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PATENT NUMBER 5,128,045 
Method for stabilizing metal ions in the presence of biofouling organisms

United States Patent 5,128,045
Parsons ,   et al. July 7, 1992

Abstract

A method for stabilizing metal ions in recirculating water systems is disclosed. This method utilizes an admixture comprising a) an ethylenically unsaturated water-soluble polymer and/or a water soluble phosphonate, b) methylene bis(thiocyanate), and c) 2-(thiocyanomethylthio)benzothiazole to solubilize metal ions thereby reducing deposition and corrosion.


Inventors: Parsons; Jennifer R. (Pittsburg, PA); Bendiksen; Beverly (Coraopolis, PA); Schell; Charles J. (Coraopolis, PA)
Assignee: Calgon Corporation (Pittsburgh, PA)
Appl. No.: 616143
Filed: November 20, 1990

 

Current U.S. Class: 210/699; 210/700; 210/701; 252/180; 514/515
Intern'l Class: C02F 001/50
Field of Search: 71/67 210/698-701,764 252/180,181 514/514,515

References Cited [Referenced By]


U.S. Patent Documents

3674457 Jul., 1972 Wolfson 514/515.
3898343 Aug., 1975 Swered et al. 514/515.
4324793 Apr., 1982 Hagen et l. 514/387.
4552665 Nov., 1985 Ralston et al. 210/701.
4612328 Sep., 1986 Jakubowski 514/515.
4719083 Jan., 1988 Baker et al. 210/698.

Primary Examiner: Hruskoci; Peter
Attorney, Agent or Firm: Mitchell; W. C., Caruso; C. M.
 

Claims




What is claimed is:

1. A method for stabilizing metal ions including iron and manganese and inhibiting biofouling in an aqueous system comprising adding to said aqueous system an effective amount of an admixture comprising:

(a) an ethylenically unsaturated water soluble polymer, alone or in combination with a water soluble phosphonate, wherein said polymer has a weight average molecular weight of less than 50,000 as determined by light scattering and comprises (i) an unsaturated mono-carboxylic acid selected form the group consisting of acrylic acid and methacrylic acid; and (ii) an unsaturated sulfonic acid selected from the group consisting of 2-acrylamido-2-methylpropyl sulfonic acid and 2-methacrylamido-2-methylpropyl sulfonic acid; wherein the weight ratio of (i): (ii) ranges from about 1:4 to about 4:1;

(b) methylene bis(thiocyanate); and

(c) 2-(thiocyanomethylthio)benzothiazole; wherein the weight ratio of a) to the sum of b) and c) is from about 20:1 to about 1:2 and wherein the weight ratio of b):c) is from about 10:1 to about 1:99, to prevent deposition of said metal ions and inhibit biofouling in said aqueous system.

2. The method of claim 1, wherein said phosphonate is selected from the group consisting of 2-phosphono-1,2,4-tricarboxybutane, amino tri(methylene phosphonic acid), hydroxyethylidene diphosphonic acid, phosphonosuccinic acid, benzene phosphonic acid, 2-aminoethyl phosphonic acid, and polyamino phosphonates.

Description




BACKGROUND OF THE INVENTION

Many metal ions are essentially insoluble in aqueous systems having pH's ranging from approximately 6.0 to 9.0. Within this pH range, these metals, including but not limited to iron, zinc, aluminum and manganese, will deposit on heat transfer surfaces causing underdeposit attack.

Recirculating cooling water utilized in industrial applications may contain metal ions, such as iron and manganese which, upon deposition as insoluble salts on heat transfer surfaces, cause decreased operating efficiency and corrosive attack.

These concerns are particularly pertinent to recirculating cooling water systems employed by large utility plants.

