KR101068008B1 - Construction material using sludge and its manufacturing method - Google Patents
Construction material using sludge and its manufacturing method Download PDFInfo
- Publication number
- KR101068008B1 KR101068008B1 KR20090007310A KR20090007310A KR101068008B1 KR 101068008 B1 KR101068008 B1 KR 101068008B1 KR 20090007310 A KR20090007310 A KR 20090007310A KR 20090007310 A KR20090007310 A KR 20090007310A KR 101068008 B1 KR101068008 B1 KR 101068008B1
- Authority
- KR
- South Korea
- Prior art keywords
- sludge
- weight
- binder
- alkaline earth
- water
- Prior art date
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 106
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 31
- 239000004035 construction material Substances 0.000 title description 5
- 239000011230 binding agent Substances 0.000 claims abstract description 62
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 54
- 229910001868 water Inorganic materials 0.000 claims abstract description 52
- 239000000203 mixture Substances 0.000 claims abstract description 33
- 239000004566 building material Substances 0.000 claims abstract description 27
- 229910052500 inorganic mineral Inorganic materials 0.000 claims abstract description 26
- 239000011707 mineral Substances 0.000 claims abstract description 26
- 239000000843 powder Substances 0.000 claims abstract description 20
- 229910052784 alkaline earth metal Inorganic materials 0.000 claims abstract description 18
- 229910052783 alkali metal Inorganic materials 0.000 claims abstract description 17
- 150000001340 alkali metals Chemical class 0.000 claims abstract description 17
- 150000001342 alkaline earth metals Chemical class 0.000 claims abstract description 17
- 150000001875 compounds Chemical class 0.000 claims abstract description 14
- 229910001617 alkaline earth metal chloride Inorganic materials 0.000 claims abstract description 13
- 239000007788 liquid Substances 0.000 claims abstract description 13
- 229910001514 alkali metal chloride Inorganic materials 0.000 claims abstract description 12
- 229910052782 aluminium Inorganic materials 0.000 claims abstract description 12
- 239000002351 wastewater Substances 0.000 claims abstract description 12
- 229910052791 calcium Inorganic materials 0.000 claims abstract description 11
- 229910052749 magnesium Inorganic materials 0.000 claims abstract description 11
- 238000000465 moulding Methods 0.000 claims abstract description 11
- 229910052761 rare earth metal Inorganic materials 0.000 claims abstract description 11
- 239000010801 sewage sludge Substances 0.000 claims abstract description 11
- 229910052710 silicon Inorganic materials 0.000 claims abstract description 11
- 229910052801 chlorine Inorganic materials 0.000 claims abstract description 10
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 10
- 229910052717 sulfur Inorganic materials 0.000 claims abstract description 10
- 239000003002 pH adjusting agent Substances 0.000 claims abstract description 9
- 239000013049 sediment Substances 0.000 claims abstract description 9
- 229910052742 iron Inorganic materials 0.000 claims abstract description 7
- 238000002156 mixing Methods 0.000 claims abstract description 7
- 229910052748 manganese Inorganic materials 0.000 claims abstract description 6
- 229910052738 indium Inorganic materials 0.000 claims description 4
- 239000003513 alkali Substances 0.000 claims description 2
- 230000015572 biosynthetic process Effects 0.000 abstract description 11
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 11
- 239000004568 cement Substances 0.000 abstract description 9
- 229910010272 inorganic material Inorganic materials 0.000 abstract description 8
- 239000011147 inorganic material Substances 0.000 abstract description 8
- 238000009833 condensation Methods 0.000 abstract description 5
- 230000005494 condensation Effects 0.000 abstract description 5
- 239000003344 environmental pollutant Substances 0.000 abstract description 5
- 238000003912 environmental pollution Methods 0.000 abstract description 5
