# Patent

## Title
Water treatment method

## Abstract

A method for treating water in a closed cooling system, having a pH of at least 7 and a temperature of at least 25° C., by adding a composition comprising 2-methyl-4-isothiazolin-3-one; wherein the composition is substantially free of non-aqueous solvents, volatile organic compounds and halogenated biocides; and wherein 2-methyl-4-isothiazolin-3-one is present in an amount sufficient to produce in the water a 2-methyl-4-isothiazolin-3-one concentration from 15 ppm to 500 ppm.

## Background
This application claims the benefit of priority under 35 U.S.C. §119(e) of U.S. Provisional Patent Application No. 60/801,554 filed on May 18, 2006 and U.S. Provisional Application Ser. No. 60/790,439 filed on Apr. 7, 2006.


This invention relates to a method for treating water in a closed cooling water system with a biocide composition.
One of the known uses of isothiazolone biocides is treatment of water cooling systems, as disclosed in U.S. Pat. No. 3,761,488. However, the isothiazolone biocide most frequently used in commercial water cooling systems is a 3:1 mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one, respectively. This mixture has several disadvantages, including the relative instability of 5-chloro-2-methyl-4-isothiazolin-3-one at high pH and high temperatures. Other biocide formulations used in cooling water systems are disadvantageous for the same reason, and also due to the presence of non-aqueous solvents, salts and volatile organic compounds in the biocide formulation.
The problem addressed by this invention is to provide a method of treating water in a closed cooling system that does not suffer from the disadvantages discussed above.
STATEMENT OF THE INVENTION
The present invention is directed to a method for treating water in a closed cooling system, having a pH of at least 7 and a temperature of at least 25° C., by adding a composition comprising 2-methyl-4-isothiazolin-3-one; wherein the composition is substantially free of non-aqueous solvents, volatile organic compounds and halogenated biocides; and wherein 2-methyl-4-isothiazolin-3-one is present in an amount sufficient to produce in the water a 2-methyl-4-isothiazolin-3-one concentration from 15 ppm to 500 ppm.
The present invention is further directed to a method for control of mycobacteria (gram positive, acid-fast bacteria) in an in-use metalworking fluid system by adding 2-methyl-4-isothiazolin-3-one.


