Classifications

• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
  • B09C—RECLAMATION OF CONTAMINATED SOIL
  • B09C1/00—Reclamation of contaminated soil
  • B09C1/08—Reclamation of contaminated soil chemically
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
  • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
  • B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
  • B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
  • B01J20/26—Synthetic macromolecular compounds
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
  • B09C—RECLAMATION OF CONTAMINATED SOIL
  • B09C1/00—Reclamation of contaminated soil
  • B09C1/002—Reclamation of contaminated soil involving in-situ ground water treatment
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
  • B09C—RECLAMATION OF CONTAMINATED SOIL
  • B09C2101/00—In situ

Definitions

• the present invention is directed to stabilized compositions of particulate activated carbon and the use of such compositions to adsorb contaminants from soil and groundwater.
• Activated carbon is commonly used as a sorbent medium for removing organic and inorganic contaminants from water. It is used in treatment systems to detoxify industrial process water, as well as in pump-and-treat systems for above- ground treatment of contaminated groundwater. In use activated carbon is typically manufactured and used in granular or powder form whereby the particulate is loaded into fluid- or fixed-bed treatment systems or dispersed or distributed over the area subject to contamination.
• activated carbon cannot distribute through soil to reach areas of contaminated water. Instead, it must be applied in a trench to treat water passing therethrough, or must be injected as a slurry which has limited or no mobility in the aquifer. This lack of mobility causes the cost of treatment to be very high, whereas the contact with contaminated water remains quite low. The high cost is primarily due to the large number of application points required to thoroughly treat a contaminated area.
• colloidal activated carbon It is therefore desirable to have improved methods and compositions that will distribute colloidal activated carbon much further in the subsurface than simple carboxymethyl cellulose. It is likewise desirable to provide such a composition of colloidal activated carbon that is of simple formulation, easy to deploy, is substantially effective at adsorbing contaminants from soil and groundwater, and is further substantially more effective in becoming dispersed and capable of being quickly and effectively deployed over a greater area of volume of soil and groundwater than prior art activated carbon compositions and methods of using the same for environmental remediation.
• the present invention specifically addresses and alleviates the above- identified deficiencies in the art.
• the present invention is directed to compositions of stabilized activated carbon and the use of such compositions in environmental remediation, and in particular as a means of absorbing contaminants in soil and groundwater.
• the invention comprises the combination of activated carbon, preferably formed to have a very fine particulate size, typically ranges from 0.1 to 10 microns, and preferably 0.5 to 2 microns, that are stabilized by at least two additives.
• the first additive is a stabilizing polymer, which may comprise either an anionic or nonionic polymer.
• the second additive is a distribution enhancement agent operative to facilitate the ability of the composition to become distributed and dispersed about a matrix of soil and groundwater.
• the distribution enhancement agent will include one or more agents selected from the group consisting of chelating agents, anionic polymers, anionic surfactants or nonionic surfactants.
• the ratio of activated carbon: first additive: second additive present in amounts relative one another are in the range of l(carbon): 0.01-1.0 (first additive) : 0.01-1.0 (second additive).
• the ratio of the aforementioned components of activated carbon: first additive: second additive are in the range of 1 (carbon) : 0.05-0.5 (first additive) : 0.025-0.5 (second additive), based upon relative weights of such components.
• the compositions of the present invention are operative to form water- based colloids of activated carbon, and can be deployed as an aqueous admixture whereby the activated carbon component of the aqueous admixture will range between 0.01% and 70.0% by weight of the water.
• the water based colloids of the present invention can be injected, such as by high pressure injection or fracturing, in the range of 0.05% to 40.0% activated carbon by weight in water and in a yet further, more highly refined embodiment, can be injected in the range of 0.1% to 20.0% carbon by weight in water.
• the water-based colloids formed according to the present invention can be applied by gravity feed or percolation into soil.
• the compositions of the present invention can be applied at a rate between approximately 1 and 80 gallons of aqueous admixture per cubic yard of soil and groundwater, and preferably between approximately 4 and 60 gallons per cubic yard.
• New compositions and methods have been developed that enable increased distribution of activated carbon colloids through soil and groundwater. This allows for very cost-effective treatment of contaminated aquifers, and therefore control over mobility of contaminants in groundwater and soil systems.
• the present invention is a mixture of very fine activated carbon (0.1 to 10 micron size, and preferably within a 0.5 to 2 micron range) stabilized by at least two additives, wherein the first additive is a stabilizing polymer, and the second additive is a distribution enhancement agent.