Water treatment to prevent scale, corrosion and biological fouling in industrial and municipal aqueous systems is a complicated problem under the best of circumstances. Cooling water in utility plants, for example, may be particularly difficult to treat, especially when the source water contains high concentrations of iron and/or manganese. Also, such plants may be operated at several cycles of concentration. The resulting high levels of iron and manganese pose a challenge to conventional polymer treatment programs designed to stabilize these metals and prevent or inhibit deposits. The added problem of the presence of fouling microorganisms such as bacteria, particularly sulfate reducing bacteria, in the recirculating water generally mandates the use of an aggressive biological treatment program. Balancing the whole range of treatment needs makes it desirable that treatment additives not be antagonistic to one another. Of course, the treatment approach utilized must also take into account the extremes of plant operating parameters such as water quality, pH, cycles of concentration and temperature. All of these factors must be considered to determine the performance limits of any treatment additives utilized.

Polymers and phosphonates, alone and in combination, have been used in the past to stabilize deposit-forming metals ions such as Fe.sup.2+, Fe.sup.3+, and Mn.sup.2+. See for example U.S. Pat. Nos. 4,936,987, 4,640,793, 4,783,267 and 4,552,665. For many cooling towers, chlorine has been used as the biocide. Unfortunately, such biocides may inhibit the ability of polymer and/or phosphonate programs to stabilize metal ions. The instant inventors have surprisingly found that combinations of methylene bis(thiocyanate) and 2-(thiocyanomethylthio)benzothiazole, conventional biocides, enhance the ability of conventional water treatment polymers and/or phosphates to stabilize metal ions. This benefit of the instant biocide compositions is surprising and unexpected.

Hence, a long-felt need in the art of water treatment to find an effective biocide which does not antagonize metal ions stabilization by polymers and/or phosphonates has been met.

The use of methylene bis(thiocyanate) is well known in the art. See, for example, U.S. Pat. Nos. 4,612,328, 3,996,378, 3,300,375 and 3,524,871. However, its surprising effect on the ability of polymers and/or phosphonates to stabilize metal ions is not known or suggested in the art. Calgon product H-102 is a blend of 10% methylene bis(thiocyanate) and 10% 2-(thiocyanomethylthio)benzothiazole, on an active weight basis.

SUMMARY OF THE INVENTION

The present invention is directed to an admixture for the control, prevention and/or inhibition of biofouling and for the stabilization of metal ions, particularly iron and manganese ions, in an aqueous system comprising a) an ethylenically unsaturated water soluble polymer and/or a water soluble phosphonate, b) methylene bis(thiocyanate) and c) 2-(thiocyanomethylthio)benzothiazole.

The present invention is also directed to a method for stabilizing metal ions in the presence of biofouling organisms, and for controlling, preventing and/or inhibiting biofouling comprising adding to an aqueous system containing metal ions and biofouling organisms an effective amount of an admixture comprising a) an ethylenically unsaturated, water soluble polymer and/or a water soluble phosphonate, b) methylene bis(thiocyanate) and c) 2-(thiocyanomethylthio)benzothiazole.

The present invention is further directed to a method for enhancing the ability of water soluble ethylenically unsaturated polymers and/or phosphonates to stabilize metal ions in aqueous systems prone to biofouling comprising adding an effective amount of methylene bis(thiocyanate) and 2-(thiocyanomethylthio)benzothiazole to said polymers and/or phosphonates or to an aqueous system treated with said polymers and/or phosphonates.

As used herein, the term "aqueous system" is meant to include any system containing water, including but not limited to cooling water systems, boiler water systems, desalination systems, gas scrubber systems, blast furnace systems, sewage sludge thermal conditioning systems, reverse osmosis systems, evaporators, paper processing systems, mining circuits, etc. The preferred aqueous systems are cooling water systems, either once-through or closed loop.

The term "stabilizing metal ions", as used herein, refers to the ability of additives to keep metal ions in solution under conditions where, absent the additive, the ions would tend to precipitate out of solution. Thus, these additives either solubilize ions or maintain ions in a soluble state, thereby inhibiting the formation and/or deposition of metallic salts on to the surfaces of aqueous systems.

The term "effective amount", as used herein, refers to the amount of additive necessary to accomplish the objective for which the additive is being used in a given aqueous system.

