CA1270418A - Synergistic biocide of 2-(thiocyanomethyl-thio) benzothiazole with a mixture of 5-chloro-2-methyl-4- isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one - Google Patents
Synergistic biocide of 2-(thiocyanomethyl-thio) benzothiazole with a mixture of 5-chloro-2-methyl-4- isothiazolin-3-one and 2-methyl-4-isothiazolin-3-oneInfo
- Publication number
- CA1270418A CA1270418A CA000514278A CA514278A CA1270418A CA 1270418 A CA1270418 A CA 1270418A CA 000514278 A CA000514278 A CA 000514278A CA 514278 A CA514278 A CA 514278A CA 1270418 A CA1270418 A CA 1270418A
- Authority
- CA
- Canada
- Prior art keywords
- isothiazolin
- methyl
- chloro
- benzothiazole
- systems
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01N—PRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
- A01N43/00—Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds
- A01N43/72—Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds having rings with nitrogen atoms and oxygen or sulfur atoms as ring hetero atoms
- A01N43/80—Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds having rings with nitrogen atoms and oxygen or sulfur atoms as ring hetero atoms five-membered rings with one nitrogen atom and either one oxygen atom or one sulfur atom in positions 1,2
Abstract
ABSTRACT OF THE DISCLOSURE
The combination of biocides, A. 5-chloro-2-methyl 4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one; and B. 2-(thiocyanomethylthio)-benzothiazole provide a synergistic material for controlling microorganisms in industrial process waters.
The combination of biocides, A. 5-chloro-2-methyl 4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one; and B. 2-(thiocyanomethylthio)-benzothiazole provide a synergistic material for controlling microorganisms in industrial process waters.
Description
INTRODUCTION
The formation of slime by mlcroorganisms is a problem which attends many systems. For example, lagoons7 lakes, ponds~
pools, and such systems as cooling water systems and pulp and paper mill systems 7 all possess conditions which are conductive to the growth and reproduction of slime-~ormlng microorganisms~
In both once-through and recirculating coolin~ systems, For example, which employ large quantities of water as a cooling medium, the ~ormation o~ slime by microorganisms is an extensiYe and constant problem Airborne organisms are readily entrained in the water ~rom cooling towers and find this warm medium an ideal environment ~or growth and multiplication. Aerobic and heliotropic organisms flourish on the tower proper while other organisms colonize and grow in such areas as the tower sump and the piping and passages o~ the cooling system. Such slime serves to deteriorate the tower structure in the case of wooden towers.
In addition, the deposition of slime on metal surfaces promotes corrosion. Furthermore, slime carried through the coolin3 system plugs and fouls lines, valves, strainers, etc. and deposits on heat exchange surfaces. In the latter case, the impedance o~
heat trans~er can greatly reduce the e~iciency of the cooling system.
In pulp and paper mill systems, slime ~ormed by microorganisms is also ~requently and, in fact, commonly encountered. Fouling or plugging by slime also occurs in the case o~ pulp and papex mill systems. O~ greater signi~icance, the slime becomes entrained in the paper produced to cause breakouts on the paper machines with consequent work st~ppages and the loss n~ production time or unsightly blemishes in the
The formation of slime by mlcroorganisms is a problem which attends many systems. For example, lagoons7 lakes, ponds~
pools, and such systems as cooling water systems and pulp and paper mill systems 7 all possess conditions which are conductive to the growth and reproduction of slime-~ormlng microorganisms~
In both once-through and recirculating coolin~ systems, For example, which employ large quantities of water as a cooling medium, the ~ormation o~ slime by microorganisms is an extensiYe and constant problem Airborne organisms are readily entrained in the water ~rom cooling towers and find this warm medium an ideal environment ~or growth and multiplication. Aerobic and heliotropic organisms flourish on the tower proper while other organisms colonize and grow in such areas as the tower sump and the piping and passages o~ the cooling system. Such slime serves to deteriorate the tower structure in the case of wooden towers.
In addition, the deposition of slime on metal surfaces promotes corrosion. Furthermore, slime carried through the coolin3 system plugs and fouls lines, valves, strainers, etc. and deposits on heat exchange surfaces. In the latter case, the impedance o~
heat trans~er can greatly reduce the e~iciency of the cooling system.