- 231100000719 pollutant Toxicity 0.000 abstract description 5
- 238000006243 chemical reaction Methods 0.000 abstract description 4
- 238000002425 crystallisation Methods 0.000 abstract description 4
- 230000008025 crystallization Effects 0.000 abstract description 4
- 239000011343 solid material Substances 0.000 abstract description 3
- 239000000126 substance Substances 0.000 abstract description 3
- 235000010755 mineral Nutrition 0.000 description 23
- 238000000034 method Methods 0.000 description 16
- 239000000463 material Substances 0.000 description 9
- 239000000460 chlorine Substances 0.000 description 7
- 239000000356 contaminant Substances 0.000 description 6
- 239000002245 particle Substances 0.000 description 6
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 5
- 239000000047 product Substances 0.000 description 5
- 238000004064 recycling Methods 0.000 description 5
- 239000010865 sewage Substances 0.000 description 5
- 239000002699 waste material Substances 0.000 description 4
- 230000006378 damage Effects 0.000 description 3
- 238000001035 drying Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000002689 soil Substances 0.000 description 3
- 231100000331 toxic Toxicity 0.000 description 3
- 230000002588 toxic effect Effects 0.000 description 3
- HGINCPLSRVDWNT-UHFFFAOYSA-N Acrolein Chemical compound C=CC=O HGINCPLSRVDWNT-UHFFFAOYSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 150000001805 chlorine compounds Chemical class 0.000 description 2
- 239000004927 clay Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 230000009931 harmful effect Effects 0.000 description 2
- 229910052700 potassium Inorganic materials 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 239000008213 purified water Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 239000002688 soil aggregate Substances 0.000 description 2
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 1
- 239000005995 Aluminium silicate Substances 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 229910052684 Cerium Inorganic materials 0.000 description 1
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 1
- 229910052692 Dysprosium Inorganic materials 0.000 description 1
- 229910052691 Erbium Inorganic materials 0.000 description 1
- 229910052693 Europium Inorganic materials 0.000 description 1
- 229910052688 Gadolinium Inorganic materials 0.000 description 1
- 206010019233 Headaches Diseases 0.000 description 1
- 229910052689 Holmium Inorganic materials 0.000 description 1
- 229910052779 Neodymium Inorganic materials 0.000 description 1
- 229910052777 Praseodymium Inorganic materials 0.000 description 1
- 229910052773 Promethium Inorganic materials 0.000 description 1
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 1
- 229910052772 Samarium Inorganic materials 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- 229910052771 Terbium Inorganic materials 0.000 description 1
- 206010047700 Vomiting Diseases 0.000 description 1
- 241000607479 Yersinia pestis Species 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000002671 adjuvant Substances 0.000 description 1
- 239000012615 aggregate Substances 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 235000012211 aluminium silicate Nutrition 0.000 description 1
- 244000052616 bacterial pathogen Species 0.000 description 1
- 230000003385 bacteriostatic effect Effects 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 229910052792 caesium Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 231100000357 carcinogen Toxicity 0.000 description 1
- 239000003183 carcinogenic agent Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- ZMIGMASIKSOYAM-UHFFFAOYSA-N cerium Chemical compound [Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce] ZMIGMASIKSOYAM-UHFFFAOYSA-N 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- KBQHZAAAGSGFKK-UHFFFAOYSA-N dysprosium atom Chemical compound [Dy] KBQHZAAAGSGFKK-UHFFFAOYSA-N 0.000 description 1
- 235000013601 eggs Nutrition 0.000 description 1