DETAILED DESCRIPTION OF THE INVENTION
“MI” or “MIT” is 2-methyl-4-isothiazolin-3-one, also referred to by the name 2-methyl-3-isothiazolone. “CMI” or “CMIT” is 5-chloro-2-methyl-4-isothiazolin-3-one, also referred to by the name 5-chloro-2-methyl-3-isothiazolone.
As used herein, the following terms have the designated definitions, unless the context clearly indicates otherwise. The term “microbicide” refers to a compound capable of inhibiting the growth of or controlling the growth of microorganisms at a locus; microbicides include bactericides, fungicides and algicides. The term “microorganism” includes, for example, fungi (such as yeast and mold), bacteria and algae. The term “locus” refers to an industrial system or product subject to contamination by microorganisms. The term “closed cooling system” refers to a system containing water used for industrial cooling applications which is not open to evaporation and in which the water loss is less than 5% of the recirculation rate. The following abbreviations are used throughout the specification: ppm=parts per million by weight (weight/weight), mL=milliliter, AI=active ingredient, i.e., total amount of isothiazolones. Unless otherwise specified, temperatures are in degrees centigrade (° C.), and references to percentages are by weight.
The composition used in the present invention preferably contains from 20% to 95% water, and from 5% to 80% MI, but is substantially free of non-aqueous solvents, i.e., it contains less than 2% of such solvents, alternatively less than 1%, alternatively less than 0.5%, alternatively less than 0.1%. The composition is substantially free of volatile organic compounds, as defined by EPA regulations, i.e., it contains less than 2% of such compounds, alternatively less than 1%, alternatively less than 0.5%, alternatively less than 0.1%. The composition is substantially free of halogenated biocides, i.e., it contains less than 0.5% of such biocides, alternatively less than 0.1%, alternatively less than 100 ppm, alternatively less than 50 ppm. Halogenated biocides include, e.g., CMI, which is often present together with MI in commercial biocides; 2-bromo-2-nitro-1-propane-1,3-diol (BNPD); and 2,2-dibromo-3-nitrilopropionamide (DBNPA). In one embodiment of the invention, the composition is substantially free of all biocides other than MI. In one embodiment, the composition is substantially free of metals, i.e., it contains less than 0.4% of metal ions, alternatively less than 0.2%, alternatively less than 0.1%. In one embodiment of the invention, when the composition is described as being substantially free of certain ingredients, the cooling water is substantially free of these ingredients, i.e., they are not added separately to the cooling water.
The composition may be used with corrosion inhibitors including, e.g., nitrites, chromates, molybdates, phosphates, zinc salts, azoles and phosphonates, which may be added separately to the cooling water. The metals present in corrosion inhibitors may be present in the cooling water in amounts that exceed those produced by any trace metals in the composition of this invention.
The composition may also be used with scale inhibitors, including, e.g., polycarboxylic acids, such as polyacrylic acids, polymaleic acids, and polyaspartic acids, or phosphates or phosphonates. Scale inhibitors may be added separately to the cooling water at use levels of less than 1 ppm, less than 10 ppm, or less than 100 ppm. Metals present in scale inhibitors may also exceed the amounts provided by the composition of this invention.
In one embodiment of the invention, the MI concentration in the cooling water is at least 20 ppm, alternatively at least 25 ppm, alternatively at least 30 ppm, alternatively at least 40 ppm, alternatively at least 50 ppm, alternatively at least 60 ppm; preferably the MI concentration is no more than 300 ppm, alternatively no more than 250 ppm, alternatively no more than 200 ppm, alternatively no more than 150 ppm, alternatively no more than 125 ppm.
In one embodiment of the invention, the pH of the cooling water is at least 7.5, alternatively at least 8, alternatively at least 8.5, alternatively at least 9; preferably the pH is no greater than 12, alternatively no greater than 11.5, alternatively no greater than 11, alternatively no greater than 10.5. In one embodiment, the cooling water temperature is at least 30° C., alternatively at least 35° C., alternatively at least 40° C.; preferably the cooling water temperature is no greater than 70° C., alternatively no greater than 60° C.
The present invention is further directed to a method for controlling the growth of mycobacteria, especially M. immunogenum, associated with hypersensitivity pneumonitis (HP) in metalworking fluids using MIT biocide as a single-pack treatment, which has low odor, does not release or contain formaldehyde, does not contain metal salts (especially copper), and which is highly stable in alkaline metalworking fluids (pH>7). The biocide is substantially free of halogenated biocides, i.e., it contains less than 0.5% of such biocides, alternatively less than 0.1%, alternatively less than 100 ppm, alternatively less than 50 ppm. In some embodiments, the biocide is free of halogenated biocides. Treatment with MIT at 50 to 300 ppm is preferred, with 100-200 ppm more preferred, and 125-150 ppm most preferred. Control of mycobacteria is achieved for a minimum of 48 hours after dosing. Levels of mycobacteria are monitored in the fluid to confirm that the growth of mycobacteria has been suppressed after treatment
The following examples provide supporting data for the concept of using 2-methyl-4-isothiazolin-3-one (MIT) biocide for the control of mycobacteria (gram positive, acid-fast bacteria) recently identified and recovered from in-use metalworking fluid system. Results of studies with laboratory and field samples have shown that MIT biocide displayed surprising efficacy in controlling growth of mycobacteria encountered in contaminated metalworking fluid systems, especially compared to known metalworking fluid biocides. In addition, use of MIT provides a one-pack, high pH stable biocide treatment which does not contain or release formaldehyde and which has no heavy metals, no solvent, and no odor.
Summary
Several commonly used biocides in the metalworking fluid industry were tested for their basic level of effectiveness versus pure cultures of Mycobacterium when using standard microbiological efficacy procedures; the Minimum Inhibitory Concentration (MIC) and Minimum Biocidal Concentration (MBC) tests. In these tests, all of the commercial biocides showed efficacy at levels below their typical maximum use rate to inhibit or kill the two strains of Mycobacterium which were evaluated. Based on these laboratory efficacy tests, it would be expected that all of these biocides would show good efficacy at their typical use rates in killing these organisms in contaminated samples from the field.
However, MIT provided unexpected results in controlling the growth of mixed populations of naturally occurring mycobacteria in all samples from six in-use and contaminated metalworking fluid systems. MIT outperformed all of the other commercial metalworking fluid biocides when used at their maximum recommended doses (including three isothiazolone products, a chlorophenolic, and a formaldehyde-releasing triazine biocide) in providing a minimum degree of efficacy (>90% kill) in all six samples of contaminated fluids received from the field.
Background
Metalworking fluids, also referred to as metal machining or metal cutting fluids, are used for cooling and lubricity in metalworking applications. Water-based metalworking fluids are susceptible to microbial contamination by various types of bacteria and fungi, as the fluids are recirculated in an open environment. Various types of gram-negative and gram-positive bacteria, yeasts, and molds are encountered. One specific type of gram-positive bacteria which has recently been identified and recovered in these fluids are members of the genus Mycobacterium, also referred to as mycobacteria.
Mycobacteria comprise a genus of bacteria, which are gram positive, contain mycolic acids in their cell walls, and respond positively to acid-fast staining using standard bacteriological procedures. These organisms have also been recently associated with the occurrence of specific health problems, known as “hypersensitity pneumonitis” (HP), which may be encountered by individuals working in a metal machining or metalworking environment in which aerosols containing these bacteria may be present. Mycobacterium immunogenum, has recently been identified as a new species of mycobacteria in metalworking fluids associated with outbreaks of HP and continues to be recovered in additional fluid systems experiencing HP problems. A recent study using M. immunogenum in mixed populations of metalworking fluids showed the isothiazolone biocide (CMT/MIT) was more effective versus triazines, PCMC, and oxazolidine biocides for rapid kill at equivalent product concentrations (Selvaraju et al., 2005, Appl. Env. Microbiol, 71:542-546).
An improved method for controlling the growth of microorganisms in metalworking fluids was described in a recent patent by Rossmoore (U.S. Pat. No. 4,608,183) using combinations of isothiazolones and monocopper citrate (CMIT/MIT/MCC). The synergy and improved stability of the CMIT compound provided improved efficacy and performance in metalworking fluids.
A method to control the growth of mycobacteria, specifically M. immunogenum, associated with HP, by using the combination of dosing a CMIT/MIT product with MCC has been recently disclosed by Rossmoore (U.S. Pat. No. 6,951,618). High levels of copper citrate (500 ppm) were shown to improve the stability of the chlorinated isothiazolone (CMIT) which is the most active isothiazolone in the CMIT/MIT mixture, but which is subject to rapid degradation by nucleophilic compounds. However, use of high levels of copper in metalworking fluids are not always desired due to discoloration of the end use fluid, increased costs for disposal and waste treatment of the spent fluids, and potential corrosion and metal staining problems. The use of MIT alone as a single product treatment for control of mycobacteria was not disclosed by Rossmoore in this patent. Thus, there exists a need for biocides to provide control of mycobacteria, specifically M. immunogenum, in metalworking fluid systems, with improved stability without the use of adding high levels of added metals or dual product dosing.
EXAMPLES
Example 1
Improved Stability of MI Versus BIT and BNPD Biocides in a pH 9 Buffer Solution at 70° C.
Summary
Studies were conducted to determine the stability of MI (2-methyl-4-isothiazolin-3-one), BIT (1,2-benzisothiazolin-3-one) and BNPD (2-bromo-2-nitro-propane-1,3-diol) under high pH and high temperature conditions. MI demonstrated excellent stability in the pH 9 buffer at 70° C. after 56 days storage. There was no loss of MI over this time. BIT showed decreasing stability over the 56 day study with 32% loss of active ingredient at day 56. BNPD was completely degraded with 5 hours at pH 9 and 70° C.
Method
pH 9 buffer containing 0.069 M boric acid, 0.017 M citric acid, 0.066 M sodium phosphate was prepared in distilled water. Biocide was dosed into the pH 9 buffer solution and stored at 70° C. in a heat block. The samples were examined for active ingredient concentration at the time points after 5 hours, and 1, 3, 7, 23, 30, 35 and 56 days. Initial biocide doses were 166 ppm MI, 199 ppm BIT and 150 ppm BNPD.
The samples were evaluated for active ingredient concentration via High Pressure Liquid Chromatography. Samples were taken from the heating blocks and allowed to cool to room temperature for 30 minutes. The samples were then diluted 1:20 in deionized water by adding 9.5 ml of deionized water to 0.5 grams of the samples in a 25 ml glass sample vial. The samples were mixed for 15 seconds and transferred to HPLC sample vials for analysis. Analytical variation for the HPLC method is ±10%.
Results
There was no loss of MI when stored at 70° C. over 56 days. BIT was less stable with 32% degraded at 70° C. BNPD stability was poor with almost immediate total degradation observed after 5 hours.