In pulp and paper mill systems, slime ~ormed by microorganisms is also ~requently and, in fact, commonly encountered. Fouling or plugging by slime also occurs in the case o~ pulp and papex mill systems. O~ greater signi~icance, the slime becomes entrained in the paper produced to cause breakouts on the paper machines with consequent work st~ppages and the loss n~ production time or unsightly blemishes in the
-2-~inal product which result in re~ects and wasted output. The previously discussed problems have resulted in the extensive utilization of biocides in cooling water and pulp and paper mill systems. Materials which have enjoyed widespread use in such applications include chlorine, organo-mercurials, chlorinated phenols, organo-bromines, and various organo-sul~ur compounds.
All of these compounds are generally useful ~or this purpose but each is attended by a variety o~ impediments. For example, chlorination is limited both by its specific toxicity for slime-~orming organisms at economic levcls and by the ability of chlorine to react which results in the expendlture of the chlorine before its full biocidal function may be achieved.
Other biocides are attended by odor problems and hazards in respect to storage, use or handling which limit their utility.
To date, no one compound or type of compoun~ has achieved a clearly established predominance in respect to the applications discussed. Likewise, lagoons, ponds, lakes, and even pools, either used ~or pleasure purposes or used for industrial purposes for the disposal and storage o~ industrial wastes, become, during the warm weather, beseiged by slime due to microorganism growth and reproduction. In the case of the recreation areas~ the problem of infection, etc. is obvious. In the case of industrial storage or disposal of industrial materials, the microorganisms cause additional problems which must be eliminated prior to the materials use or the waste is treated for disposal.
Naturally, economy is a major consideration in respect to all of these biocides. Such economic considerations attach to both the cost o~ the blocide and the expense of its application.
The cost performance index of any biocide is derived from the basic cost of the material, its effectiveness per unit of weight, ~ ~ 7q~
the duration of its biocidal or biostatic e~fect in the system treated, and the ease and frequency of its addition to the system treated. To date, none of the commercially available biocides have exhibited a prolonged biocidal effect. Instead7 their e~ectiveness is rapidly reduced as the result of exposure to physical conditions such as temperature 7 association with ingredients contained by the system toward which they exhibit an a~inity or substantivity, etc., with a resultant restriction or elimination of their biocidal effectiveness.
As a consequence, the use of such biocides involves their continuous or frequent addition to systems to be treat~d and their addition to a plurality o~ points or zones i~ the systems to be treated. Accordingly, the cost o~ the biocide and the labor cost of such means of applying it are considerable. In other instances, the difficulty of access to the zone in which slime formation is experienced precludes the e~fective use of a biocide. For example, in a particular system there is no access to an area at which slime formation occurs and it may only be applied at a point which is upstream in the flow system.
However, the physical or chemical conditions, e.g., chemical reactivity, thermal degradation, etc. which exist between the point at which the biocide may be added to the system and the point at which its biocidal effect is desired render the e~fective use of a biocide impossi~le.
Similarly, in a system experiencing relatively slow ~low, such as a paper mill, if a biocide is added at the beginnin~ of the system, its biocidal effect may be completely dissipated before it has reached all of the points at which this effect is desired or required. As a consequence, the bioclde must be added at a plurality of points, and even then a graduated ~ 3~ ~
biocidal effect will be experienced between one point o~ addition to the system and the next point downstream at which the biocides may be added. In addition to the increased cost of utilizing and maintaining plural feed points, gross ineconomies in respect to the cost of the biocide are experienced. Specifically, at each point o~ addition, an excess of the biocide is added to the system in order to compensate for that portion of the biocide which will be expended in reacting with other constituents present in the system or experience physical changes which impair its biocidal activity.
It is now known that the mixture of 75%
5-chloro-2-methyl-4-isothiazolin-3-one and 25%
2-methyl-4-isothiazolin 3-one which is sold under the trademark of Kathon-886 by Rohm and Haas may be blended with cert2in sulfones to produce a synergistic biocide. This is the subject matter of U.S. Patent No. 3,~29,561.
