Biocidal Compositions and Use Thereof Containing a Synergistic Mixture of 2-Bromo-2-Nitropropane-1,3-Diol and Tetradecyl Dimethyl Sulfonium Methosulfate

The formation of slimes by microorganisms is a problem that is encountered in many aqueous systems. For example, the problem is not only found in natural waters such as lagoons, lakes, ponds, etc. and confined waters as in pools, but also in such industrial systems as cooling water systems, air washer systems and pulp and paper mill systems. All possess conditions which are conducive to the growth and reproduction of slime-forming microorganisms. In both once-through and recirculating cooling systems, for example, which employ large quantities of water as a cooling medium, the formation of slime by microorganisms is an extensive and constant problem.

Airborne organisms are readily entrained in the water from cooling towers and find this warm medium an ideal environment for 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 of the cooling system. The slime formation not only aids in the deterioration of the tower structure in the case of wooden towers, but also, by its deposition on metal surfaces, promotes corrosion, In addition, slime carried through the cooling system plugs and fouls lines, valves, strainers, etc. and deposits on heat exchange surfaces. In the latter case, the impedance of heat transfer can greatly reduce the efficiency of the cooling system.

In pulp and paper mill systems, slime formed by microorganisms is commonly encountered and causes fouling, plugging, or corrosion thereof. The slime also becomes entrained in the paper produced to cause breakouts on the paper machines, with consequent work stoppages and the loss of production time, and/or is responsible for unsightly blemishes in the final product, which result in rejects 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, chlorinated phenols, organo-bromines, and various organo-sulfur compounds. All of these compounds are generally useful for this purpose but each is attended by a variety of impediments. For example, chlorination is limited both by its specific toxicity for slime-forming organisms at economic levels and by the tendency of chlorine to react, which results in the expenditure of the chlorine before its full biocidal function is 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 compound has achieved a clearly established predominance in respect to the applications discussed. Likewise, lagoons, ponds, lakes, and even pools, either used for pleasure purposes or used for industrial purposes for the disposal and storage of industrial wastes, become, during the warm weather, beseiged by slime due to microorganism growth and reproduction. In the case of the recreational areas the problem of infection 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 material's use or disposal of the waste.

Naturally, economy is a major consideration in respect to all of these biocides. Such economic considerations attach to both the cost of the biocide 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, the duration of its biocidal or biostatic effect in the system treated, and the ease and frequency of its addition to the system treated. To date, none of the commercially available biocides has exhibited a prolonged biocidal effect. Instead, their effectiveness is rapidly reduced as the result of exposure to physical conditions such as temperature, association with ingredients contained by the system toward which they exhibit an affinity or substantivity, etc., with a resultant restriction or elimination of their biocidal effectiveness, or by dilution.

As a consequence, the use of such biocides involves their continuous or frequent addition to systems to be treated and their addition to a plurality of points or zones in the systems to be treated. Accordingly, the cost of 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 effective use of a biocide. For example, if in a particular system there is no access to an area at which slime formation occurs the biocide can 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 biodical effect is desired render the effective use of a biocide impossible.

Similarly, in a system experiencing relatively slow flow, such as a paper mill, if a biocide is added at the beginning 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 biocide must be added at a plurality of points, and even then a diminishing biocidal effect will be experienced between one point of 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 of 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.

The biocidal compositions of the present invention comprise, as active ingredients, (1) 2-bromo-2-nitropropane-1,3-diol (hereinafter "BNPD") and (2) a trialkyl sulfonium salt such as tetradecyl dimethyl sulfonium methosulfate (TDSM).

BNPD is sold by The Boots Company, Ltd., Nottingham, England, as an industrial water treatment antibacterial agent.

TDSM is sold by Metal and Thermit.

Surprisingly, the present inventors have found that a composition comprising BNPD and TDSM is especially efficacious in controlling the growth of bacterial microbes, specifically the Klebsiella pneumoniae species. This particular species is a member of the capsulated, facultative class of bacteria and is generally present in air, water and soil. These bacteria continually contaminate open cooling systems and pulping and papermaking systems and are among the most common slime formers. This slime may be viewed as being a mass of agglomerated cells stuck together by the cementing action of the gelatinous polysaccharide or proteinaceous secretions around each cell. The slimy mass entraps other debris, restricts water flow and heat transfer, and may serve as a site for corrosion.

The fact that the Klebsiella species used in the tests is a facultative species is important as, by definition, such bacteria may thrive under either aerobic or anaerobic conditions. Accordingly, by reason of demonstrated efficacy in the growth inhibition of this particular species, one can expect similar growth inhibition attributes when other aerobic or anaerobic bacterial species are encountered.

As above noted, BNPD is available from The Boots Company, Ltd. and is sold under the trademarks "Myacide AS" or "Bronopol." It is a white free flowing crystalline solid that is readily soluble in cold water. The product is from about 95-100% pure.