- UYAHIZSMUZPPFV-UHFFFAOYSA-N erbium Chemical compound [Er] UYAHIZSMUZPPFV-UHFFFAOYSA-N 0.000 description 1
- OGPBJKLSAFTDLK-UHFFFAOYSA-N europium atom Chemical compound [Eu] OGPBJKLSAFTDLK-UHFFFAOYSA-N 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- UIWYJDYFSGRHKR-UHFFFAOYSA-N gadolinium atom Chemical compound [Gd] UIWYJDYFSGRHKR-UHFFFAOYSA-N 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 231100000869 headache Toxicity 0.000 description 1
- KJZYNXUDTRRSPN-UHFFFAOYSA-N holmium atom Chemical compound [Ho] KJZYNXUDTRRSPN-UHFFFAOYSA-N 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 description 1
- 229910052746 lanthanum Inorganic materials 0.000 description 1
- FZLIPJUXYLNCLC-UHFFFAOYSA-N lanthanum atom Chemical compound [La] FZLIPJUXYLNCLC-UHFFFAOYSA-N 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 229910052744 lithium Inorganic materials 0.000 description 1
- 230000005415 magnetization Effects 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 230000010534 mechanism of action Effects 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- WSFSSNUMVMOOMR-NJFSPNSNSA-N methanone Chemical compound O=[14CH2] WSFSSNUMVMOOMR-NJFSPNSNSA-N 0.000 description 1
- QEFYFXOXNSNQGX-UHFFFAOYSA-N neodymium atom Chemical compound [Nd] QEFYFXOXNSNQGX-UHFFFAOYSA-N 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- PUDIUYLPXJFUGB-UHFFFAOYSA-N praseodymium atom Chemical compound [Pr] PUDIUYLPXJFUGB-UHFFFAOYSA-N 0.000 description 1
- VQMWBBYLQSCNPO-UHFFFAOYSA-N promethium atom Chemical compound [Pm] VQMWBBYLQSCNPO-UHFFFAOYSA-N 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 230000002787 reinforcement Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 229910052701 rubidium Inorganic materials 0.000 description 1
- 229910052707 ruthenium Inorganic materials 0.000 description 1
- KZUNJOHGWZRPMI-UHFFFAOYSA-N samarium atom Chemical compound [Sm] KZUNJOHGWZRPMI-UHFFFAOYSA-N 0.000 description 1
- 229910052706 scandium Inorganic materials 0.000 description 1
- SIXSYDAISGFNSX-UHFFFAOYSA-N scandium atom Chemical compound [Sc] SIXSYDAISGFNSX-UHFFFAOYSA-N 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 230000002269 spontaneous effect Effects 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 229920003002 synthetic resin Polymers 0.000 description 1
- 239000000057 synthetic resin Substances 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- GZCRRIHWUXGPOV-UHFFFAOYSA-N terbium atom Chemical compound [Tb] GZCRRIHWUXGPOV-UHFFFAOYSA-N 0.000 description 1
- 239000004753 textile Substances 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- XREXPQGDOPQPAH-QKUPJAQQSA-K trisodium;[(z)-18-[1,3-bis[[(z)-12-sulfonatooxyoctadec-9-enoyl]oxy]propan-2-yloxy]-18-oxooctadec-9-en-7-yl] sulfate Chemical compound [Na+].[Na+].[Na+].CCCCCCC(OS([O-])(=O)=O)C\C=C/CCCCCCCC(=O)OCC(OC(=O)CCCCCCC\C=C/CC(CCCCCC)OS([O-])(=O)=O)COC(=O)CCCCCCC\C=C/CC(CCCCCC)OS([O-])(=O)=O XREXPQGDOPQPAH-QKUPJAQQSA-K 0.000 description 1
- 238000002525 ultrasonication Methods 0.000 description 1
- 230000008673 vomiting Effects 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 229910052727 yttrium Inorganic materials 0.000 description 1
- VWQVUPCCIRVNHF-UHFFFAOYSA-N yttrium atom Chemical compound [Y] VWQVUPCCIRVNHF-UHFFFAOYSA-N 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/24—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing alkyl, ammonium or metal silicates; containing silica sols
- C04B28/26—Silicates of the alkali metals
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B18/00—Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
- C04B18/04—Waste materials; Refuse
- C04B18/0418—Wet materials, e.g. slurries
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B28—WORKING CEMENT, CLAY, OR STONE
- B28B—SHAPING CLAY OR OTHER CERAMIC COMPOSITIONS; SHAPING SLAG; SHAPING MIXTURES CONTAINING CEMENTITIOUS MATERIAL, e.g. PLASTER
- B28B3/00—Producing shaped articles from the material by using presses; Presses specially adapted therefor