The instant inventors have discovered that methylene bis(thiocyanate)/2-(thiocyanomethylthio)benzothiazole compositions enchance the ability of conventional water treatment polymers and phosphonates to stabilize metal ions. This use of such compositions is surprising and unexpected.

DETAILED DESCRIPTION OF THE INVENTION

In the broadest sense, the instant invention relates to compositions comprising: a) a water soluble, ethylenically unsaturated polyer and/or a water soluble phosphonate; b) methylene bis(thiocyanate); and c) 2-(thiocyanomethylthio)benzothiazole, wherein the polymer to phosphonate weight ratio of a), if a phosphonate is used, ranges from about 99:1 to about 1:99 and wherein the weight ratio of a) to the sum of b) and c) ranges from about 99:1 to about 1:99. Also, the weight ratio of b) to c) ranges from about 99:1 to about 1:99. Additionally, such compositions may comprise the water of an aqueous system, wherein said water contains metal ions selected from the group consisting of Fe.sup.+2, Fe.sup.+3, Zn.sup.+2, Al.sup.+3, and Mn.sup.+2 and biofouling organisms.

More particularly, the instant invention is directed to a method for stabilizing metal ions in the presence of biofouling organisms and for controlling, preventing and/or inhibiting biofouling, comprising adding to an aqueous system containing metal ions and biofouling organisms an effective amount of a composition comprising: a) a water soluble, ethylenically unsaturated polymer and/or a water soluble phosphonate; b) methylene bis(thiocyanate); and c) 2-(thiocyanomethylthio)benzothiazole.

Further, the instant invention is directed to improved ethylenically unsaturated, water soluble polymer/water soluble phosphonate compositions which additionally comprise methylene bis(thiocyanate) and 2-(thiocyanomethylthio)benzothiazole and to a method for enhancing the ability of polymer and/or phosphonate compositions to stabilize metal ions in aqueous systems comprising adding to such compositions or to aqueous systems in which they are present an effective amount of a composition comprising methylene bis(thiocyanate) and 2-(thiocyanomethylthio)benzothiazole.

The instant invention also relates to an improved method for treating an aqueous system, preferably a recirculating cooling water system, which method comprises adding to the system being treated an effective amount of a composition comprising: a) an ethylenically unsaturated water soluble polymer and/or a water soluble phosphonate; b) methylene bis(thiocyanate); and c) 2-(thiocyanomethylthio)benzothiazole.

Any ethylenically unsaturated, water-soluble polymer may be used as component (a). For example, water soluble polycarboxylates may be used. Such polycarboxylates include, but are not limited to, polymers derived from acrylic acid, methyacrylic acid, vinyl acetic acid, allyl acetic acid, fumaric
 
Specific examples of acceptable polymers include homopolymers of acrylic acid or methacrylic acid, copolymers of acrylic acid and methacrylic acid, homopolymers of maleic acid or anhydride, copolymers of any of the above monomers with acrylamide or methacrylamide, hydrolyzed polyacrylamides, copolymers of acrylic acid and hydroxypropyl acrylate, copolymers of maleic acid or anhydride and sulfonated styrene and sulfonated polystyrenes.

A preferred polymer is a water soluble polymer having a weight average molecular weight of less than about 50,000 as determined by low angle laser light scattering comprising i) an unsaturated carboxylic acid selected from the group consisting of acrylic acid, methacrylic acid, .alpha.-halo acrylic acid, maleic acid or anhydride, itaconic acid or anhydride, vinyl acetic acid, allyl acetic acid, fumaric acid, .beta.-carboxyethyl acrylate, their salts, and mixtures thereof, and ii) an unsaturated sulfonic acid selected from the group consisting of 2-acrylamido-2-methylpropylsulfonic acid, 2-methacrylamido-2-methylpropylsulfonic acid, vinyl sulfonic acid, sulfoalkyl acrylate, sulfoalkyl methacrylate, allyl sulfonic acid, methally sulfonic acid, and 3-methacrylamido-2-hydroxypropyl sulfonic acid.

