AU2008200033A1 - Compositions for removing metal ions from aqueous process solutions and methods of use thereof - Google Patents

Compositions for removing metal ions from aqueous process solutions and methods of use thereof Download PDF

Info

Publication number
AU2008200033A1
AU2008200033A1 AU2008200033A AU2008200033A AU2008200033A1 AU 2008200033 A1 AU2008200033 A1 AU 2008200033A1 AU 2008200033 A AU2008200033 A AU 2008200033A AU 2008200033 A AU2008200033 A AU 2008200033A AU 2008200033 A1 AU2008200033 A1 AU 2008200033A1
Authority
AU
Australia
Prior art keywords
metal ions
aqueous process
metallic compound
alkyls
composition
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.)
Abandoned
Application number
AU2008200033A
Inventor
Peter Morton
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Canadus Technologies LLC
Original Assignee
Canadus Technologies LLC
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Priority claimed from AU2002355854A external-priority patent/AU2002355854B2/en
Application filed by Canadus Technologies LLC filed Critical Canadus Technologies LLC
Priority to AU2008200033A priority Critical patent/AU2008200033A1/en
Publication of AU2008200033A1 publication Critical patent/AU2008200033A1/en
Abandoned legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Description

P/00/01 Regulation 3.2
AUSTRALIA
Patents Act 1990 COMPLETE
SPECIFICATION
STANDARD PATENT Invention Title: Compositions for removing metal ions from aqueous process solutions and methods of use thereof The following statement is a full description of this invention, including the best method of performing it known to us: 00
O
COMPOSITIONS FOR REMOVING METAL IONS FROM AQUEOUS PROCESS SOLUTIONS AND METHODS OF USE THEREOF 00 FIELD OF INVENTION The present invention describes a composition and process using the composition for removal of metal ions from aqueous process solutions.
BACKGROUND OF THE INVENTION Various metals are used in many useful industrial processes. For example, silver is used in many image-forming industrial processes, such as photography, thermography, and photothermography. Such processes, however, result in waste solutions containing metal ions at levels that may be undesirable to the environment. In addition, many countries now have laws that control the levels of certain metal ions that can be released into the environment. Since commercial disposal of large volumes of untreated waste solutions can be costly, there has been a concerted effort to treat the waste solutions in a cost effective manner. Furthermore, these metals can be of sufficient value to justify their recovery.
Metals have been removed from aqueous waste solutions utilizing processes such as ion exchange, electrolysis, and settling. However, all of these known processes have their limitations. Ion exchange is costly, slow and impractical. The ion exchange resins -1A- 00 are expensive because they require complex and sophisticated fabrication processes.
Some of this cost can be recouped by regenerating the ion exchange resins. However, the waste solutions produced during regeneration typically have to be treated. Similarly, Cc electrolysis is also costly due to maintenance, resource requirements, and energy input.
Electrolysis is also very sensitive to contaminants and generally provides ineffective 00levels of metal recovery.
N1 Settling processes typically use one or more agents that transform the metals into materials that are no longer soluble in the system and settle to the bottom of the tank.
However, currently known settling processes have the following limitations. Undesirably large amounts of sludge, which cannot be regenerated, can be formed. Some settling processes require heating to very high temperatures, greater than 80 C, to provide useful results. Still others require the use of a change in pH to cause the transformation of the metal into an insoluble material.
Accordingly, there is a need for effective recovery of metal ions from aqueous waste solutions (hereafter also referred to as aqueous process solutions).
005072616 00 Reference to any prior art in the specification is not, and should not be taken as, an acknowledgment, or any form of suggestion, that this prior art forms part of the common general O knowledge in Australia or any other jurisdiction or that this prior art could reasonably be expected C to be ascertained, understood and regarded as relevant by a person skilled in the art.
C€3 As used herein, except where the context requires otherwise, the term "comprise" and 00 variations of the term, such as "comprising", "comprises" and "comprised", are not intended to exclude other additives, components, integers or steps.
SUMMARY OF THE INVENTION The present invention provides a composition for removing metal ions from an aqueous process solution, the composition comprising a monomeric non-metallic compound, which comprises a thiuram, wherein the non-metallic compound is capable of forming a complex with a metal ion in an aqueous process solution.
The process for removing metal ions from aqueous process solutions may include (i) reacting metal ions in an aqueous process solution having a wetting agent with a composition (also referred to herein as a treatment composition) having a non-metallic compound to form an organometallic complex precipitate, and (ii) separating the organometallic complex precipitate from the aqueous process solution. The reacting step is preferably conducted at a temperature of less than or equal to about 50' C. The process is preferably conducted at a pH of greater than or equal to about 3.0. In one embodiment, the treatment composition includes non-metallic compound that is a thiuram. In another embodiment, the treatment composition further includes an additional nonmetallic compound that is a dithiocarbamate.