- B28B3/02—Producing shaped articles from the material by using presses; Presses specially adapted therefor wherein a ram exerts pressure on the material in a moulding space; Ram heads of special form
- B28B3/022—Producing shaped articles from the material by using presses; Presses specially adapted therefor wherein a ram exerts pressure on the material in a moulding space; Ram heads of special form combined with vibrating or jolting
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B18/00—Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
- C04B18/04—Waste materials; Refuse
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/24—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing alkyl, ammonium or metal silicates; containing silica sols
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Structural Engineering (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Environmental & Geological Engineering (AREA)
- Civil Engineering (AREA)
- Manufacturing & Machinery (AREA)
- Mechanical Engineering (AREA)
- Treatment Of Sludge (AREA)
Abstract
본 발명은 슬러지를 이용한 건자재 및 이의 제조 방법에 관한 것으로, 정수슬러지, 하수슬러지, 폐수슬러지, 퇴적슬러지 등과 같은 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%로 구성되어지되 바인더는 C 5 ∼ 71.7%, O 20 ∼ 86.7%, Mg 1 ∼ 67.7%, Al 1 ∼ 67.7%, Si 3 ∼ 69.7%, S 0.5 ∼ 67.2%, Cl 0.5 ∼ 67.2%, Ca 2 ∼ 68.7%, Ti 0.1 ∼ 66.8%, Mn 0.05 ∼ 66.75%, Fe 0.05 ∼ 66.75% 및 In 0.1 ∼ 66.8%의 원소 구성비를 갖는 광물질 분말 10 ∼ 90중량%와 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 클러스터화된 물에 투입하여 알칼리금속 및 알칼리토금속으로 구성되는 군으로부터 선택된 적어도 1종 이상의 알칼리금속 및 알칼리토금속을 용출시킨 용액에 희토류 원소를 전체 클러스터화된 물의 중량에 대하여 1중량% 미만 함유하는 물과 pH조절제를 혼합한 액상의 결합제 10 ∼ 90중량%로 구성되고, 상기 슬러지와 바인더를 준비하는 단계; 상기 슬러지와 바인더를 혼합하는 단계; 상기 슬러지와 바인더의 혼합물을 성형틀에 투입하는 단계; 상기 성형틀에 진동을 가한 후, 슬러지와과 바인더의 혼합물을 2차 투입한 다음 프레스 성형하는 단계; 탈형 후 자연양생하여 고화시키는 단계로 구성되는 방법으로 건자재를 제조함으로써 슬러지에 존재하는 무기물 및 바인더 내부의 무기물 용탈(dissolusion) → 아쿠아졸 형성(formation of aquasols) → 응축(condensation) → 겔 형성(gel formation) → 결정화(crystallization)하는 반응으로 강한 결합력이 발휘되기 때문에 일정 강도 이상의 건자재를 제조할 수 있을 뿐만 아니라 시멘트의 사용으로 인한 문제점을 해결할 수 있고, 무기물로만 이루어진 바인더를 사용함으로써 오염물의 배출이 없어 환경 오염을 유발하지 않고, 슬러지에 함유된 중금속이나 오염물질들이 강력하게 결합되어 있어 2차 오염의 문제가 없으며, 자연양생을 행함으로써 경제적일 뿐만 아니라 간단한 방법으로 건자재를 제조할 수 있다.The present invention relates to a building material using sludge and a method for producing the same, comprising sludge such as purified sludge, sewage sludge, wastewater sludge, sediment sludge, etc., and 60 to 95% by weight of the sludge and 5 to 40% by weight of the binder. 71.7%, O 20-86.7%, Mg 1-67.7%, Al 1-67.7%, Si 3-69.7%, S 0.5-67.2%, Cl 0.5-67.2%, Ca 2-68.7%, Ti 0.1-66.8% At least one compound selected from the group consisting of 10 to 90% by weight of mineral powder having an elemental composition ratio of 0.05 to 66.75%, Mn 0.05 to 66.75% and Fe 0.1 to 66.8%, and alkali metal chlorides and alkaline earth metal chlorides. Water containing less than 1% by weight of rare earth elements in a solution of at least one alkali metal and alkaline earth metal selected from the group consisting of alkali metals and alkaline earth metals in clustered water, based on the weight of the total clustered water And Comprising 10 to 90% by weight of the liquid binder mixed with a pH adjuster, preparing the sludge and the binder; Mixing the sludge and the binder; Injecting a mixture of the sludge and the binder into a mold; Applying vibration to the mold, and then press molding the mixture of sludge and binder; Dissolving the inorganic substances present in the sludge and forming the inorganic materials in the sludge by forming the solid materials after natural curing and solidifying after demolding → formation of aquasols → condensation → gel formation (gel) formation) Because strong binding force is exerted by the crystallization reaction, it is possible not only to manufacture building materials with a certain strength, but also to solve the problems caused by the use of cement. Without causing environmental pollution, heavy metals or pollutants contained in the sludge is strongly combined, there is no problem of secondary pollution, it is economical and can be manufactured in a simple way by performing natural curing.