Such preferred polymers may also comprise iii) an unsaturated polyalkylene acid moiety, such as allyl polyethylene glycol, methally polyethylene glycol, polyethylene glycol acrylate, polyethylene glycol methacrylate, methoxy allyl polyethylene oxide, alkoxyallyl polyethylene oxide and the polypropylene equivalents thereof. Also, mixtures of polyethers formed from polyethylene oxide with other polyalkylene oxides, such as propylene or butylene oxide may be used. The polyether chain may be capped with an alkyl, aralkyl, sulfonate or phosphonate group, a metal ion, or uncapped.

If moiety iii) is used, the polymer preferably comprises about 35 to about 90% by weight, i), about 5 to about 40%, by weight, ii), and about 5 to about 40%, by weight, iii).

More preferred polymers are selected from the group consisting of the following water soluble polymers: homopolymers of acrylic acid, homopolymers of methylacrylic acid, homopolymers of maleic acid or anhydride, polymers comprising i) acrylic acid, methacrylic acid or maleic acid and ii) acrylamide or methacrylamide, hydrolyzed polyacrylamides, polymers comprising i) acrylic acid and ii) hydroxy propyl acrylate, polymers comprising i) maleic acid and ii) sulfonated styrene, sulfonated polystyrenes and polymers comprising i) acrylic acid or methacrylic acid and ii) 2-acrylamido-2-methylpropyl sulfonic acid or 2-methacrylamido-2-methylpropyl sulfonic acid. These preferred polymers are water soluble and have molecular weights of less than about 50,000 as determined by light scattering techniques.

The most highly preferred polymers are selected from the group consisting of water-soluble polymers having a weight average molecular weight of less than 50,000 as determined by light scattering comprising:

(i) an unsaturated mono-carboxylic acid selected from the group consisting of acrylic acid and methacrylic acid; and

(ii) an unsaturated sulfonic acid selected from the group consisting of 2-acrylamido-2-methylpropyl sulfonic acid and 2-methacrylamido-2-methylpropyl sulfonic acid;

wherein the weight ratio of (i):(ii) ranges from about 1:4 to about 4:1. Such polymers are commerically available from Calgon Corporation, Pittsburgh, Pa. as TRC-233.RTM..

Any water soluble phosphonate may additionally be used with the above polymers as a portion of component (a). Examples include, but are not limited to, 2-phosphono-1,2,4-tricarboxybutane, amino tri(methylene phosphonic acid), hydroxyethylidene diphosphonic acid, phosphonosuccinic acid, benzene phosphonic acid, 2-aminoethyl phosphonic acid polyamino phosphonates and the like. Additional phosphonates are identified in U.S. Pat. No. 3,837,803, which is hereby incorporated by reference. The preferred phosphonates are 2-phosphono-1,2,4-tricarboxybutane, amino tri(methylene phosphonic acid) and hydroxyethylidene diphosphonic acid, all of which are commercially available. If a phosphonate is used, the ratio of polymer to phosphonate, on an active weight basis, should range from about 99:1 to about 1:99, preferably from about 50:1 to about 1:50, and most preferably from about 20:1 to about 1:20.

Component (b) is methylene bis(thiocyanate) (hereinafter also referred to as MBT). MBT is commerically available from Calgon Corporation, Pittsburgh, Pa. Component (c) is 2-(thiocyanomethylthio)benzothiazole.

The weight ratio of component a) to the sum of components b) and c) in the instant admixtures ranges from about 99:1 to about 1:99, preferably from about 50:1 to about 1:20, and most preferably from about 20:1 to about 1:10. The weight ratio of component b) to component c) should range from about 99:1 to about 1:99, preferably from about 50:1 to about 1:50. Preferably, the amount of b) and c) necessary is determined based upon the characteristics of the aqueous system to be treated, such as its potential for biofouling, and the concentration of metal ions present. It should be noted that virtually any amount of b) and c) is believed to enhance the efficiacy of polymer and/or phosphonate compositions with respect to metal ion stabilization. However, an enhancing amount may be inadequate to control biofouling. Most preferably, the weight ratio of components b) and c) to component a) ranges from about 10:1 to about 1:20.