Percent Remaining after:






















23
30
35
56


Biocide
0
5 hr
1 day
3 day
7 day
day
day
day
day





MI
100
96
96
96
93
95
101
93
102


BIT
100
98
97
94
92
86
 71
63
 68


BNPD
100
 0
 0
nt
nt
nt
nt
nt
nt





nt = not tested






Example 2
Improved Stability of MI Versus BIT with Various Oxidizing and Reducing Agents at pH 7 and pH 9
Summary
The stability of MI and BIT was evaluated in the presence of various redox agents in pH 7.0 and 9.0 buffer at 2 and 8 days. The results showed greater stability of MI versus BIT under various redox conditions and at elevated pH. Both biocides showed slight degradation with sodium bisulfite at pH 9, but were significantly degraded at pH 7.0. Bisulfite is a known deactivating agent for isothiazolones, especially at lower pH values.
Methods
Oxidizing agents (2 mM) included hydrogen peroxide (H2O2; 68 ppm), t-butyl hydrogen peroxide (t-BHP; 180 ppm), and potassium persulfate (K2O8S2; 540 ppm). Reducing agents (2 mM) included iso-ascorbic acid (IAA; 352 ppm) and sodium bisulfite (NaHSO3; 208 ppm). Biocides were tested at 1 mM concentrations, representing 115 ppm MI and 166 ppm BIT.
The pH 7.0 buffer contained 0.00426% monopotassium phosphate plus 0.019% magnesium chloride hexahydrate. The pH 9.0 buffer contained 0.0046 M hydrochloric acid plus 0.013 M borax. Stock solutions of the redox agents were prepared and added to aliquots of each buffer to give 2 mM concentrations. The biocides were then added to give 1 mM concentrations. The samples were stored at 25° C. and analyzed for biocide level by HPLC at 0, 2 and 8 days.
Results
The results showed greater stability of MI versus BIT under various redox conditions and at elevated pH. MI was more stable than BIT for all of the oxidants tested and only a minimal pH effect was seen at 8 days with hydrogen peroxide. Very little, if any, BIT remained after 8 days with all oxidants at pH 9. BIT also showed more degradation at higher pH versus pH 7, especially with hydrogen peroxide. MI showed better stability versus BIT against the ascorbic acid reducing agent and was not affected by pH. Both biocides showed slight degradation with sodium bisulfite at pH 9, but were significantly degraded at pH 7.0 within 2 days (a known deactivating agent for isothiazolones).