건자재, 건자재 제조방법, 무기질 바인더, 슬러지 Building materials, manufacturing method, inorganic binder, sludge
Description
본 발명은 슬러지를 이용한 건자재 및 이의 제조 방법에 관한 것으로, 좀 더 구체적으로는 정수슬러지, 하수슬러지, 폐수슬러지, 퇴적슬러지 등과 같은 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%로 구성되어지되 바인더는 C 5 ∼ 71.7%, O 20 ∼ 86.7%, Mg 1 ∼ 67.7%, Al 1 ∼ 67.7%, Si 3 ∼ 69.7%, S 0.5 ∼ 67.2%, Cl 0.5 ∼ 67.2%, Ca 2 ∼ 68.7%, Ti 0.1 ∼ 66.8%, Mn 0.05 ∼ 66.75%, Fe 0.05 ∼ 66.75% 및 In 0.1 ∼ 66.8%의 원소 구성비를 갖는 광물질 분말 10 ∼ 90중량%와 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 클러스터화된 물에 투입하여 알칼리금속 및 알칼리토금속으로 구성되는 군으로부터 선택된 적어도 1종 이상의 알칼리금속 및 알칼리토금속을 용출시킨 용액에 희토류 원소를 전체 클러스터화된 물의 중량에 대하여 1중량% 미만 함유하는 물과 pH조절제를 혼합한 액상의 결합제 10 ∼ 90중량%로 구성되고, 상기 슬러지와 바인더를 준비하는 단계; 상기 슬러지와 바인더를 혼합하는 단계; 상기 슬러지와 바인더의 혼합물을 성형틀에 투입하는 단계; 상기 성형틀에 진동을 가한 후, 슬러지와과 바인더의 혼합물을 2차 투입한 다음 프레스 성형하는 단계; 탈형 후 자연양생하여 고화시키는 단계로 구성되는 방법으로 건자재를 제조함으로써 슬러지에 존재하는 무기물 및 바인더 내부의 무기물 용탈(dissolusion) → 아쿠아졸 형성(formation of aquasols) → 응축(condensation) → 겔 형성(gel formation) → 결정화(crystallization)하는 반응으로 강한 결합력이 발휘되기 때문에 일정 강도 이상의 건자재를 제조할 수 있을 뿐만 아니라 시멘트의 사용으로 인한 문제점을 해결할 수 있고, 무기물로만 이루어진 바인더를 사용함으로써 오염물의 배출이 없어 환경 오염을 유발하지 않고, 슬러지에 함유된 중금속이나 오염물질들이 강력하게 결합되어 있어 2차 오염의 문제가 없으며, 자연양생을 행함으로써 경제적일 뿐만 아니라 간단한 방법으로 건자재를 제조할 수 있는 슬러지를 이용한 건자재 및 이의 제조 방법에 관한 것이다.The present invention relates to a building material using sludge and a method for manufacturing the same, and more specifically, composed of 60 to 95% by weight of sludge such as purified sludge, sewage sludge, wastewater sludge, sediment sludge and 5 to 40% by weight of the binder. The binder is C 5-71.7%, O 20-86.7%, Mg 1-67.7%, Al 1-67.7%, Si 3-69.7%, S 0.5-67.2%, Cl 0.5-67.2%, Ca 2 68.7%, 10 to 90% by weight of mineral powder having an elemental composition ratio of 0.1 to 66.8% of Ti, 0.05 to 66.75% of Mn, 0.05 to 66.75% of Fe and In 0.1 to 66.8%, and at least one selected from the group consisting of alkali metal chlorides and alkaline earth metal chlorides. 1 weight of the rare earth element is added to the weight of the total clustered water in a solution in which at least one compound is added to clustered water and eluted at least one alkali metal and alkaline earth metal selected from the group consisting of alkali metals and alkaline earth metals. % Only it consists of water with a pH control agent which contains as binder 10 to 90% by weight of a liquid mixture, comprising: preparing the sludge with the binder; Mixing the sludge and the binder; Injecting a mixture of the sludge and the binder into a mold; Applying vibration to the mold, and then press molding the mixture of sludge and binder; Dissolving the inorganic substances present in the sludge and forming the inorganic materials in the sludge by forming the solid materials after natural curing and solidifying after demolding → formation of aquasols → condensation → gel formation (gel) formation) Because strong binding force is exerted by the crystallization reaction, it is possible not only to manufacture building materials with a certain strength, but also to solve the problems caused by the use of cement. It does not cause environmental pollution, and heavy metals or contaminants contained in the sludge are strongly combined, so there is no problem of secondary pollution, and it is economical by performing natural curing and uses sludge that can be manufactured in a simple way. It relates to a building material and a manufacturing method thereof.