An effective amount of the instant composition should be used, based on the characteristics of the system being treated. Preferably, at least about 0.1 ppm of the instant composition should be used, more preferably about 1 to about 100 ppm. Order of addition is not believed to be critical. Thus, the individual components of a), and components b) and c) may be added, separately or in some combination thereof, to the aqueous system being treated. Methods of addition are well known to those skilled in the art of water treatment.

Exemplary of the best mode is addition of an effective amount for a given system of a composition comprising:

a) Calgon polymer TRC-233 which is a 60/40 w/w acrylic acid/AMPSA copolymer, and HEDP (hydroxyethylidene diphosphonic acid) at a weight ratio ranging from about 10:1 to about 1:1;

b) MBT; and

c) 2-(thiocyanomethylthio)benzothiazole; wherein the weight ratio of a):b) ranges from about 20:1 to about 1:2 and wherein the weight ratio of b):c) ranges from about 10:1 to about 1:10.

EXAMPLES

The following examples are intended to further demonstrate the invention, They are not, however, intended to limit the invention in any way.

METAL STABILIZATION TESTS

Base Water Preparation

Synthetic recirculating water was prepared based on that of a large utility plant operating at three cycles of concentration. The synthetic cooling tower water contained 9 ppm iron and 3 ppm manganese, with the remaining dissolved solids listed in Table 1. To facilitate the setup of several stabilization tests, the base water was prepared in ten liter batches by adding MgSO.sub.4, CaCl.sub.2.H.sub.2 O, CaSO.sub.4 and NaHPO.sub.4 to 10 L of distilled, deionized water. The weights of these salts are listed in Table 1.


 

                  TABLE 1
    ______________________________________
    SYNTHETIC 3X RECIRCULATING WATER
           Synthetic Water
           Ion Concentration
    Ion    (mg/L)        Ion Source   g per 10 L
    ______________________________________
    Mg.sup.++
           39            MgSO.sub.4   1.926
    Ca.sup.++
           150           CaCl.sub.2.H.sub.2 O
                                      2.664
                         CaSO.sub.4   2.673
    PO.sub.4.sup.3-
           3             Na.sub.2 HPO.sub.4
                                      0.043
    HCO.sub.3
           305           NaHCO.sub.3  .sup.a 2.754
    SiO.sub.2
           36            Na.sub.2 SiO.sub.3.9H.sub.2 O
                                      .sup.b 0.568
    SO.sub.4.sup.2-
           340           MgSO.sub.4   --
                         CaSO.sub.4   --
    Cl.sup.-
           128.5         CaCl.sub.2.2H.sub.2 O
                                      --
    Na.sup.+
           131           Na.sub.2 HPO.sub.4
                                      --
                         NaHCO.sub.3  --
                         Na.sub.2 SiO.sub.3.9H.sub.2 O
                                      --
    ______________________________________
     .sup.a added from a 84 g NaHCO.sub.3 /L solution (5 ml/1000 ml)
     .sup.b added from a 34.08 g Na.sub.2 SiO.sub.3.9H.sub.2 O/L solution (5
     ml/1000 ml)
 



Test Procedure

The test apparatus consisted of one liter beakers and gang stirrers. The base water was added to the beakers, followed by 5 mL of 34.8 g/L Na.sub.2 SiO.sub.3.9H.sub.2 O and 5 mL of 1.0M NaHCO.sub.3. The chemical treatment and biocide, if present, were added next from 20 g/L product solutions. The next component added was chlorine to accelerate the oxidation of the metals, especially manganese. It was pipetted from a freshly prepared solution of 190.5 g/L Clorox, standardized before use. Iron and manganese were then added from atomic absorption reference standards (1 mL/1000 mL=1 ppm metal ion). The total test volume was 1000 mL at the end of these additions and the pH was then adjusted to 8.5 with 1.0N NaOH. The beakers were placed under a gang stirrer at room temperature at 60 rpm for 24 hours, after which time they were removed and an aliquot filtered through Whatman 41 filter paper (25 .mu.m filter paper). A 50 mL sample of the filtrate was digested with 0.25 mL concentrated nitric acid and 2.5 mL concentrated HCl.