00
O
O
DETAILED DESCRIPTION OF THE INVENTION The present invention provides a composition for removing metal ions from aqueous process solutions. The term "aqueous process solution," as used herein, means any liquid containing from about 1 ppm to about 15,000 ppm of metal ions. The term "about," as 0 5 used herein, means plus or minus 10% of the referenced value. The term "aqueous", as 00 0 used herein, means containing greater than about 50%, by weight of the solution, of water or a water miscible solvent. The processes used herein for aqueous process solutions can also be used for appropriate gaseous process mixtures. Nonlimiting examples of aqueous process solutions include the processing solutions from the following technologies: photography, photothermography, thermography, lithography, metallurgy, semiconductor polishing, and x-ray imaging. The term "metal ion," as used herein, means the soluble form of any metal in Groups IB through VIIB and VIII of the periodic table (according to CRC Handbook of Chemistry and Physics, 62nd Edition, 1981 1982), including the elements having the atomic numbers of 58-71 and 90-103, aluminum, gallium, indium, thallium, germanium, tin, lead, antimony, bismuth, mixtures thereof, and alloys thereof.
Metal ions of particular interest are those identified in the Resource Conservation Recovery Act (RCRA). The metal ions are preferably selected from the group consisting of arsenic, barium, cadmium, chromium, cesium, copper, iron, lead, mercury, nickel, selenium, silver, technetium, thallium, zinc, actinides, lanthanides, mixtures thereof, and alloys thereof.
A method or process is described herein for reacting a treatment composition having a non-metallic compound with metal ions in an aqueous process solution having a wetting agent to form an organometallic complex precipitate, and separating the organometallic complex precipitate from the aqueous process solution. The organometallic complex may be separated by any technique or process known to the -4- 00 skilled artisan, settling, filtration, centrifugation, etc. Treated aqueous process solutions can have less than about 100 ppm, preferably less than about 20 ppm, and more preferably less than about 5 ppm of metal ions.
Cc€ 0It has been surprisingly found that the process described herein can effectively remove metal ions to these low levels even in the presence of high 00 concentrations of chelators. Chelators are typically used to maintain the metal ions in the process solution, thereby hindering their removal. The present process can be utilized to effectively remove metal ions in process solutions having chelator to metal ion numeric proportions of greater than about 500:1. In fact, the present process can also be effective in any of the following chelator to metal ion numeric proportions: from about 1,250,000:1 to about 10:1; from about 500,000:1 to about 20:1; and from about 100,000:1 to about 100:1.
The preferred treatment compositions of the present invention include from about to 100%, preferably from about by 50% to about 99.99%, by weight of the composition, of a non-metallic compound, which associates with the metal ion, and from 0.0% to about 99.0%, preferably from about by 0.01% to about 50%, by weight of the composition, of an appropriate carrier. The non-metallic compound is preferably not a polymer. The treatment compositions can be provided in dry or liquid forms. Accordingly, the carrier can be any liquid or solid material known to the skilled artisan that is either neutral in its effect or enhances one or more properties of the non-metallic compound and its use, e.g., storage and handling properties. An example of an appropriate carrier is mineral oil.
In the present invention, the treatment compositions include a non-metallic compound that is a thiuram, which can also be referred to as thiram. The thiuram is sparingly soluble in the aqueous process solution. The term "sparingly soluble," as used herein, means that less than 0.1% by weight of the 00
O
O
material is soluble in the aqueous process solution. Without wanting to be limited by any one theory, it is believed that the non-metallic compounds of the present invention form an organometallic complex with the metal ion. The organometallic complex becomes a r< precipitate that can be separated from the aqueous solution by any separation technique or method known to the skilled artisan. Nonlimiting separation techniques or methods 0 0 include filtration, gravity settling, centrifugation, flocculation, cake filtration, membrane CN filtration, and floatation (liquid/air filtration).
One group of thiurams can be characterized by the general chemical formula as illustrated below.
S S R II II N-C- Sl -C-N R2 \R, wherein, m is an integer of 1 or 2; and RI, R 2
R
3 and R 4 are individually selected from the group consisting of C-C10 linear alkyls, C3-C10 branched alkyls, C3-C10 cycloalkyls, and substituted and unsubstituted aryls. As is well known to the skilled artisan, any of the carbon atoms or hydrogen atoms in each of the above described R-groups can be substituted with chemical moieties that tailor the performance of the non-metallic compound without significantly effecting the requisite solubility properties.