% Remaining after 2
% Remaining after 8



Days
Days












MI
BIT
MI
BIT















Redox Agent
pH 7
pH 9
pH 7
pH 9
pH 7
pH 9
pH 7
pH 9


















None
100
100
100
100
100
100
100
100


H2O2
100
94
39
8
100
88
15
0


t-BHP
99
98
43
38
102
96
8
6


K-persulfate
90
93
0
0
75
73
0
0


IAA
100
105
89
77
96
103
86
75


Na bisulfite
29
70
38
82
26
78
28
77





*redox agents added at 2 mM and biocides added at 1 mM






Example 3
Improved Stability of MI Versus CMI and BIT Isothiazolones in Buffered Water at Various pH and Temperatures
Summary
Stability studies were conducted versus three isothiazolone in buffered deionized water at two different temperatures (22° and 50° C.). MI was shown to be the most stable with only slight loss of active at 50° C. and pH 12 after 90 days. BIT showed good stability up to pH 10 at both temperatures. CMI was the least stable of the isothiazolones tested and was most affected by increasing temperature.
Methods
Biocides were added to buffer solutions and stability was tested at 22° and 50° C. using HPLC to measure biocide concentration at 0 time, 21 days, 43 days, and 88-90 days. Biocide stability was determined in the following buffer solutions: pH2, 0.01M HCl; pH6, 0.1M KH2PO4; pH8, 0.025M borate; pH10, 0.025M borate; pH12, 0.05M Na2HPO4. Biocide concentrations tested were 100 ppm MI, 200 ppm BIT, 44 ppm CMI.
Results
Stability studies were conducted versus three isothiazolone in buffered water at two different temperatures (22° and 50° C.). MI was the most stable biocide tested, followed by BIT, with CMI the least stable over the range of conditions. MI showed excellent stability at room temperature up to pH 12. At 50° C., MI stability decreased slightly, but only at pH 12. BIT showed excellent stability at room temperature and 50° C. up to pH 10. Slight degradation occurred at pH 12 at both temperatures. CMI showed rapid and complete degradation at pH 10-12 at room temperature (22° C.) and poor stability at pH 6-12 at the higher temperature.













Percent Remaining at:















Biocide
Day
pH 2
pH 6
pH 8
pH 10
pH 12











Biocide stability at 22° C. in buffered water.















CMI
0
100
100
100
100
100




21
100
100
100
0
0




43
100
100
91
0
0




88
100
100
95
0
0



BIT
0
100
100
100
100
100




21
97
100
98
100
69




43
83
86
77
85
55




88
95
100
84
96
63



MI
0
100
100
100
100
100




21
104
100
100
100
98




43
98
94
95
89
93




88
100
100
100
100
100







Biocide stability at 50° C. in buffered water.















CMI
0
100
100
100
100
100




21
100
100
15
0
0




43
93
65
0
0
0




88
100
30
0
0
0



BIT
0
100
100
100
100
100




21
95
100
94
100
68




43
80
88
73
81
55




90
93
100
89
95
68



MI
0
100
100
100
100
100




21
100
98
100
98
90




43
97
93
95
93
78




90
100
100
100
100
76










Example 4
Effective Levels of MI Versus Bacteria and Fungi
Summary
Minimum Inhibitory Concentration (MIC) studies with bacteria and fungi demonstrated that MI alone required significantly higher concentrations for efficacy compared to MI present in the 3:1 ratio CMI+MI combination product. In the CMI+MI combination, the level of antimicrobial activity is solely due to the chlorinated isothiazolone (CMI) and the level of MI present is significantly lower than the level of MI alone required for efficacy.
Methods
Minimum inhibitory concentration (MIC) studies were conducted to determine the lowest level of biocide required to inhibit growth of bacteria and fungi. Tests were conducted in 96-well microtiter plates. Biocides were added to growth media in the plates and serially diluted to obtain a range of concentrations. Bacterial tests were conducted in trypticase soy broth (TSB; pH 7) using an overnight inoculum added at 106 colony forming units per ml. Samples were incubated at 25° C. for two days and the MIC value determined visually on a growth no-growth basis. Fungal tests were conducted in malt extract broth (MEB; pH 4.7) using an 5-7 day inoculum added at 104 colony forming units per ml. Samples were incubated at 25° C. for 7 days and the MIC value determined as above.
Results
The MIC studies show that the level of MI required for efficacy is significantly (10-100×) greater than the MI level present in the 3:1 ratio CMI:MI combination product for control of both bacteria and fungi. The average MIC value for MI alone versus bacteria and fungi was 24 and 63 ppm MI alone, respectively; whereas, in the 3:1 combination the MI was present at only 0.56 and 0.34 ppm, respectively. Thus, the MI present in the combination biocide was significantly lower than that required from MI alone and the CMI component of the blended isothiazolone was solely responsible for the efficacy observed.