It is also known that Kathon-886 may be synergistically combined with either chlorine or chlorine dioxide to provide an improved microbiocide ~or treating aqueous systems of the type described above. This is described in U.S. Patent No. 47295,932.
Kathon-886 is effective at low dosages, e.g. a few parts per million, for treatin9 industrial systems contaminated with a wide variety o~ microorganiSmS. These microorganisms include bacteria, molds, fungi, yeast and algae. In many cases, however, in order to achieve good control of microbiological growth in industrial cooling systems, Kathon-886 must be used at high dosages, e.g. in excess of lO ppm. When such badly contaminated systems are treated with Kathon-886, it is relatively impossible to reduce the total count to a low level. Due to the high cost of Kathon-886, it is, therefore, not practical to use this ~'7~
material for controlling aqueous industrial systems which are heavily contaminated by microorganisms. Such systems containing heavy microorganism contamination are the type o~ system which bene~it most from the practice o~ the instant invention.
These heavily contaminated systems are often further characterized as containing large amounts of deposits which are composed of dea~ microorganism masses. In severe cases they can often have the appearance of bearded slimes.
THE INvENTIbN
The invention comprises a synergistic biocidal composition useful in treating industrial process waters to prevent and control the growth of microorganisms, which composition comprises:
A. ~rom 5 - 95~ by weight of 75%
5-chloro-2-methyl-4-isothiazolin-3-one and 25%
2-methyl-4-isothiazolin-3-one; and 8. from 95 - 5% by weight of 2-~thiocyanomethylthio)-benzothiazole.
This combination is effective at low dosages 7 e.g.
l-lOppm.
l Evaluation o~ the Invention I ~
The synergism of these two components is demonstrated by adding 2-(thiocyanomethylthio)-benzothiazole ~commercially known as TCMTB) and a mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one ~commercially known as Kathon) in varying ratios over a range of concentrations to liquid nutrient medium. In this study of the control of bacterial growth, the nutrient medium was tryptone glucose extract agar.
The concentrations of the above toxicants were added to aliquots o- medium at temperature of 50C. Once treated, the medium was poured into sterile Petri dishes and allowed to solidif~.
Each test plate was inoculated with a bacterial suspension containing 0.1 ml of a nutrient broth culture of Pseudomonas aeruginosa. After an incubation at 37C for over forty-eight hours, the lowest concentration of each toxicant or of each ratio of the combined toxicants that prevented growth on the agar was taken as the end point.
The end points of each of the ratios tested were then compared with end points of the concentrations of the pure toxicants. Syner~ism was determined according to the industrially-accepted method described by S. C. Kull, P. C.
Eisman9 H. D. Sylwestrowicz, and R. L. Mayer in ~pplied Microbiolo~, VolO 9, pages 538-541 (1936).
As regards the Kull, et al. document, the data here presented can be described as follows:
QA=the ppm of actives oE TC~TB alone which produced an end po;nt Qa=the ppm of actives of TCMTB, in combination, which produced an endpoint =the ppm of actives of Kathon alone which produced an endpoint Qb=the ppm of active~ of Kathont in combination, which proauced an endpoin~
if Qa ~ Qb ~ 1 indicates s~rnergy QA QB
> 1 indicates antagonis~
= 1 indicates additivity ~X7()~
TALLP: I
SYNERGISM STUDY FOR CO~!BINATION 3IOCID2S AGAINST BACTERIA
Growth: ~
No Growth: -Control Cultureo 3. 00 x 107 organisms ;?er ml F~atic~
TC. lTB/
KATElO~: __Co centrations (ppm~
0.3 0.6 1.0 1.5 3.0 5.~ 7.5 10 20 30 40 50 100~0 ~ ~ + ~ + ~ +
90/10 + ~ ~ ~ + +
10/gO + ~ + ~
75~25 +
2 5 ~ 7 5 ~ I +
5 ~ / 5 0 ~ + ~ + ~
Ratio Q~ + QP
TCMTB/RAT~ONQA QB
9U/10 0. 783 ~l Syn~rgy 10/90 0. 458 ~1 Synergy 75/25 0. 604 ~1 Synergy 25/7S 0. 394 <1 Synergy 50/50 0. 575 ~1 Synergy -1~04~
QA = 20 ppm active TCr~5TB
QB = 3 pprn active KATHOM