Atomic absorption analysis was used to determine the concentration of Fe.sup.3+ and Mn.sup.2+. Percent stabilization of the metals was calculated using the following equation: ##EQU1##

A summary of the abbreviations for various polymers, phosphonate and biocides utilized in the examples is shown in Table 2.

 

                  TABLE 2
    ______________________________________
    PRODUCT DESCRIPTIONS
              ACTIVE           %        FUNC-
    ADDITIVE  INGREDIENT(S)    ACTIVE   TION
    ______________________________________
    AMP       Amino tri(methylene
                               5.0      Phos-
              phosphonic acid)          phonate
    MBT/      Methylene bis(thiocyanate)
                               10       Biocide
    TCMTB     and 2-(Thiocyanomethyl-
                               10
              thio)-benzothiazole,
              available from Calgon
              as H-102
    DMAC      Dodecyl dimethyl 50       Biocide
              ammonium chloride
    DGH       Dodecylguanidine 12.50    Biocide
              hydrochloride
    GLU       Gluteraldehyde   45       Biocide
    DBNPA     2,2-Dibromo-3-   5        Biocide
              nitrilopropionamide
    PENETRANT The penetrant is an
              admixture of various
              surfactants and
              polyacrylic acid, available
              from Calgon as CL-361
    KATH0N*   5-Chloro-2-methyl-4-
                               1.15     Biocide
              isothiazoline-3-one and
              2-methyl-4-isothiazoline-
                               0.35
              3-one
    NaBr      Sodium Bromide   46       Biocide
    AA/AMPSA  Composition containing a
                               20       Polymer/
    HEDP      60/40 w/w acrylic acid/
                               3.7      Phos-
              2-acylamindo-2-methyl     phonate
              propyl sulfonic acid
              polymer and
              hydroxyethylidene diphos-
              phonic acid, commercially
              available from Calgon
              as PCL-402
    AA/AMPSA  60/40 acylic acid/2-
                               30       Polymer
              acylamindo 2-
              methylpropyl sulfonic acid
              polymer, MW approx.
              8200
    HEDP      Hydroxyethylidene
                               60       Phos-
              diphosphonic acid         phonate
    MI        Methylisothiazoline       Biocide
    ______________________________________
     (*KATHON is a registered trademark of Rohm and Haas)
 



EXAMPLES 1-14

The test procedure was followed by employing a polymer and/or phosphonate and one of various biocides including H-102, DMAC, DGH, or DBNPA. The penetrant was also used. The results are shown in Table 3.

 

                  TABLE 3
    ______________________________________
    IRON/MANGANESE STABILIZATION BY H-102 BIOCIDE
    ______________________________________
    Example PCL-402  PENETRANT   H-102 % Stabilization
    Number  (mg/L)   (mg/L)      (mg/L)
                                       Fe    Mn
    ______________________________________
    1       50       15          21    85    100
    2       50       15          --    48    38
    3       50       --          21    72    87
    4       50       --          --    27    22
    5       50        5           6    61    59
    ______________________________________
     Conditions: Synthetic 3X Recirculating Water: pH 8-9; 9.0 mg/L Fe; 3.0
     mg/L Mn; 5.0 mg/L Cl.sub.2 ; 24 Hours; 60 rpm; 60.degree. C.; 25 micron
     Filtration.



