 0.4779 to 0.0089. For the flask left as is, the corrosion rate had decreased
from an initial value of 0.46 mpy to 0.2 mpy (only a 2-fold decrease). This example
illustrates that both 5-MBT and 4-MBT are very effective yellow metal corrosion inhibitors.
Example 2
[0016] A field sample of discharge from a utility treated with a mixed tolyltriazole preparation
was analyzed for 4- and 5-MBT using HPLC and found to contain only 4-MBT. This sample
was spiked with 2 ppm of a mixed isomer tolyltriazole (TT) preparation (1.16 ppm 5-MBT
and 0.84 ppm 4-MBT). It was found that the 5-MBT levels had not changed in about ten
hours. When measured at the end of 40 hours, 5-MBT had completely disappeared (Figure
1). 4-MBT levels, on the other hand, remained constant throughout the experiment.
This type of extremely selective degradation (5-MBT vs. 4-MBT) following an initial
acclimation period, is very typical of microbiological processes. Addition of sulfuric
acid (up to 15%), in order to lyse any bacteria, did not result in recovery of 5-MBT
ruling out processes such as adsorption by cell walls.
[0017] This example illustrates that 4-MBT is resistant to microbiological degradation in
a cooling water environment, whereas 5-MBT is not.
Example 3
[0018] A field sample from a utility was analyzed for TT by HPLC and found to contain only
4-MBT. The sample was split into eight fractions. One fraction was left as is and
spiked with 2 ppm TT. The other seven fractions were subjected to one of the following
processes and then spiked with TT:

[0019] Additionally, the eighth sample was spiked with 2 ppm TT and chilled in a refrigerator
at 4
° C. It was found that in the field sample with no treatment, 5-MBT disappeared in approximately
2 days. In samples 2 through 8, 5-MBT was stable for up to one month (analysis was
not performed after this time). Since all the treatments listed in sample nos. 2 through
8 either have bactericidal effect or inhibit bacterial metabolism, preservation of
5-MBT in these samples seems to point to a microbiological mode of degradation When
sample no. 8 (chilled sample) was kept at room temperature, the 5-MBT disappeared
in about two days.
[0020] This example provides evidence of microbiological mechanism of degradation of 5-MBT.
Example 4
[0021] The field water sample from Example 2 was split into four portions. The first portion
was contained in a brown glass bottle and completely covered in aluminum foil. The
second portion was contained in a transparent volumetric flask. The third portion
was contained in a plastic bottle, and the fourth container was contained in a plastic
bottle and covered with aluminum foil. All of the samples were spiked with 2 ppm of
TT from Example 2. After two days, the samples were assayed for TT using HPLC. It
was found that the 5-MBT isomer had disappeared in all of them However, 4-MBT concentrations
did not change. This example illustrates that disappearance of the 5-MBT isomer is
not due to a container effect (e.g. adsorption on plastic, etc.) or a photochemical
phenomenon.
Example 5
[0022] A Pilot Cooling Tower water sample known to degrade 5-MBT was split into three parts.
To the first portion, 5-MBT was repeatedly spiked (each time waiting for the previous
spike to disappear). A cumulative concentration of 1050 ppm was spiked to this portion.
Whenever 5-MBT was spiked to the first portion, the same concentration of 4-MBT was
spiked to the second portion and distilled water was spiked to the third portion.
Samples were withdrawn at various intervals and assayed for total aerobic counts and
for 4- or 5-MBT using HPLC. The results showed that 5-MBT concentrations in the first
portion decreased to zero following each spike of 5-MBT. However, 4-MBT concentrations
in the second portion steadily increased, consistent with amount of 4-MBT spiked to
the sample. Figure 2 depicts total aerobic bacterial counts as a function of cumulative
dosage of 4-MBT, 5-MBT and distilled water. It can be clearly seen that addition of
5-MBT to the first flask and its subsequent degradation results in a significant increase
in total cell counts. No such increase was found for the 4-MBT isomer and the control
sample.
[0023] At the end of the experiment, 1.9 ml of the first portion was spiked into a Greene
cell containing a copper electrode immersed in 1000 ml of standard No. 13 Chicago
Tap Water. This would result in 2 ppm of 5-MBT based on a cumulative spike of 1050
ppm. Similarly, 1.9 ml of the second and third portion was spiked into separate Greene
cells containing copper electrodes immersed in standard No. 13 Chicago Tap Water.
Electrochemical corrosion measurements (Linear Polarization Resistance) showed that
the corrosion rate of 4-MBT spiked sample had decreased roughly hundred fold to less
than 0.005 mpy in 20 hours. The 5-MBT spiked sample and the sample spiked with distilled
water, on the other hand, showed only a two-fold decrease.
[0024] This example illustrates that 5-MBT is aerobically degraded in the presence of certain
bacteria. This degradation is irreversible, and the degradation product is not a yellow
metal corrosion inhibitor. 4-MBT is completely stable in the presence of bacteria
and is, therefore, preferred for yellow metal corrosion inhibition over 5-MBT in such
situations.