~. 90/10 . Q~ = 10 ppM X . 90 = 9 Qb ~ 10 ppm x .10 =~ 1 9 + 1- 0.783 Bo ln/90 Qa ~ 105 pp)~ X .la = 0.15 Qb ~ 1.5 ppm x .90 = 1035 O15 + ]. 35 - 0.458 C. 7~/25 Qa ~ S pprn x 0~75 = 3.75 Qb 5 PP~ x 0 . 2 5 - 1. Z 5 3O75 ~ 1.25 - 0.604 2U- 3~
D. 25~75 Qa = 1.5 ppm x 0.25 = .375 Qb = 1. 5 ppm x 0O 75 = 1.125 375 ~ 1ol25 = 0~394 . 20 3 Eo 50/50 52a ~ 3 ppm x 0. 50 - 1. 5 Qb = 3 pPm x 0. 50 = 1. 5 1.5 ~ 1.5 - 0.575
All of these compounds are generally useful ~or this purpose but each is attended by a variety o~ impediments. For example, chlorination is limited both by its specific toxicity for slime-~orming organisms at economic levcls and by the ability of chlorine to react which results in the expendlture of the chlorine before its full biocidal function may be achieved.
Other biocides are attended by odor problems and hazards in respect to storage, use or handling which limit their utility.
To date, no one compound or type of compoun~ has achieved a clearly established predominance in respect to the applications discussed. Likewise, lagoons, ponds, lakes, and even pools, either used ~or pleasure purposes or used for industrial purposes for the disposal and storage o~ industrial wastes, become, during the warm weather, beseiged by slime due to microorganism growth and reproduction. In the case of the recreation areas~ the problem of infection, etc. is obvious. In the case of industrial storage or disposal of industrial materials, the microorganisms cause additional problems which must be eliminated prior to the materials use or the waste is treated for disposal.
Naturally, economy is a major consideration in respect to all of these biocides. Such economic considerations attach to both the cost o~ the blocide and the expense of its application.
The cost performance index of any biocide is derived from the basic cost of the material, its effectiveness per unit of weight, ~ ~ 7q~
the duration of its biocidal or biostatic e~fect in the system treated, and the ease and frequency of its addition to the system treated. To date, none of the commercially available biocides have exhibited a prolonged biocidal effect. Instead7 their e~ectiveness is rapidly reduced as the result of exposure to physical conditions such as temperature 7 association with ingredients contained by the system toward which they exhibit an a~inity or substantivity, etc., with a resultant restriction or elimination of their biocidal effectiveness.
As a consequence, the use of such biocides involves their continuous or frequent addition to systems to be treat~d and their addition to a plurality o~ points or zones i~ the systems to be treated. Accordingly, the cost o~ the biocide and the labor cost of such means of applying it are considerable. In other instances, the difficulty of access to the zone in which slime formation is experienced precludes the e~fective use of a biocide. For example, in a particular system there is no access to an area at which slime formation occurs and it may only be applied at a point which is upstream in the flow system.
However, the physical or chemical conditions, e.g., chemical reactivity, thermal degradation, etc. which exist between the point at which the biocide may be added to the system and the point at which its biocidal effect is desired render the e~fective use of a biocide impossi~le.
Similarly, in a system experiencing relatively slow ~low, such as a paper mill, if a biocide is added at the beginnin~ of the system, its biocidal effect may be completely dissipated before it has reached all of the points at which this effect is desired or required. As a consequence, the bioclde must be added at a plurality of points, and even then a graduated ~ 3~ ~
biocidal effect will be experienced between one point o~ addition to the system and the next point downstream at which the biocides may be added. In addition to the increased cost of utilizing and maintaining plural feed points, gross ineconomies in respect to the cost of the biocide are experienced. Specifically, at each point o~ addition, an excess of the biocide is added to the system in order to compensate for that portion of the biocide which will be expended in reacting with other constituents present in the system or experience physical changes which impair its biocidal activity.