Examples of useful non-metallic compounds of formula include, but are not limited to, tetramethylthiuram monosulfide (CAS# 97-74-5); bis(dimethyldithiocarbamoyl) disulfide (CAS# 137-26-8); tetrabenzylthiuram disulfide (CAS# 10591-85-2); tetraethylthiuram disulfide (CAS# 97-77-8); tetrabutylthiuram disulfide (CAS# 1634-02-2), dipentamethylenethiuram tetrasulfide (CAS# 120-54-7), and mixtures thereof.
00
O
a In another embodiment of the present invention, the treatment compositions of the present invention further include a water soluble, non-metallic compound that is a dithiocarbamate. One group of dithiocarbamates can be characterized by the general ¢C chemical formula as illustrated below.
00 I S S II Yo.
0 S -C-N \R6 wherein, n is an integer of 1 or 2; o is an integer of 1 or 2; R 5 and R 6 are individually 0o selected from the group consisting of C1-C10 linear alkyls, C3-C10 branched alkyls, C3cyclo-alkyls, and substituted and unsubstituted aryls; and Y is an element selected from Groups IA and IIA of the periodic table. As is well known to the skilled artisan, any of the carbon atoms or hydrogen atoms in each of the above-described R-groups can be substituted with moieties that enhance the performance of the non-metallic compound.
Examples of useful non-metallic compounds of formula (II) include, but are not limited to, sodium dimethyldithiocarbamate (CAS# 128-04-1), sodium diethyldithiocarbamate (CAS# 148-18-5), sodium dibenzyldithiocarbamate (CAS# 55310-46-8), sodium dibutyldithiocarbamate (CAS# 136-30-1), and mixtures thereof.
The aqueous process solution also has a wetting agent in a concentration from about 0.01 molar to 10 molar, more preferably from about 0.025 molar to 0.5 molar, and most preferably from about 0.05 molar to 0.25 molar. Some process solutions may already have a wetting agent as a component of the waste stream. For example, photographic waste solutions typically contain wetting agents in sufficient concentration.
If the aqueous process solution does not contain a wetting agent, an appropriate amount of a wetting agent may be added. Wetting agents, also known as surfactants, are -7- 00
O
O
Scompounds that reduce the surface tension of liquids, or reduce interfacial surface tension between two liquids or a liquid and a solid. It is, therefore, believed that the wetting agent helps to lower the barrier of reaction. Wetting agents may be soluble in both n organic and water solutions. However, it is preferred that the wetting agents used herein be at least soluble in the aqueous solution at the concentrations used. General categories 00 of useful wetting agents include, but are not limited to, non-ionic surfactants, anionic CN surfactants, cationic surfactants, carboxylic acids, alcohols, and amines. Zwitter-ionic and amphoteric surfactants may also be useful. Examples of useful wetting agents are disclosed in the Kirk-Othmer Encyclopedia of Chemical Technology (John Wiley and Sons, New York), U.S. Patent No. 6,399,676 issued to Labude, et al. on June 4, 2002, and U.S. Patent No. 6,087,312 issued to Masotti, et al on July 11, 2000, all of which are incorporated herein by reference in their entirety. Examples of useful wetting agents include, but are not limited to, acetic acid, propanoic acid, methanol, ethanol, propanol, tetraethyl ammonium hydroxide, fatty acids and salts thereof, alkylaryl sulfonates, and mixtures thereof.
The present process can be conducted at a wide variety of reaction variables, which can be tailored for optimization accordingly to any particular process. As in any chemical reaction, increasing the reaction or retention time, duration of physical contact of the non-metallic compound and the aqueous process solution, is beneficial to increasing the quantity and/or size of the precipitated organometallic complex.
Accordingly, it is preferred to maximize the reaction or retention time as much as allowable taking into consideration other process and economic variables. Typically, the reaction or retention time is at least 0.1 hours, preferably from about 0.5 hours to about 125 hours, and more preferably from about 1 hour to about 10 hours. As is well 00 understood by the skilled artisan, lower reaction or retention times can be needed at higher reaction temperatures.
The reaction can be conducted at a wide range of temperatures. Preferably, the Cc reaction temperature is less than or equal to about 500 C, more preferably less than or equal to about 450 C, and most preferably at ambient temperatures. Ambient 00 temperatures, as used herein, means the normal temperature range of the surrounding "1 environment, which typically can range about from 50 C to about 400 C. The processes of the present invention, therefore, can be conducted with little or no heating, thereby decreasing the cost of heat inputs to the system. However, a small amount of heating to achieve reaction temperatures within the above ranges may be desirable to achieve optimum processing results.
Since at least some of the non-metallic compounds in the treatment composition are sparingly soluble in the aqueous process solutions, it is preferred to employ any of the known mixing technologies during and after the initial reaction. As is well known to the skilled artisan, however, introduction of air into a system, having a minority of hydrophobic components in a majority ofhydrophilic components, can result in an emulsion. Such emulsions typically form a layer on top of the hydrophilic phase. The emulsion layer can be removed by utilizing any technology or process known in the art, skimming technology. If technology like skimming is not employed in the separation step, the formation of an emulsion layer can be prevented by minimizing the introduction of air into the system after the treatment composition is added to the aqueous solution. For example, mixing can be controlled to prevent the formation of a vortex, which introduces air into the system, by placing a blade in an off-center position at the bottom of the tank. Alternatively, the tank can have a floating top that significantly reduces the amount of air on top of the mixture in the tank.