MIC (ppm)
Conc. of MI in the












CMI + MI
3:1 CMI + MI



MI
(3:1)
 Combination MIC











Comparison of Minimum Inhibitory Concentration (MIC) Values


for MI alone versus CMI + MI Combination versus Bacteria










Bacteria





Alcaligenes faecalis
28
2.5
0.63


Citrobacter freundii
25
0.8
0.20


Citrobacter freundii
41
0.8
0.20


Enterobacter cloacae
25
1.5
0.38


Enterobacter aerogenes
82
8.0
2.00


Escherichia coli
31
2.5
0.63


Klebsiella pneumoniae
12
0.4
0.10


Proteus mirabilis
21
0.8
0.20


Pseudomonas aeruginosa
15
2.5
0.63


Pseudomonas aeruginosa
25
2.5
0.63


Pseudomonas fluorescens
31
3.0
0.75


Pseudomonas fluorescens
16
2.5
0.63


Pseudomonas oleovorans
6
2.5
0.63


Pseudomonas oleovorans
6
1.2
0.30


Pseudomonas putida
13
3.0
0.75


Shewanella putrefaciens
13
1.2
0.30


Average
24
2.2
0.56









MI: CMI + MI
10.9



MIC Ratio







Comparison of Minimum Inhibitory Concentration (MIC) Values


for MI alone versus CMI + MI Combination versus Fungi










Fungi





Acremonium strictum
16
0.6
0.15


Candida albicans
100
1.5
0.38


Field Isolate
8
0.4
0.10


Field Isolate
21
0.2
0.05


Field Isolate
6
0.2
0.05


Fusarium solani
13
0.4
0.10


Fusarium sp.
25
0.4
0.10


Geotrichum candidum
250
7.0
1.75


Rhodotorula rubra
125
1.5
0.38


Trichosporon sp.
63
1.2
0.30


Average
63
1.3
0.34









MI: CMI + MI
46.8



MIC Ratio









Example 5
Improved Efficacy of MI Versus BIT Against Bacteria and Fungi at Elevated pH Values
Summary
Minimum Inhibitory Concentration (MIC) studies with bacteria and fungi demonstrated that MI efficacy was not significantly affected by increasing pH (pH 9 vs. pH 7), whereas BIT was less effective for control of microbial growth under more alkaline conditions (pH 9). Based on these findings, MI would be a more desirable biocide for effective control of microorganisms under high pH conditions.
Methods
Minimum inhibitory concentration (MIC) studies were conducted to determine the lowest level of biocide required to inhibit growth of bacteria and fungi. Tests were conducted in 96-well microtiter plates. Biocides were added to growth media in the plates and serially diluted to obtain a range of concentrations. Tests were conducted in one-half strength trypticase soy broth (TSB; adjusted to pH 7.1 or pH 9.0). Bacteria and fungi were added to samples at 106 colony forming units per ml and incubated at 30° C. for three days. MIC values were determined visually on a growth no-growth basis.
Results
Minimum Inhibitory Concentration (MIC) studies with bacteria and fungi demonstrated that MI efficacy was not significantly affected by increasing pH (pH 9 vs. pH 7), whereas BIT was less effective for control of microbial growth under more alkaline conditions (pH 9).
MIC values for MI showed no major difference in antimicrobial activity at pH 7.1 versus pH 9.0. Results at both pH values were generally identical, or within one well in the microtiter plate (equal to a 2× difference) which is the limit of resolution of the MIC test. None of the organisms tested with MI showed more than a 2× change in efficacy as a function of pH.
BIT, by comparison, showed significantly higher MIC values at pH 9.0 versus pH 7.1 for most of the bacteria and fungi tested. Eight of the nine organisms showed a pH effect with BIT, with MIC values from 4 to 30× higher at pH 9.0 versus pH 7.1.
These results demonstrate MI as a highly effective biocide for use in applications with elevated pH conditions.












Minimum Inhibitory Concentration


Organism
(ppm)









And
MI
BIT











Strain Number
pH 7.1
pH 9.0
pH 7.1
pH 9.0














Aspergillus niger #128
100
100
50
200


Aspergillus sp. #120
50
50
50
400


Rhodotorula rubra #156
25
25
<6.3
100


Pseudomonas aeruginosa #13
12.5
6.3
50
200


Pseudomonas pseudoalcaligenes
25
25
12.5
25


#15


Alcaligenes faecalis #93
3.2
6.3
<1.6
6.3


Alcaligenes xylosoxydans #95
12.5
25
6.3
25


Pseudomonas diminuta #99
12.5
6.3
3.2
12.5


Streptomyces sp. #130
3.2
3.2
<1.6
3.2









Values in bold represent a 4× or greater increase in the MIC at pH 9.0 versus 7.1.