일반적으로 슬러지는 수돗물을 생산하는 과정에서 발생하는 부산폐기물인 정수슬러지, 하수 및 폐수처리장에서 발생되는 하수 및 폐수슬러지, 하천, 호소, 해안가에 자연발생적으로 퇴적하여 생성되는 최적슬러지 등이 있다. 이들 슬러리 중 퇴적슬러리는 재활용시 오염도가 다른 슬러지에 비하여 높지는 않지만 인체에 해를 미칠 정도의 오염물질이 함유되어 있고, 정수, 하수 및 폐수슬러지들은 처리과정에서 최종적으로 응집, 침강되어 발생되는 부산물로써, 함수율이 매우 높고 수분 탈리가 어려우며 중금속으로 오염되어 있다. 또한, 다량의 유기물이 함유되어 있어 방치하면 쉽게 자연 분해되어 심한 악취를 풍기고, 주변 환경을 오염시키며 체내 흡입 시 두통과 구토를 일으키는 원인이 되기도 한다.In general, sludge is an optimum sludge produced by spontaneous deposition on sewage and wastewater sludge, streams, lakes, and coasts, which are by-product wastewater sludge produced in the production of tap water, sewage and wastewater treatment plants. Among these slurries, sediment sludge is not as high as other sludges in recycling, but contains contaminants that are harmful to the human body. The purified water, sewage and wastewater sludges are by-products generated by the final flocculation and sedimentation during the treatment process. As a result, the water content is very high, the water is difficult to desorb and contaminated with heavy metals. In addition, it contains a large amount of organic matter easily decomposes naturally and gives off a bad smell, pollutes the surrounding environment and causes headaches and vomiting when inhaled.
상기와 같은 슬러지의 처리는 대부분 해양투기나 소각처리 혹은 단순매립에 의존하고 있다. 그러나, 해양투기의 경우 갈수록 심화되는 해양생태계 파괴의 주범 으로 인식되어 2011년부터 해양투기가 전면 금지될 예정이다. 또한, 소각 처리의 경우, 불완전한 연소로 인한 다이옥신, 포름알데히드, 아크로레인 등 이른바 맹독성 발암물질을 배출시켜 사회문제를 야기하고, 건설 및 유지비용이 막대하여 에너지자원이 부족한 우리나라의 실정에는 적합하지 않은 방법이다. 그리고, 매립의 경우에도 갈수록 매립장 확보가 어려워지고, 침출수 문제, 병원성 세균, 해충의 알, 분진발생, 악취발생 등과 관련된 민원이 끊임없이 제기되어 처리하기가 쉽지 않은 상태이다.The treatment of sludge as described above is mostly dependent on ocean dumping, incineration or simple landfill. However, in the case of ocean dumping, it is recognized as the main culprit of the deepening of marine ecosystem destruction. In addition, incineration causes social problems by releasing so-called highly toxic carcinogens such as dioxin, formaldehyde, and acrolein due to incomplete combustion, which is not suitable for the situation of Korea where energy resources are insufficient due to the high construction and maintenance costs. It is a way. Also, even in the case of landfill, it is difficult to secure landfill, and complaints related to leachate problems, pathogenic bacteria, eggs of pests, dust generation, odor occurrence, etc. are constantly raised and difficult to handle.