-9- 00 Lastly, the present process can be conducted at a wide range ofpH's, especially if the process is conducted in a substantially oxygen-free environment. However, due to the increased possibility of organic materials being degraded by oxidized metal ions in ¢€3 Cc oxygen rich environments, Fenton's reaction, it is preferred to conduct the process at a pH of greater than or equal to about 3.0, preferably from about 4.0 to 12.0, and more oO preferably from about 7.0 to 12.0. It is also believed that the present processes provide N, better separation of metal ions at lower surface tensions, at about the surface tension of 1% by weight of acetic acid in water.
In one embodiment of the present invention, the process involves introducing the treatment compositions of the present invention to the aqueous process solution in batch or continuous systems. Such systems can be run in parallel and/or in series. Such systems typically utilize a container, such as a tank, containing the aqueous process solution, and the container is adapted to provide mixing, by utilizing any mixing technology known to the skilled artisan. The treatment composition is added in a concentration that is proportional to the metal ions present in the aqueous process solution by any well-known method of addition, by metering. In this embodiment, the treatment composition is added so that the non-metallic compound is at a concentration of from about 1.0:1.0 to about 1.0:4.0, preferably from about 1.0:1.2 to about 1.0:3.0, and more preferably from about 1.0:1.5 to about 1.0:2.5 by molar ratio of the non-metallic compound to the metal ions present in the aqueous process solution. Some non-metallic compounds can even be effective at concentration levels of at least 2.5 x 10 3 by weight of the aqueous process solution and the non-metallic compound. More of the nonmetallic compound may be needed at lower pH's, below about pH 4, in oxygen rich environments and when higher levels of contaminants are present, greater than about 5 ppm. Contaminants are any chemical compounds other than the metal ions and water.
00 In addition, an appropriate amount of a wetting agent may be added if the process solution does not contain the required levels described above.
This embodiment also includes a separation step after the completion of the Cc reaction, or after the end of the appropriate reaction or retention time. Any separation technology or method known to the skilled artisan can be used to separate the 00 organometallic complex precipitate from the aqueous process solution, settling, C1 centrifugation, filtering, and the like. In continuous systems, a separation device can be placed in series to the mixing container. The resulting precipitate can then be further processed, as described hereinafter.
In another embodiment of the present process, the aqueous process solution containing the metal ions can be introduced to a bed of the treatment composition containing the non-metallic compound in powder or bead form. An appropriate amount of a wetting agent may be added if the process solution does not contain the required levels described above. In this embodiment, a reaction bed is packed with the treatment composition, and a flow of aqueous process solution is controlled through the bed via gravity or positive pressure to optimize the reaction or retention time of reaction in relation to other process and economic variables. The reaction bed can be in any acceptable geometric form. Typically, 2 moles of metallic ions will require about 1 mole ofnon-metallic compound. More of the non-metallic compound may be needed at lower pH's, below about pH 4, in oxygen rich environments and when higher levels of contaminants are present, greater than about 5 ppm. The treatment composition in the reaction bed can be replaced when removal of metal ions has reached an unacceptable degree. The resulting precipitate can then be further processed, as described hereinafter.
Optional ingredients known to the skilled artisan can also be used to aid in or optimize any of the process steps described above. For example, flocculating agents can -11- 00
O
O
c be used to aid in the settling process. Nonlimiting examples of flocculating agents include acrylates. Also, antifoaming agents can also be used in the mixing step, assuming that the degree of agitation is not changed. Nonlimiting examples of antifoaming agents rn include silicone oils.
As is well understood by the skilled artisan, the processes described herein 00 0can be used in conjunction with other conventionally known metal ion recovery systems, c such as photochemical developer, fixer, and bleach-fix processing solutions utilizing metallic replacement, electrolytic recovery, chemical precipitation, ion exchange and reverse osmosis. For example, the aqueous process solution can first be treated electrolytically before the present process is used. Alternatively, the present process can be used first before electrolytic treatment.