Example 6
Minimum Inhibitory Concentration (MIC) and Minimum Biocidal Concentration (MBC) Studies with Commercial Biocides Versus Pure Cultures of Mycobacterium in Standard Laboratory Media
MIC and MBC studies were conducted to determine the basic efficacy of several commercial biocides typically used in metalworking fluids, for inhibition and killing of two strains of mycobacteria using standard media and laboratory procedures. Results showed that all commercial biocides demonstrated efficacy (both inhibition and killing) of both strains at levels below their maximum recommended use level. This indicates that these biocide possess the inherent antimicrobial efficacy against strains of mycobacteria, when tested in the absence of other bacteria and using standard laboratory media.
The lowest concentration of microbicide required to inhibit bacteria was determined by a high resolution MIC test. Varying amounts of each microbicide were added to media in a 96-well microtiter plate. The media used for the MIC tests was 10% Trypicase Soy Broth ( 1/10× TSB). Ten-fold serial dilutions were performed on a Biomek 2000 Workstation to obtain a range of closely spaced concentrations of microbicides. A cell suspension of stationary phase microorganisms, adjusted to provide 106 colony forming units (CFU)/mL in each well for bacteria was added to the microtiter plate. The microtiter plates were incubated for 24 hours at 30° C. for Mycobacterium immunogenum and 37° C. for Mycobacterium chelonae. The presence or absence of microbial growth was determined by measuring the turbidity in each well using a Thermomax microplate reader set at an absorbance of 650 nm. The lowest concentration of compound in which no growth was observed was considered the MIC value for the microbicide. The MIC value for each microbicide was determined from the average of four determinations for bacteria.
Bacterial strains tested included Mycobacterium chelonae (ATCC 14472) and Mycobacterium immunogenum (ATCC 700505). Mycobacterial cultures were grown overnight at 30° C. (M. immunogenum) or 37° C. (M. chelonae), in a rotary shaking bath in Middlebrook 7H10 Agar with Middlebrook enrichment. A 1:20 dilution of the overnight culture was made into the appropriate test media and inoculated to give a final concentration of 106 to 107 CFU/ml.
MBC tests were conducted by transferring samples from the MIC test samples into fresh media and observing for growth of the culture. Growth was determined as above. In this test using Biomek 2000 Workstation, 10 μl samples taken from the 96-well MIC plates were placed in 190 ml of fresh growth media to determine the number of surviving organisms for the same gradient of biocide concentrations. These plates were incubated and read in the same fashion as the MIC plates. The lowest level of biocide from the MIC plates that showed no survivors upon transfer to fresh media after 2 days was considered the MBC.
Results shown in Table 1 demonstrate that all the commercial biocides demonstrated efficacy (both inhibition and killing) of both strains at levels less than their maximum recommended use level. Based on these data, it would be expected that these biocides should all be effective against similar organism encountered in actual metalworking fluid samples from the field.







TABLE 1







Minimum Inhibitory Concentration (MIC) and Minimum Biocidal Concentration


(MBC) of Various Biocides Against Pure Cultures Strains of Mycobacterium












Minimum Inhibitory
Minimum Biocidal



Maximum
Concentration
Concentration



Use Level
(ppm active)
(ppm active)












Biocide
(ppm active)
M. chelonae
M. immunogenum
M. chelonae
M. immunogenum















CMIT/MIT
17.5
2.9
3.0
3.0
3.0


CMIT/MIT/MCC
17.5
0.8
1.1
0.8
1.1


MIT
150
15
50
40
84


BIT
340
63
113
75
188


Triazine
1180
43
39
314
314


Oxazolidine
1560
42
38
34
836


PCMC
3450
20
35
60
75









Example 7
Comparison of Biocide Efficacy at the Maximum Recommended Dose Levels for Eradication and Control of Mycobacteria in Contaminated Samples of Metalworking Fluids from In-Use Systems
A comparative study was conducted evaluating six metalworking fluid biocides versus natural, resident populations of Mycobacterium from six in-use metalworking fluids. CMIT/MIT, CMIT/MIT/MCC, MIT, BIT, triazine, and PCMC microbicides were tested under controlled laboratory conditions to determine their efficacy at the maximum manufacturer's recommended dose rate (Table 2). The metalworking fluids were known to contain high levels of mycobacteria prior to dosing with biocides. Samples were then dosed with biocides, incubated with agitation at room temperature and viable mycobacteria counts determined after 48 hours by plating onto Middlebrook 7H10 medium, with Tween 80, glycerin, cyclohexamide, chloramphenicol, and gentamycin to suppress the growth of unwanted microorganisms.
The comparative efficacy (log kill) of the various biocides dosed at 100% of the manufacturer's maximum recommended treatment rate are shown in Table 3. MIT was the only biocide which provided at least a one-log reduction (90% kill) in each of the six metalworking fluids (Table 4). MIT was also the only biocide which provided at least a two-log reduction (99% kill) in five of the six fluids tested. PCMC was effective in five fluids tested with at least a 90% kill and in four fluids with a minimum 99% kill. CMIT/MIT and CMIT/MIT/MCC were only effective in four of the six fluids tested at these kill rates. Triazine and BIT biocides did not show efficacy in any of the fluids tested.
These results showed MIT as surprisingly effective for controlling the growth of mycobacteria in naturally contaminated metalworking fluids at the maximum recommended dose levels, especially since all of these biocides previously demonstrated efficacy against pure cultures of these organisms in laboratory studies at lower levels. MIT significantly outperformed all other biocides, including CMIT/MIT/MCC, previously reported by Rossmoore (U.S. Pat. No. 6,951,618) as a highly effective biocide versus mycobacteria. However, the MIT treatment method does not require the use of two products and does not require high levels of copper salts, which add color to fluids and poses potential corrosion, metal staining and waste treatment problems.