It is now known that the mixture of 75%
5-chloro-2-methyl-4-isothiazolin-3-one and 25%
2-methyl-4-isothiazolin 3-one which is sold under the trademark of Kathon-886 by Rohm and Haas may be blended with cert2in sulfones to produce a synergistic biocide. This is the subject matter of U.S. Patent No. 3,~29,561.
It is also known that Kathon-886 may be synergistically combined with either chlorine or chlorine dioxide to provide an improved microbiocide ~or treating aqueous systems of the type described above. This is described in U.S. Patent No. 47295,932.
Kathon-886 is effective at low dosages, e.g. a few parts per million, for treatin9 industrial systems contaminated with a wide variety o~ microorganiSmS. These microorganisms include bacteria, molds, fungi, yeast and algae. In many cases, however, in order to achieve good control of microbiological growth in industrial cooling systems, Kathon-886 must be used at high dosages, e.g. in excess of lO ppm. When such badly contaminated systems are treated with Kathon-886, it is relatively impossible to reduce the total count to a low level. Due to the high cost of Kathon-886, it is, therefore, not practical to use this ~'7~
material for controlling aqueous industrial systems which are heavily contaminated by microorganisms. Such systems containing heavy microorganism contamination are the type o~ system which bene~it most from the practice o~ the instant invention.
These heavily contaminated systems are often further characterized as containing large amounts of deposits which are composed of dea~ microorganism masses. In severe cases they can often have the appearance of bearded slimes.
THE INvENTIbN
The invention comprises a synergistic biocidal composition useful in treating industrial process waters to prevent and control the growth of microorganisms, which composition comprises:
A. ~rom 5 - 95~ by weight of 75%
5-chloro-2-methyl-4-isothiazolin-3-one and 25%
2-methyl-4-isothiazolin-3-one; and 8. from 95 - 5% by weight of 2-~thiocyanomethylthio)-benzothiazole.
This combination is effective at low dosages 7 e.g.
l-lOppm.
l Evaluation o~ the Invention I ~
The synergism of these two components is demonstrated by adding 2-(thiocyanomethylthio)-benzothiazole ~commercially known as TCMTB) and a mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one ~commercially known as Kathon) in varying ratios over a range of concentrations to liquid nutrient medium. In this study of the control of bacterial growth, the nutrient medium was tryptone glucose extract agar.
The concentrations of the above toxicants were added to aliquots o- medium at temperature of 50C. Once treated, the medium was poured into sterile Petri dishes and allowed to solidif~.
Each test plate was inoculated with a bacterial suspension containing 0.1 ml of a nutrient broth culture of Pseudomonas aeruginosa. After an incubation at 37C for over forty-eight hours, the lowest concentration of each toxicant or of each ratio of the combined toxicants that prevented growth on the agar was taken as the end point.
The end points of each of the ratios tested were then compared with end points of the concentrations of the pure toxicants. Syner~ism was determined according to the industrially-accepted method described by S. C. Kull, P. C.
Eisman9 H. D. Sylwestrowicz, and R. L. Mayer in ~pplied Microbiolo~, VolO 9, pages 538-541 (1936).