• the addition of one or more distribution enhancement agents enables the colloidal material to distribute significantly further through soil and groundwater during application than the compositions and methods of the prior art.
• the first additive, or stabilizing polymer can be an anionic polymer or a nonionic polymer.
• examples include but are not limited to carboxymethyl cellulose (CMC), carrageenan, polyacrylic acid, xanthan gum (nonionic), and combinations thereof.
• the second additive, or distribution enhancement agent is selected from the following list: chelating agents, anionic polymers, anionic surfactants, or nonionic surfactants, and possible combinations thereof.
• Chelating agents include but are not limited to citrates, phosphates (e.g.
• SHMP SHMP, STTP, TSPP), silicates, borates, sulfates, carbonates, aminocarboxylic acids and salts thereof (e.g. EDTA, MGDA and NTA), polyamines such as ethylene diamine, as well as combinations thereof.
• Anionic polymers of the second additive include but are not limited to sulfated or carboxylated polysaccharides, polyacrylates, polyacrylamides, lignosulfonate, polyacrylate copolymers, and combinations thereof.
• Anionic surfactants include but are not limited to dioctyl sodium sulfosuccinate, alkyl and aryl sulfates (e.g. sodium lauryl sulfate), alkyl carboxylates
• Nonionic surfactants include but are not limited to alkyl polyethylene oxides, ethylene oxide polymers, polyethylene oxide lauryl ether (e.g., Brij 30® produced by Croda, Inc.), ethylene oxide -propylene oxide copolymers (e.g., Tergitol XD® produced by the Dow Chemical Company), and combinations thereof.
• compositions of this invention are preferably formed wherein the relative weight ratios of carbon: first additive (stabilizing polymer) : second additive (distribution enhancing agent) are in the range of: 1 : 0.01-1.0 : 0.01-1.0 and preferably in the ranges of 1 : 0.05-0.5 : 0.025-0.5
• the method of groundwater treatment using this invention includes injection or other application of the above compositions as a water-based colloid such that the activated carbon concentration between 0.01% and 70.0% by weight in water.
• the material can be injected in the range of 0.05% to 40.0% activated carbon by weight in water. Even more preferably, it can be injected in the range of 0.1% to 20.0% carbon by weight in water.
• the aqueous admixture containing the compositions of the present invention can be applied by gravity feed or percolation in the amount sufficient to adsorb the contaminants believed to be present in a given area of contaminated soil/groundwater.
• a general application rate can range from between approximately 1 to 80 gallons of the aqueous admixture of the water-based colloid of the present invention per cubic yard of soil and groundwater to be treated, and preferably between approximately 4 and 60 gallons of the aqueous admixture per cubic yard treated.
• Example 1 Dispersion preparation: A series of colloidal dispersions were prepared with the following general composition: 1% w/w activated carbon (approximately 1.5 micron average particle size), 0.25% w/w stabilizing polymer, and 0.25% w/w distribution enhancement agent. The dispersions were prepared as follows: The stabilizing polymer and second additive were mixed thoroughly into water with a high-shear mixer and mixed until homogeneous. A slurry of activated carbon in water was then added to the mixture. Each dispersion was mixed for an additional 5 minutes resulting in a very homogeneous, black colloidal suspension. The compositions of the tested dispersions and some comparative samples are shown in Table 1.
• Example 2 Column transport testing: Each of the colloids in Example 1 was diluted with tap water to a carbon concentration of 2,000 mg/L. A 25 g aliquot of each diluted colloid was eluted through a glass column (bed dimensions 2.5 x 24.0 cm) packed with saturated soil having a sand/silt/clay ratio of 93.7/3.9/2.4. The 25 g sample was eluted through the column and flushed with additional tap water until the column effluent was clear. Activated carbon in the combined effluent from each column study was measured by UV-visible spectroscopy. The total mass of carbon eluted was calculated using a calibration curve.
• Example #1 For comparison to the prior art, a standard colloid sample stabilized only by CMC was studied (Sample #1). The mass of carbon eluted by each sample is reported in table 1, and the amount of carbon eluted is also reported as a percentage relative to the standard.

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• Chemical & Material Sciences (AREA)
• Engineering & Computer Science (AREA)
• Life Sciences & Earth Sciences (AREA)
• Environmental & Geological Engineering (AREA)
• Soil Sciences (AREA)
• Organic Chemistry (AREA)
• Water Supply & Treatment (AREA)
• Analytical Chemistry (AREA)
• Hydrology & Water Resources (AREA)
• Chemical Kinetics & Catalysis (AREA)
• Processing Of Solid Wastes (AREA)
• Water Treatment By Sorption (AREA)
• Colloid Chemistry (AREA)
• Soil Conditioners And Soil-Stabilizing Materials (AREA)

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• 2014
  • 2014-08-01 WO PCT/US2014/049468 patent/WO2015017820A1/en not_active Ceased
  • 2014-08-01 JP JP2016531939A patent/JP6441341B2/ja active Active
  • 2014-08-01 DK DK14832703.4T patent/DK3027562T3/en active
  • 2014-08-01 EP EP14832703.4A patent/EP3027562B1/en active Active
  • 2014-08-01 US US14/449,404 patent/US9770743B2/en active Active

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