TABLE 2







Biocides tested and dose levels for in-use eradication efficacy


studies versus mycobacteria in contaminated field samples.










50% of




Maximum
100% of


Biocide Tested
Dose
Maximum Dose





CMIT/MIT
 9 ppm
 17.5 ppm


(14% active KATHON TM 886 MW)


CMIT/MIT/MCC
 9 ppm
 17.5 ppm


(1.5% active KATHON TM CC)


MIT
 75 ppm
  150 ppm


(50% active KORDEK TM LX 5000)


Triazine
588 ppm
1,180 ppm


(78.5% active GROTAN TM)


PCMC
1725 ppm 
3,450 ppm


(46% active PREVENTOL TM CMK)


BIT
171 ppm
  342 ppm


(19% active PROXEL TM GXL)





Biocides are given as active ingredient dose levels.


See previous text for specific chemical composition of the actives.


KATHON TM and KORDEK TM are registered trademarks of the Rohm and Haas Company.


GROTAN TM is a registered trademark of the Troy Chemical Company, Ltd.


PREVENTOL TM is a registered trademark of the Lanxess Corporation.


PROXEL TM is a registered trademark of the Arch Corporation.













TABLE 3







Log reduction of mycobacteria counts in naturally contaminated metalworking


fluids 48 hours after adding biocides at 100% of the recommended maximum


dose level.









Log Reduction in Mycobacterial Counts



versus Control (no biocide)













Biocide
Fluid 1
Fluid 2
Fluid 3
Fluid 4
Fluid 5
Fluid 6





MIT
5.88
5.00
2.00
3.64
1.90
3.88


CMIT/MIT
4.97
5.00
0.00
3.24
0.09
3.88


CMIT/MIT/MCC
5.57
5.00
0.00
3.54
0.00
3.88


Triazine
0.00
0.12
0.00
0.00
0.00
0.00


BIT
0.00
0.00
0.60
0.00
0.06
0.00


PCMC
5.88
5.00
1.00
5.24
0.90
3.88


Untreated Control*
1.5 × 106
2.0 × 105
1.0 × 106
3.5 × 105
8.0 × 105
1.5 × 104


(Initial Count)


Untreated Control*
3.5 × 106
6.0 × 105
3.0 × 106
5.0 × 105
1.0 × 106
7.5 × 104


(48 hour count)





*Mycobacterial counts (per ml) in untreated control samples













TABLE 4







Efficacy of six biocides versus mycobacteria in naturally


contaminated fluids 48 hours after doing at 100% of


recommended maximum levels.












No. of Fluids with
No. of Fluids with




≧90% Kill
≧99% Kill



Biocide
(1-log reduction)
(2-log reduction)







MIT
6
5



CMIT/MIT
4
4



CMIT/MIT/MCC
4
4



PCMC
5
4



Triazine
0
0



BIT
0
0










Example 8
Comparison of Biocide Efficacy at 50% of the Maximum Recommended Dose Levels for Eradication and Control of Mycobacteria in Contaminated Samples of Metalworking Fluids from In-Use Systems
The six metalworking fluid samples containing mycobacteria study from Example 7, were also tested using the same biocides with dosing at 50% of the maximum manufacturer's recommended rate (Table 2) under the same conditions. These metalworking fluids were known to contain high levels of mycobacteria prior to dosing with biocides. Samples were then dosed with biocides, incubated with agitation at room temperature and viable mycobacteria counts determined after 48 hours by plating onto Middlebrook 7H10 medium, with Tween 80, glycerin, cyclohexamide, chloramphenicol, and gentamycin to suppress the growth of unwanted microorganisms.
The efficacy (log kill) data for dosing at 50% of the maximum treatment rate are shown in Table 5. MIT and CMIT/MIT/MCC were the only biocide which provided at least a one-log reduction (90% kill) in four of the six fluids and at least a two-log reduction (99% kill) in three of the six fluids tested (Table 6). CMIT/MIT achieved a minimum 90% to 99% kill in only three fluids. PCMC provided ≧90% kill in three fluids and achieved a ≧99% kill in only two fluids. Triazine and BIT biocides did not show efficacy in any of the six fluids tested.
These results showed MIT as surprisingly effective for controlling the growth of mycobacteria in naturally contaminated metalworking fluids even when dosed at 50% of the maximum recommended treatment level, especially since all of these biocides previously demonstrated efficacy against pure cultures of these organisms in laboratory studies at low levels. At one-half the recommended use rate, MIT provided similar efficacy compared to CMIT/MIT/MCC biocide, previously reported by Rossmoore (U.S. Pat. No. 6,951,618) as a highly effective biocide versus mycobacteria. However, the MIT treatment method does not require the use of two products and does not require high levels of copper salts, which add color to fluids and poses potential corrosion, metal staining, and waste treatment problems.







TABLE 5







Log reduction of mycobacteria counts in naturally contaminated


metalworking fluids 48 hours after adding biocides at 50% of the recommended


maximum dose level.