Example 6
[0025] Three liters of a solution containing 1 ml/L of heavy metals, 1 g/L of NH
4CI, 0.5 g/L potassium phosphate (dibasic salt) and 0.1 g/L MgS0
4 was prepared and the pH adjusted to 7.0 with H
3PO4.. The solution was then split into three parts. To the first part, 50 ppm of 5-MBT
was spiked. To the second part, 50 ppm of 4-MBT was spiked. To the third part, distilled
water was spiked. To each of the parts, 8 ml of an inoculum containing bacteria acclimated
with 5-MBT (from 5-MBT spiked sample in Example 5) was added. The three solutions
were then transferred to respirometry bottles and the oxygen consumption by the bacteria
in the bottles was measured as a function of time. It was found that the 5-MBT spiked
samples showed a significantly higher oxygen consumption (55 ppm per 50 ppm of 5-MBT)
than 4-MBT and the distilled water spiked samples. The 5-MBT spiked sample was repeatedly
spiked with 100, 150, 200 and 250 ppm of 5-MBT, each time waiting for the oxygen consumption
from the previous spike to level off. The results are shown in Figure 3.
[0026] This example illustrates that 5-MBT is aerobically degraded by certain bacteria,
whereas 4-MBT is not.
[0027] Changes can be made in the composition, operation and arrangement of the method of
the present invention described herein without departing from the concept and scope
of the invention as defined in the following claims:
1. A method of preventing the corrosion of cooling system yellow metal surfaces in
contact with water, the method comprising the step of adding to the water a mixed
isomer tolyltriazole composition including at least 45% by weight of 4-methylbenzotriazole
[and less than 55% by weight 5-methylbenzotriazole].
2. The method of Claim 1, wherein the tolyltriazole composition is added to the water
in a final concentration of from 0.01 to about 100 parts per million of 4-methylbenzotriazole.
3. The method of Claim 1 or 2, wherein the tolyltriazole composition is added to the
water intermittently.
4. The method of Claim 1 or 2, wherein the tolyltriazole composition is added to the
water continuously.
5. The method of any of Claims 1-4, wherein the tolyltriazole composition is added
to the water in a final concentration of from about 0.1 to about 20 parts per million
of 4-methylbenzotriazole.
6. The method of any of Claims 1-5, wherein the method includes a further step of
adding a non-tolyltriazole corrosion inhibitor to the water.
7. A method of preventing the corrosion of yellow metal surfaces of a cooling water
tower in contact with water which contains microorganisms, the method comprising the
steps of adding to the water a mixed isomer tolyltriazole composition which includes
at least 60% by weight of 4-methylbenzotriazole [and less than 40% by weight 5-methylbenzo-triazole].
8. The method of Claim 7 wherein the mixed isomer tolyltriazole composition includes
at least 80% by weight of 4-methylbenzotriazole [and less than 20% by weight 5-methylbenzotriazole].
9. The method of Claim 7 or 8, wherein the mixed isomer tolyltriazole composition
includes at least 90% by weight of 4-methylbenzotriazole [and less than 10% by weight
5-methylbenzotriazole].
10. The method of any of Claims 7-9 wherein the mixed isomer tolyltriazole composition
includes at least 95% by weight of 4-methylbenzotriazole [and less than 5% by weight
5-methylbenzotriazole].
11. The method of any of Claims 7-10, wherein the mixed isomer tolyltriazole composition
is added to the water in a final concentration of from 0.01 to about 100 ppm of 4-methylbenzotriazole.
12. A method of preventing the corrosion of yellow metal surfaces in contact with
water in a cooling water tower which contains microorganisms, the method comprising
the steps of adding to the water a mixed isomer tolyltriazole composition which includes
at least 95% by weight of 4-methylbenzotriazole [and less than 5% by weight 5-methylbenzotriazole];
and adding to the water a non-tolyltriazole corrosion inhibitor.
13. A microbiologically stable corrosion inhibitor comprising a tolyltriazole composition
which contains at least 45 % by weight of 4-methylbenzotriazole, optionally in admixture
with a non-tolyltriazole corrosion inhibitor.
14. The corrosion inhibitor of Claim 13, wherein the tolyltriazole composition includes
at least 45 % by weight of 4-methylbenzotriazole and less than 55 % by weight of 5-methylbenzotriazole.
15. The corrosion inhibitor of Claim 13 or 14, wherein the tolyltriazole composition
includes at least 60 % by weight, preferably at least 80 % by weight of 4-methylbenzotriazole,
and less than 40 % by weight, preferably less than 20 % by weight of 5-methylbenzotriazole.
16. The corrosion inhibitor of any of Claim 13 to 15, wherein the tolyltriazole composition
includes at least 90 % by weight, preferably at least 95 % by weight of 4-methylbenzotriazole,
and less than 10 % by weight, preferably less than 5 % by weight of 5-methylbenzotriazole.
17. The corrosion inhibitor of any of Claims 13 to 16 for use of preventing the corrosion
of cooling system surfaces in contact with water, in particular water containing microorganisms.
18. The corrosion inhibitor of any of Claims 13 to 17 for use of preventing the corrosion
of cooling system yellow metal surfaces in contact with water, in particular water
containing microorganisms.