As described above, it is believed that the non-metallic compounds of the present invention react with metal ions to form an organometallic complex. Without wanting to be limited by any one theory, it is believed that the metallic ion associates to one or more sulfur groups on the non-metallic compound via van der Waals forces, ionic forces, delta, and/or sigma bonds. The recovered organometallic complex can, therefore, be further processed to recover the metal ions as native metal by removing these attractive forces by any method known to the skilled artisan. Alternatively, the complexed non-metallic compound can simply be removed by any method known to the skilled artisan. Examples of suitable removal techniques include, but are not limited to, oxidization, degradation, acidification, and flame refining.
00
O
O
EXAMPLES
Ct Example 1.
Use of the Treatment Composition with Mixing CAqueous process solutions containing metal ions can be introduced into a container fitted with a mixing device, and an appropriate amount of a wetting agent may 0 0 be added if the process solution does not contain the required levels described above. The CN mixing device may be any apparatus that will fully agitate the liquid. Typical examples include, but are not limited to, mixers, such as Lightin series 10, and pumps, such as Iwaki MD-70 or March model 1A-MD. Once the liquid is transferred into the container, the treatment composition can be added, and the mixture can then be agitated. The reaction is allowed to proceed until the desired concentration of metal ion is achieved.
Reaction time to completion is influenced by various factors including temperature, pH, and solution composition.
In particular, silver ion was removed from a photochemical fixer solution having silver ions at about 2000 ppm. The reaction was conducted at a pH of about 7 and at a reaction temperature of about 250 C, as follows. Using a 55-gallon (208 container and a side mounted mixer that allows full mixing of the tank, while minimizing introduction of air into the system, 50 gallons (189 of photochemical fixer solution was added.
The concentrations of the individual components in the fixer solution was not easily discernable because the fixer solution was the actual waste stream from a photographic laboratory. However, it was estimated, from the starting compositions used, that the waste fixer solution contained from about 0.01 to about 0.1 molar of acetate, a wetting agent. After turning on the mixer, 2 pounds (0.9 kg.) of pure bis(dimethyldithiocarbamoyl) disulfide (CAS# 137-26-8) in powder form was added.
After allowing the reaction to proceed for about four hours, the reaction mixture was -13- 00 allowed to settle for 30 minutes to form a layer at the bottom of a precipitate containing -an organometallic complex. The supernatant aqueous solution was tested for silver ions using a Perkin Elmer flame atomic absorption spectrometer. The procedure for using Cc such atomic absorption spectrometers to obtain concentrations of metal ions is well known in the art. The filtered aqueous solution contained less than about 5 ppm of silver 00 ions.
Example 2.
Use of the Treatment Composition in a Column The treatment compositions of the present invention can also be used in a fixed bed reactor, such as a column, by compressing the treatment composition to form pellets or beads having a length or diameter, respectively, from about 2 to about 6 millimeter that can be placed in the fixed bed reactor. Using a column as an example, the column housing may be in the form of a tube with proper connections at both ends to allow the aqueous process solution to enter and exit the column while maintaining the treatment composition pellets in the column. First, an appropriate amount of a wetting agent may be added if the process solution does not contain the required levels described above.
Once the treatment composition is added to the column, the aqueous process solution can be slowly pumped into the column. The treated solution leaving the column can then be filtered to yield a precipitate of an organometallic complex containing silver ions. This embodiment can provide treated solutions containing less than about 10 ppm of silver ions by adjusting the flow rate. Adjustment of the flow rate can compensate for other factors that can effect performance, such as the initial silver ion concentration, pH, and other metal ions.
00
O
In particular, silver ions were removed from a photochemical fixer solution having silver ions at a concentration of about 2000 ppm. The experiment was conducted at a pH
O
of about 7 and at a reaction temperature of about 250 C, as follows. Using a column large enough to hold about 10 pounds (4.5 kg.) of pure bis(dimethyldithiocarbamoyl) disulfide (CAS# 137-26-8) in pellet form, about 200 gallons (757 of photochemical fixer 00 solution was steadily pumped through the column at a rate of one gallon (3.8 per hour, Sthereby allowing the experiment to proceed for about 200 hours. The retention time was about 5 hours. The treated solution exiting the column was filtered using a 1-micron bag filter to yield a precipitate containing silver ions. The bag filter was purchased from Filter Specialist, Inc. The filtered aqueous solution was tested for silver ions using a Perkin Elmer flame atomic absorption spectrometer. The procedure for using such atomic absorption spectrometers to obtain concentrations of metal ions is well known in the art. The filtered aqueous solution contained less than about 10 ppm of silver ions.