Log Reduction in Mycobacterial



Counts versus Control (no biocide)













Biocide
Fluid 1
Fluid 2
Fluid 3
Fluid 4
Fluid 5
Fluid 6





MIT
3.48
3.80
0.00
2.00
0.06
1.78


CMIT/MIT
2.00
2.30
0.00
0.77
0.00
2.00


CMIT/MIT/MCC
1.88
5.00
0.00
2.54
0.00
2.18


Triazine
0.00
0.00
0.00
0.00
0.06
0.00


BIT
0.00
0.00
0.00
0.00
0.00
0.00


PCMC
0.00
1.00
0.00
5.24
0.51
3.88


Untreated Control*
1.5 × 106
2.0 × 105
1.0 × 106
3.5 × 105
8.0 × 105
1.5 × 104


(Initial Count)


Untreated Control*
3.5 × 106
6.0 × 105
3.0 × 106
5.0 × 105
1.0 × 106
7.5 × 104


(48 hour count)





*Mycobacterial counts (per ml) in untreated control samples













TABLE 6







Efficacy of six biocides versus mycobacteria in naturally


contaminated fluids 48 hours after dosing at 50% of


recommended maximum levels.












No. of Fluids





with
No. of Fluids with




≧90% Kill
≧99% Kill



Biocide
(1-log reduction)
(2-log reduction)







MIT
4
3



CMIT/MIT
3
3



CMIT/MIT/MCC
4
3



PCMC
3
2



Triazine
0
0



BIT
0
0










Example 9
Comparison of Stability of MIT Versus CMIT (with and Without MCC) in Aggressive Metalworking Fluids
Stability studies were conducted in three high pH metalworking fluid use dilutions to compare the persistence of MIT biocide versus CMIT biocide, tested alone and in combination with MCC). Aliquots of the use-diluted fluids were dosed with 17.5 ppm active CMIT/MIT and CMIT/MIT/MCC and stored at 25° C. Biocide concentrations were determined at time zero and weekly using high performance liquid chromatography (HPLC) analysis.
Results showed that MIT alone retained greater than 90% of the biocide active after 3-4 weeks in all three of the high pH use-diluted fluids (Table 7). By contrast, CMIT alone rapidly degraded in the three fluids with none remaining after 3-4 weeks. Addition of 300 ppm MCC improved CMIT stability moderately, but none of the fluid had more than 16% of the biocide remaining after 3-4 weeks.
These results clearly demonstrate the superior stability of MIT biocide relative to the combination of CMIT plus MCC in typical (high pH) metalworking fluid use dilutions. Rossmoore (U.S. Pat. No. 6,951,618) previously reported MCC as an effective stabilizer to prevent degradation of CMIT in aggressive fluids; however, this effect was not observed to be long-lived or highly effective for extended periods in the fluids tested herein. Thus, MIT was shown to be not only the most effective biocide for control of mycobacteria in metalworking fluids, it was also shown to be the most stable isothiazolone biocide for long-term persistence for microbial control in aggressive fluids.







TABLE 7







Stability of CMIT versus MIT in end-use dilutions of metalworking fluids.













% CMIT






Remaining
% CMIT




(without
Remaining
% MIT


Fluid Type
Time
MCC)
(with MCC)
Remaining














Soluble Fluid 1
2 wk
28
38
95


(pH 9.2)
4 wk
10
18
100


Synthetic Fluid 2
1 wk
13
42
92


(pH 9.4)
3 wk
 0*
0
94


Soluble Fluid 3
2 wk
25
35
95


(pH 9.3)
4 wk
 0
16
100





CMIT added at 11-13 ppm


MCC added at 300 ppm


MIT added at 3.6-4.3 ppm


*= none detected (<0.8 ppm)


Analytical precision was +/−10%.

## Claims

1. A method for treating water in a closed cooling system, having a pH from 9 to 10.5 and a temperature of at least 35° C. and no more than 60° C., by adding a composition comprising 2-methyl-4-isothiazolin-3-one; wherein said composition is substantially free of metal ions non-aqueous solvents, volatile organic compounds and halogenated biocides; wherein metal ions, non-aqueous solvents, volatile organic compounds and halogenated biocides are not added separately to the water; and wherein 2-methyl-4-isothiazolin-3-one is present in an amount sufficient to produce in the water a 2-methyl-4-isothiazolin-3-one concentration from 15 ppm to 500 ppm to control the growth of microorganisms in said water.

2. The method of claim 1 in which the concentration of 2-methyl-4-isothiazolin-3-one is from 25 ppm to 300 ppm.

3. The method of claim 2 in which the water is substantially free of biocides other than 2-methyl-4-isothiazolin-3-one.

4. The method of claim 3 in which the concentration of 2-methyl-4-isothiazolin-3-one is from 30 ppm to 200 ppm.

5. A method for controlling the growth of mycobacteria in metalworking fluids; said method comprising adding 50 to 300 ppm of a 2-methyl-4-isothiazolin-3-one composition which does not contain metal salts to a metalworking fluid having a pH from 8 to 12; wherein the fluid is substantially free of halogenated biocides.