As regards the Kull, et al. document, the data here presented can be described as follows:
QA=the ppm of actives oE TC~TB alone which produced an end po;nt Qa=the ppm of actives of TCMTB, in combination, which produced an endpoint =the ppm of actives of Kathon alone which produced an endpoint Qb=the ppm of active~ of Kathont in combination, which proauced an endpoin~
if Qa ~ Qb ~ 1 indicates s~rnergy QA QB
> 1 indicates antagonis~
= 1 indicates additivity ~X7()~
TALLP: I
SYNERGISM STUDY FOR CO~!BINATION 3IOCID2S AGAINST BACTERIA
Growth: ~
No Growth: -Control Cultureo 3. 00 x 107 organisms ;?er ml F~atic~
TC. lTB/
KATElO~: __Co centrations (ppm~
0.3 0.6 1.0 1.5 3.0 5.~ 7.5 10 20 30 40 50 100~0 ~ ~ + ~ + ~ +
90/10 + ~ ~ ~ + +
10/gO + ~ + ~
75~25 +
2 5 ~ 7 5 ~ I +
5 ~ / 5 0 ~ + ~ + ~
Ratio Q~ + QP
TCMTB/RAT~ONQA QB
9U/10 0. 783 ~l Syn~rgy 10/90 0. 458 ~1 Synergy 75/25 0. 604 ~1 Synergy 25/7S 0. 394 <1 Synergy 50/50 0. 575 ~1 Synergy -1~04~
QA = 20 ppm active TCr~5TB
QB = 3 pprn active KATHOM
~. 90/10 . Q~ = 10 ppM X . 90 = 9 Qb ~ 10 ppm x .10 =~ 1 9 + 1- 0.783 Bo ln/90 Qa ~ 105 pp)~ X .la = 0.15 Qb ~ 1.5 ppm x .90 = 1035 O15 + ]. 35 - 0.458 C. 7~/25 Qa ~ S pprn x 0~75 = 3.75 Qb 5 PP~ x 0 . 2 5 - 1. Z 5 3O75 ~ 1.25 - 0.604 2U- 3~
D. 25~75 Qa = 1.5 ppm x 0.25 = .375 Qb = 1. 5 ppm x 0O 75 = 1.125 375 ~ 1ol25 = 0~394 . 20 3 Eo 50/50 52a ~ 3 ppm x 0. 50 - 1. 5 Qb = 3 pPm x 0. 50 = 1. 5 1.5 ~ 1.5 - 0.575
Claims (2)
1. A synergistic biocidal composition useful in treating industrial process waters to prevent and control the growth of microorganisms, which composition comprises:
A. from 5 - 95% by weight of 75%
5-chloro-2-methyl-4-isothiazolin-3-one and 25%
A. from 5 - 95% by weight of 75%
5-chloro-2-methyl-4-isothiazolin-3-one and 25%
2-methyl-4-isothiazolin-3-one; and B. from 95 - 5% by weight of 2-(thiocyanomethylthio)-benzothiazole.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US06/757,695 US4595691A (en) | 1985-07-22 | 1985-07-22 | Synergistic biocide of 2-(thiocyanomethylthio) benzothiazole with a mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one |
| US757,695 | 1985-07-22 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA1270418A true CA1270418A (en) | 1990-06-19 |
Family
ID=25048831
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA000514278A Expired - Fee Related CA1270418A (en) | 1985-07-22 | 1986-07-21 | Synergistic biocide of 2-(thiocyanomethyl-thio) benzothiazole with a mixture of 5-chloro-2-methyl-4- isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one |
Country Status (2)
| Country | Link |
|---|---|
| US (1) | US4595691A (en) |
| CA (1) | CA1270418A (en) |
Families Citing this family (43)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4732905A (en) * | 1987-03-13 | 1988-03-22 | Betz Laboratories, Inc. | Biocidal compositions and use thereof containing a synergistic mixture of 2-bromo-2-nitropropane-1,3-diol and a mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one |
| US4975109A (en) * | 1988-05-02 | 1990-12-04 | Lester Technologies Corp. | Microbiocidal combinations of materials and their use |
| US5256182A (en) * | 1988-05-02 | 1993-10-26 | Lester Technologies Corp. | Microbiocidal combinations of materials and their use |
| US4914118A (en) * | 1989-05-25 | 1990-04-03 | Betz Laboratories, Inc. | Biocidal compositions and use thereof containing a synergistic mixture of 2-(decylthio)ethanamine hydrochloride and a mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one |
| ZA908425B (en) * | 1989-11-03 | 1991-07-31 | Rohm & Haas | Synergistic microbicidal combinations |
| US5468759A (en) * | 1991-12-19 | 1995-11-21 | Rohm And Haas Company | Synergistic microbicidal combinations containing 4,5-dichloro-2-octyl-3-isothiazolone and certain commercial biocides |