                               ADDI-   %
           PCL-    PENE-           TIONAL  STABILI-
    Example
           402     TRANT    DMAC   BIOCIDE ZATION
    Number (mg/L)  (mg/L)   (mg/L) (mg/L)  Fe   Mn
    ______________________________________
     6     50      5.1      7.5    --      71   88
     7     50      5.1      6.0    --      78   89
     8     50      5.1      4.5    --      79   84
     9     50      5.1      3.0    --      84   91
    10     50      --       7.5    --      80   91
    11     50      5.1      --     --      100  95
    12     50      5.1      7.5    15 H-102
                                           92   89
    13     50      5.1      7.5    15 DBNPA
                                           74   89
    14     50      5.1      7.5    15 DGH  90   91
    ______________________________________
     Conditions: Synthetic 3X Recirculating Water: pH 8.5; R.T.; 24 hrs; 9 mg/
     Fe; 3 mg/L Mn; 5 mg/L Cl.sub.2 ; 25 micron Filtration.
 



EXAMPLES 15-20

The previously described test procedure was followed and the effect of increasing the test period from 24 to 48 hours was examined. As shown in Table 4, neither AA/AMPSA nor the PCL-402 combinations were affected by such an increase in time.

 

                                      TABLE 4
    __________________________________________________________________________
    Effect of Time on Fe.sup.2+  and Mn.sup.2+  Stabilization
                                                   Corrected
                                                   % Stabilization
    Example Number
             mg/L
                 Treatment
                        Time (Hrs.)
                              PENETRANT (mg/L)
                                          mg/L
                                              Biocide
                                                   Fe  Mn
    __________________________________________________________________________
    15       50  PCL-402
                        48    5.1         6   MBT  94  100
                                          9   DBNPA
    16       14.3
                 AA/AMPSA
                        48    5.1         6   MBT  92  100
             30  PCL-402                  9   DBNPA
    17       35.7
                 AA/AMPSA
                        48    5.1         6   H-102
                                                   76  85
                                          9   DBNPA
    18       3.33
                 HEDP   48    5.1         6   MBT  13  11
                                          9   DBNPA
    19       35.7
                 AA/AMPSA
                        24    5.1         6   MBT  90  89
                                          9   DBNPA
    20       3.33
                 HEDP   24    5.1         6   MBT  15  17
                                          9   DBNPA
    __________________________________________________________________________
     Conditions: Synthetic 3X Recirculating Water: pH 8-9; 9.0 mg/L Fe; 3.0
     mg/L Mn; 5.0 mg/L Cl.sub.2 ; 24 Hours; 60 rpm; 60.degree. C.; 25 micron
     Filtration.
 



EXAMPLES 21-24

The previously described test procedure was followed at 10.degree. C. and at room temperature. As shown in Table 5, the reduced temperature had no impact on iron and manganese stabilization.

 

                                      TABLE 5
    __________________________________________________________________________
    IRON/MANGANESE STABILIZATION COLD WATER STUDY
    Example
         Temp.
             AA/AMPSAA-HEDP
                         PENETRANT
                                 H-102
                                     % Stabilization
    Number
         (.degree.C.)
             (mg/L)      (mg/L)  (mg/L)
                                     Fe  Mn
    __________________________________________________________________________
    21   10  10          0       0   100 100
    22   10  10          3.4     4   100 100
    23   R.T.
             10          0       0    97 100
    24   R.T.
             10          3.4     4    96 100
    __________________________________________________________________________
     Conditions: Primary Service Water; pH 7.0; 4 hrs; 5 mg/L Cl.sub.2 ; 3 mg/
     Fe; 1 mg/L Mn; 25 micron Filtration.
 



Table 6, below, summarizes the effects of various biocides on iron and manganese stabilization.

 

                  TABLE 6
    ______________________________________
    EFFECTS OF SELECTED BIOCIDES
    ON FE/MN STABILIZATION
    IN 3X RECIRCULATING WATER
                    Effect on
                    Stabilization
    Biocide(s)        Fe     Mn
    ______________________________________
    H-102             +      +
    DMAC              -      0
    DGH               0      0
    DMAC/MBT          0      0
    DMAC/DBNPA        -      0
    DMAC/DGH          0      0
    MI/DBNPA          0      0
    DGH/DBNPA         0      0
    ______________________________________
     (+ = Positive
     - = Negative
     0 = Neutral)
 


 

 

 

 

 

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