Claims (7)

1. A composition for removing metal ions from an aqueous process solution, the 0 composition comprising a monomeric non-metallic compound, which comprises a thiuram, wherein the non-metallic compound is capable of forming a complex with a metal ion in an C 5 aqueous process solution. 00 O S2. The composition according to claim 1, wherein the thiuram is characterized by the general chemical formula S S R /R3 N C-f (I) R2 R4 wherein, m is an integer of 1 or 2; and Ri, R
2 R 3 and R 4 are individually selected from the group consisting of C1-C10 linear alkyls, C3-C10 branched alkyls, C3-C10 cyclo-alkyls, and substituted and unsubstituted aryls.
3. The composition according to claim 2, wherein the thiuram is selected from the group consisting of tetramethylthiuram monosulfide, bis(dimethyldithiocarbamoyl) disulfide, tetrabenzylthiuram disulfide, tetraethylthiuram disulfide, tetrabutylthiuram disulfide, dipentamethylenethiuram tetrasulfide, and mixtures thereof.
4. The composition according to any one of the preceding claims, wherein the non- metallic compound further comprises a dithiocarbamate. 005072616 00
5. The composition according to claim 4, wherein the dithiocarbamate is characterized by the general chemical formula (II): S--C-N Yo+ (I) 00 n 0 (w wherein, n is an integer of 1 or 2; o is an integer of 1 or 2; R 5 and R 6 are individually selected from the group consisting of C1-C10 linear alkyls, C3- branched alkyls, C3-C10 cyclo-alkyls, and substituted and unsubstituted aryls; and Y is an element selected from Groups IA and IIA of the periodic table.
6. The composition according to claim 5, wherein the dithiocarbamate is selected from the group consisting of sodium dimethyldithiocarbamate, sodium diethyldithiocarbamate, sodium dibenzyldithiocarbamate, sodium dibutyldithiocarbamate, and mixtures thereof.
7. A composition for removing metal ions from an aqueous process solution substantially as hereinbefore described and with reference to the accompanying examples -17-
AU2008200033A 2001-08-03 2008-01-04 Compositions for removing metal ions from aqueous process solutions and methods of use thereof Abandoned AU2008200033A1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
AU2008200033A AU2008200033A1 (en) 2001-08-03 2008-01-04 Compositions for removing metal ions from aqueous process solutions and methods of use thereof