| GB9003871D0 (en) * | 1990-02-21 | 1990-04-18 | Rohm & Haas | Stabilization of isothiazolones |
| US5063217A (en) * | 1990-08-13 | 1991-11-05 | Betz Laboratories, Inc. | Biocidal compositions and use thereof containing a synergistic mixture of n-tributyl tetradecyl phosphonium chloride and a mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiozolin-3-one |
| CA2058252A1 (en) * | 1991-03-18 | 1992-09-19 | Linda R. Robertson | Synergistic product selection test for biocides |
| US5198440A (en) * | 1991-09-05 | 1993-03-30 | Buckman Laboratories International, Inc. | Synergistic combinations of 2-(thiocyanomethylthio)-benzothiazole with hexahydro-1,3,5-tris(2-hydroxyethyl)-s-triazine in controlling fungal and bacterial growth in aqueous fluids |
| US5196443A (en) * | 1991-09-25 | 1993-03-23 | Buckman Laboratories International, Inc. | Synergistic combinations of 2-(thiocyanomethylthio) benzothiazole with a mixture of 4,4-dimethyloxazolidine and 3,4,4-trimethyloxazolidine in controlling fungal and bacterial growth in aqueous fluids |
| US5413795A (en) * | 1992-08-14 | 1995-05-09 | Buckman Laboratories, International, Inc. | TCMTB on a solid carrier in powdered form, method of manufacture and method of use |
| US5571443A (en) * | 1994-12-30 | 1996-11-05 | Buckman Laboratories International, Inc. | Synergistic combination of 2-(thiocyanomethylthio)benzothiazole and thiophanate compounds useful as fungicides |
| US5693631A (en) * | 1995-05-30 | 1997-12-02 | Buckman Laboratories International, Inc. | Potentiation of the microbicide 2-(thiocyanomethylthio) benzothiazole using an N-alkyl heterocyclic compound |
| FR2748267B1 (en) * | 1996-04-19 | 1999-04-23 | Assche Charles Jacques Van | NOVEL PROCESSES FOR BIOCIDAL TREATMENT OF INDUSTRIAL AND BATHING WATER BY APPLICATION OF SUBSTANCES INDUCING MORTALITY TO LIGHT |
| US6419879B1 (en) | 1997-11-03 | 2002-07-16 | Nalco Chemical Company | Composition and method for controlling biological growth using stabilized sodium hypobromite in synergistic combinations |
| US5922745A (en) * | 1997-11-03 | 1999-07-13 | Nalco Chemical Company | Composition and method for inhibiting the growth of microorganisms including stabilized sodium hypobromite and isothiazolones |
| US6322749B1 (en) | 1999-02-24 | 2001-11-27 | Nalco Chemical Company | Composition and method for inhibiting the growth of microorganisms including stabilized sodium hypobromite and isothiazolones |
| US6235299B1 (en) | 1998-02-27 | 2001-05-22 | Buckman Laboratories International Inc | Potentiation of biocide activity using diethanolamide |
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Family Cites Families (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3664821A (en) * | 1970-01-02 | 1972-05-23 | Betz Laboratories | Slimicidal composition and its use |
| US3929561A (en) * | 1975-03-03 | 1975-12-30 | Betz Laboratories | Synergistic compositions containing bis (trichloromethyl) sulfone and their use |
| US3928198A (en) * | 1975-03-06 | 1975-12-23 | Betz Laboratories | Synergistic compositions containing 2,2-dibromo-3-nitrilopropionamide and 3,3,4,4-tetrachlorotetrahydrothiopene-1,1-dioxide and their use |
| US4295932A (en) * | 1980-07-14 | 1981-10-20 | Naloc Chemical Company | Synergistic blend of biocides |
| US4285765A (en) * | 1980-09-24 | 1981-08-25 | Buckman Laboratories, Inc. | Slime control compositions and methods of using the same |
| US4479961A (en) * | 1984-01-23 | 1984-10-30 | Nalco Chemical Company | Synergistic fungicide/biocide of 2-(thiocyanomethylthio) benzothiazole and bis (trichloromethyl) sulfone |
-
1985
- 1985-07-22 US US06/757,695 patent/US4595691A/en not_active Expired - Lifetime
-
1986
- 1986-07-21 CA CA000514278A patent/CA1270418A/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| US4595691A (en) | 1986-06-17 |
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