WO2009129184A1 - Retrait et élimination du radium - Google Patents

Retrait et élimination du radium Download PDF

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Publication number
WO2009129184A1
WO2009129184A1 PCT/US2009/040372 US2009040372W WO2009129184A1 WO 2009129184 A1 WO2009129184 A1 WO 2009129184A1 US 2009040372 W US2009040372 W US 2009040372W WO 2009129184 A1 WO2009129184 A1 WO 2009129184A1
Authority
WO
WIPO (PCT)
Prior art keywords
radium
cation exchange
strong acid
exchange resin
acid cation
Prior art date
Application number
PCT/US2009/040372
Other languages
English (en)
Inventor
James Spain
Original Assignee
Basin Water, Inc.
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
Application filed by Basin Water, Inc. filed Critical Basin Water, Inc.
Publication of WO2009129184A1 publication Critical patent/WO2009129184A1/fr

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • C02F2001/425Treatment of water, waste water, or sewage by ion-exchange using cation exchangers
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/006Radioactive compounds

Definitions

  • This invention relates to the removal and disposal of radium present in potable water sources.
  • Radioactive contaminants Radium is one of these radionucleotides. Much of this contamination is naturally occurring. In most cases these radionucleotide contaminants are at levels that are low enough to not be considered a health concern. At higher levels radionucleotides in drinking water may cause cancer.
  • DOWEX RSC barium sulfate-doped styrene resin.
  • RSC sodium Selective Complexer
  • This resin is not regenerable and in some settings needs a significant level of sulfate, such as up to about 30 parts per million, in the water being treated to have a long resin life.
  • use of DOW RSC is incompatible with low pH water sources such as water sources at pH 5.5 or lower. As with many resins, iron contamination in the water supplies can shorten the effective resin life.
  • DOWEX RSC resin is relatively expensive and thus is commonly operated for long periods. This long run cycle leads to the accumulation of large enough amounts of radium on the resin that when it is removed from service it must be treated as a hazardous radioactive material and thus must be discarded into a "low level radioactive material disposal" site. The cost of such disposal is very high, currently at least $225 per Ib. This is as much or more than the cost of the fresh resin itself. This leads to a non economic operation.
  • this invention relates to a process for removing radium from radium-contaminated water, which process comprises:
  • This process of the invention contacting radium-contaminated water with a strong acid cation exchange resin under radium exchanging conditions. This contacting is carried out in a contacting zone. This contacting results in the formation of a reduced radium content water and a radium-containing strong acid cation exchange resin.
  • This contacting is continued as additional radium-contaminated water is brought into contact with the radium-containing strong acid cation exchange resin. This gives rise to the formation of additional reduced radium content water and an enhanced radium content radium-containing strong acid cation exchange resin.
  • the contacting is stopped when the radium content of the enhanced radium content radium-containing strong acid cation exchange resin approaches but does not exceed 200 pCi/g. At this point the enhanced radium content radium-containing strong acid cation exchange resin is recovered from the contacting zone.
  • the recovered enhanced radium content radium-containing strong acid cation exchange resin having a radium content approaching but not exceeding 200 pCi/g is then admixed and encapsulated with mineral-based material and formed into solid bodies of encapsulated enhanced radium content radium-containing strong acid cation exchange resin.
  • strong acid cation exchange resins refer to polymeric resins having acid groups with a pka of less than 4, preferably less than 3, more preferably less than 2 and most preferably less than 1, attached thereto, wherein the acid group is neutralized to an acid metal salt such as an alkali or alkaline metal salt.
  • Preferred salts include sodium, potassium, calcium and the like.
  • Preferred polymeric resins include polystyrene resin and preferred acid groups include sulfonic acid groups.
  • Preferred resins are highly crosslinked, macroporous strong acid cation exchange resin based on sulfonated polystyrene, crosslinked with divinylbenzene and are available from Resintech, West Berlin, NJ, USA under the tradename SACMP.
  • this invention relates to a process comprising
  • the strong acid cation exchange resin is a macroreticular resin.
  • the macroreticular resin is a styrene -based resin.
  • the styrene-based macroreticular resin is a sulfonate-containing cross-linked resin.
  • the mineral-based material comprises clay.
  • the contacting is stopped when the radium content of the enhanced radium content radium-containing strong acid cation exchange resin is greater than about 100 pCi/g. In some embodiments, the contacting is stopped when the radium content of the enhanced radium content radium-containing strong acid cation exchange resin is greater than about 150 pCi/g. In some embodiments, the contacting is stopped when the radium content of the enhanced radium content radium-containing strong acid cation exchange resin is greater than about 180 pCi/g.
  • the contacting is stopped when the radium content of the enhanced radium content radium-containing strong acid cation exchange resin is greater than about 190 pCi/g. In all cases, the radium content of the enhanced radium content radium-containing strong acid cation exchange resin does not exceed 200 pCi/g.
  • the encapsulating causes substantially all enhanced radium content radium-containing strong acid cation exchange resin is encapsulated in mineral- based material and forms solid bodies.
  • a greater than about 60% of the enhanced radium content radium-containing strong acid cation exchange resin is encapsulated in mineral-based material and forms solid bodies. In some embodiments, a greater than about 80% of the enhanced radium content radium-containing strong acid cation exchange resin is encapsulated in the mineral-based material and forms solid bodies. In some embodiments, a greater than about 90% of the enhanced radium content radium-containing strong acid cation exchange resin is encapsulated in mineral-based material and forms solid bodies. In some embodiments, a greater than about 95% of the enhanced radium content radium- containing strong acid cation exchange resin is encapsulated in the mineral-based material and forms solid bodies.
  • the encapsulating comprises dewatering the mineral-based material after admixing.
  • the radium-contaminated water has a pH of about or below 5.5. In some embodiments, the radium-contaminated water has a pH of about 5.5.
  • the radium-contaminated water additionally comprises iron ions.
  • the invention provides a process comprising:
  • a strong acid cation exchange resin such as SACMP from Resintech, West Berlin, New Jersey, U.S.A
  • the radium- contaminated water is allowed to flow through the vessel comprising the resin under radium-exchanging conditions at a flow rate of 10-12 gallons per minute per square foot of vessel cross-sectional area under ambient conditions.
  • the water effluent from the contacting zone preferably has a reduce radium level of less than 5 picocuries per liter (pCi/L). The process is continued until the radium absorbed by the resin reaches a concentration of 200 picocuries per gram (pCi/g) of resin.

Abstract

La présente invention concerne le retrait et l'élimination du radium présent dans des sources d'eau potable.
PCT/US2009/040372 2008-04-18 2009-04-13 Retrait et élimination du radium WO2009129184A1 (fr)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US4634908P 2008-04-18 2008-04-18
US61/046,349 2008-04-18

Publications (1)

Publication Number Publication Date
WO2009129184A1 true WO2009129184A1 (fr) 2009-10-22

Family

ID=41199438

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/US2009/040372 WO2009129184A1 (fr) 2008-04-18 2009-04-13 Retrait et élimination du radium

Country Status (1)

Country Link
WO (1) WO2009129184A1 (fr)

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4800024A (en) * 1986-04-07 1989-01-24 Iso-Clear Systems Corporation Removal of heavy metals and heavy metal radioactive isotopes from liquids

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4800024A (en) * 1986-04-07 1989-01-24 Iso-Clear Systems Corporation Removal of heavy metals and heavy metal radioactive isotopes from liquids

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