Applications Claiming Priority (5)

Application Number Priority Date Filing Date Title
US60/309,837 2001-08-03
US60/309,854 2001-08-03
US60/309,836 2001-08-03
AU2002355854A AU2002355854B2 (en) 2001-08-03 2002-08-01 Compositions for removing metal ions from aqueous process solutions and methods of use thereof
AU2008200033A AU2008200033A1 (en) 2001-08-03 2008-01-04 Compositions for removing metal ions from aqueous process solutions and methods of use thereof

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
AU2002355854A Division AU2002355854B2 (en) 2001-08-03 2002-08-01 Compositions for removing metal ions from aqueous process solutions and methods of use thereof

Publications (1)

Publication Number Publication Date
AU2008200033A1 true AU2008200033A1 (en) 2008-01-31

Family

ID=39016165

Family Applications (1)

Application Number Title Priority Date Filing Date
AU2008200033A Abandoned AU2008200033A1 (en) 2001-08-03 2008-01-04 Compositions for removing metal ions from aqueous process solutions and methods of use thereof

Country Status (1)

Country Link
AU (1) AU2008200033A1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113060860A (en) * 2021-03-22 2021-07-02 中南大学 Treatment method of chemical nickel wastewater

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113060860A (en) * 2021-03-22 2021-07-02 中南大学 Treatment method of chemical nickel wastewater

Similar Documents

Publication Publication Date Title
AU2002355854B2 (en) Compositions for removing metal ions from aqueous process solutions and methods of use thereof
AU2002355854A1 (en) Compositions for removing metal ions from aqueous process solutions and methods of use thereof
JP2912226B2 (en) Wastewater treatment method
US4332687A (en) Removal of complexed heavy metals from waste effluents
EP0039819B1 (en) Process for treating a liquid waste composition containing copper ions and an organic complexing agent
WO1984003692A1 (en) Method for removing heavy metals from aqueous solutions by coprecipitation
US5338460A (en) Sulfide precipitation of heavy metals from aqueous solutions
WO1981002569A1 (en) A method of purifying waste aqueous solutions from heavy metals
AU605992B2 (en) Process for the treatment of effluents containing cyanide and toxic metals, using hydrogen peroxide and trimercaptotriazine
US4172784A (en) Process for the separation of cadmium (Cd++)-ions from sewage, waste water and aqueous solutions
US5108620A (en) Process for recovery of spent etchant
US20150211091A1 (en) Silver Recovery Methods and Silver Products Produced Thereby
AU2008200033A1 (en) Compositions for removing metal ions from aqueous process solutions and methods of use thereof
CA2251480A1 (en) Waste treatment of metal plating solutions
Aktas Silver recovery from silver-rich photographic processing solutions by copper
EP0737679A1 (en) Method of making trialkali and triammonium salts of TMT and metal salts
US5211843A (en) Mobile apparatus for environmentally treating spent etchant safely
CA2978153C (en) Dissolved air flotation for removal of selenium
US5281339A (en) Removal of contaminants
US6126840A (en) Process for removing silver in the presence of iron from waste effluent
CN1775938A (en) Composition for removing metal ions from aqueous process solutions and methods of use threrof
JPH06144802A (en) Recovery of iodine from waste liquid containing organoiodine compound
JPH0720285A (en) Removing method of underwater radioactive substance
JP2007196107A (en) Selenium-containing wastewater treatment method and apparatus

Legal Events

Date Code Title Description
MK4 Application lapsed section 142(2)(d) - no continuation fee paid for the application