In accordance with the present invention, the combined BNPD:TDSM treatment may be added to the desired aqueous system in need of biocidal treatment, in an amount of from about 0.1 to about 200 parts of the combined treatment to one million parts (by weight) of the aqueous medium. Preferably, about 5 to about 50 parts of the combined treatment per one million parts (by weight) of the aqueous medium is added.

The combined treatment is added, for example, to cooling water systems, paper and pulp mill systems, pools, ponds, lagoons, lakes, etc., to control the formation of bacterial microorganisms, which may be contained by, or which may become entrained in, the system to be treated. It has been found that the BNPD/TDSM compositions and methods of utilization of the treatment are efficacious in controlling the facultative bacterium, Klebsiella pneumoniae, which may populate these systems. It is thought that the combined treatment composition and method of the present invention will also be efficacious in inhibiting and controlling all types of aerobic and anaerobic bacteria.

Surprisingly, it has been found that when the BNPD/TDSM ingredients are mixed, in certain instances, the resulting mixtures possess a higher degree of bactericidal activity than that of the individual ingredients comprising the mixture. Accordingly, it is possible to produce a highly efficacious bactericide. Because of the enhanced activity of the mixture, the total quantity of the bacterial treatment may be reduced. In addition, the high degree of bactericidal effectiveness which is provided by each of the ingredients may be exploited without use of higher concentrations of each.

The following experimental data were developed. It is to be remembered that the following examples are to be regarded solely as being illustrative, and not as restricting the scope of the invention.

BNPD and TDSM were added in varying ratios and over a wide range of concentrations to a liquid nutrient medium which was subsequently inoculated with a standard volume of a suspension of the facultative bacterium Klebsiella pneumoniae. Growth was measured by determining the amount of radioactivity accumulated by the cells when .sup.14 C-glucose was added as the sole source of carbon in the nutrient medium. The effect of the biocide chemicals, alone and in combination, is to reduce the rate and amount of .sup.14 C incorporation into the cells during incubation, as compared to controls not treated with the chemicals. Additions of the biocides, alone and in varying combinations and concentrations, were made according to the accepted "checkerboard" technique described by M. T. Kelley and J. M. Matsen, Antimicrobial Agents and Chemotherapy. 9: 440, (1976). Following a two hour incubation, the amount of radioactivity incorporated in the cells was determined by counting (.sup.14 C liquid scintillation procedures) for all treated and untreated samples. The percent reduction of each treated sample was calculated from the relationship: ##EQU1##

Plotting the % reduction of .sup.14 C level against the concentration of each biocide acting alone results in a dose-response curve, from which the biocide dose necessary to achieve any given % reduction can be interpolated.

Synergism was determined by the method of calculation described by F. C. Kull, P. C. Eisman, H. D. Sylwestrowicz and R. L. Mayer, Applied Microbiology 9, 538, (1961) using the relationship: ##EQU2## where: Q.sub.a =quantity of compound A, acting alone, producing an end point

Q.sub.b =quantity of compound B, acting alone, producing an end point

Q.sub.A =quantity of compound A in mixture, producing an end point

Q.sub.B =quantity of compound B in mixture, producing an end point

The end point used in the calculations is the % reduction caused by each mixture of A and B. Q.sub.A and Q.sub.B are the individual concentrations in the A/B mixture causing a given % reduction. Q.sub.a and Q.sub.b are determined by interpolation from the respective dose-response curves of A and B as those concentrations of A and B acting alone which produce the same % reduction as each specific mixture produced.

Dose-response curves for each active acting alone were determined by linear regression analysis of the dose-response data. Data were fitted to a curve represented by the equation shown with each data set. After linearizing the data, the contributions of each biocide component in the biocide mixtures to the inhibition of radioisotope uptake were determined by interpolation with the dose response curve of the respective biocide. If, for example, quantities of Q.sub.A plus Q.sub.B are sufficient to give a 50% reduction in .sup.14 C content, Q.sub.a and Q.sub.b are those quantities of A or B acting alone, respectively, found to give 50% reduction in .sup.14 C content. A synergism index (SI) is calculated for each combination of A and B.

Where the SI is <1, synergism exists. Where the SI=1, additivity exists. Where SI>1, antagonism exists.

The data in the following tables come from treating Klebsiella pneumoniae, a common nuisance bacterial type found in industrial cooling waters and in pulping and paper making systems, with varying ratios and concentrations of BNPD and TDSM. Shown for each combination is the % reduction of .sup.14 C content, the calculated SI, and the weight ratio of BNPD to TDSM.

In Tables I and II, differences seen between the replicates are due to normal experimental variance.

In accordance with Tables I-II supra., unexpected results occurred more frequently within the ratios of BNPD:TDSM product of from about 16:1 to 1:4. At present, it is preferred that any commercial product embodying the invention comprises a weight ratio of active component of about 1:1 BNPD:TDSM.

While we have shown and described herein certain embodiments of the present invention, it is intended that there be covered as well any change or modification therein which may be made without departing from the spirit and scope of the invention.