이러한 슬러지를 재활용함으로써 슬러지의 처리를 행하는 기술이 많이 연구되고 있다. 예를 들어, 하수슬러지를 이용한 퇴비화, 정수 및 하수슬러지를 이용한 복토용, 성토용, 지반강화용, 토지개량용 그리고 건축자재용 흙골재로의 개발, 시멘트 원료로의 사용에 대한 많은 연구가 진행되고 있는 실정이다.Many techniques for treating sludge by recycling such sludge have been studied. For example, many studies have been conducted on composting using sewage sludge, covering soil using sewage sludge, soil filling, ground reinforcement, land improvement and building materials as soil aggregates, and using cement as raw materials. It's happening.
특히, 건자재로의 이용은 특허 제860017호 "공정오니 및 슬러지를 이용한 토목 및 건축자재용 흙골재조성물 및 이의 제조방법", 특허 제602441호 "폐기물을 이용한 고형화 제품 제조 방법과 제조 시스템", 특허 제450898호 "하수슬러지를 이용한 소성 건자재 제조방법", 특허 제812828호 "하ㆍ폐수슬러지를 고형화시키는 고화제(파라픽스) 및 이를이용하여 제조되는 복토재", 특허 제757518호 "폐산, 폐알칼리 및 슬러지의 처리 및 자원화 방법", 특허 제490731호 "폐자재슬러지를 로타리킬른에서 건조 또는 소성하여 토목, 건축자재를 제조하는 방법", 특허 제458876호 "섬유 폐기 슬러지를 재활용한 건축 자재 제조방법", 특허 제517230호 "황토, 점토, 백토 및 고령토로 이루어진 여재원료 및 음식물쓰레기, 유기성폐기물, 산업용폐기 물로 이루어진 다공성 세라믹 제조방법", 특허 제583763호 "하수처리장 탈수슬러지를 활용한 경량골재의 제조방법", 특허 제520463호 "유기성 슬러지를 활용한 불연성 경량 건축마감재료의 제조방법 및 그 제품" 등과 같이 많은 문헌에 기재되어 있다.Particularly, the use of building materials is described in Korean Patent No. 860017 "Soil Aggregate Composition for Civil Engineering and Building Materials Using Process Sludge and Sludge and Its Manufacturing Method", Patent No. 60441 "Method and Manufacturing System for Solidified Product Using Waste", Patent No. 450898 "Method for manufacturing fired construction materials using sewage sludge", Patent No. 812828 "Solidizer for solidifying sewage and wastewater sludge (Parafix) and cover material manufactured using it", Patent No. 757518 "Waste acid, waste alkali" And Sludge Treatment and Recycling Method ", Patent No. 490731" Method for Manufacturing Civil and Building Materials by Drying or Firing Waste Material Sludge in Rotary Kiln ", Patent No. 458876," Manufacturing Material for Recycling Textile Sludge " ", Patent No. 517230" Polymer raw material consisting of ocher, clay, clay and kaolin and a method for producing porous ceramics consisting of food waste, organic waste, industrial waste " , Patent No. 583763, "Method of Manufacturing Lightweight Aggregate Using Sewage Treatment Sludge," Patent No. 520463, "Method of Manufacturing Nonflammable Lightweight Building Finish Material Using Organic Sludge and Its Product", etc. .
그러나, 종래의 슬러지를 재활용하여 건자재를 제조하는 방법들은 제조되는 제품에서 중금속은 물론 기타 오염물질이 용출되어 2차 오염을 일으켜 토양 및 주변 환경을 오염시키는 문제점들이 있고, 제조되는 제품의 강도가 만족스럽지 못하여 실제 적용이 미약하며, 시멘트를 일정량 사용하고 있어 시멘트 사용으로 인한 환경오염 문제 및 시멘트 제조시 발생되는 이산화탄소로 인한 환경 파괴를 유발하고, 제조 공정이 복잡하며, 많은 전처리 공정 및 제조 공정을 거쳐야 하는 등의 문제점이 있었다. However, conventional methods for manufacturing dry materials by recycling sludge have problems of eluting heavy metals as well as other pollutants from the manufactured products, causing secondary pollution, contaminating soil and the surrounding environment, and satisfactory strength of the manufactured products. Because it is not practical, its practical application is weak, and because a certain amount of cement is used, it causes environmental pollution problems due to the use of cement and environmental damage caused by carbon dioxide generated during cement production, and the manufacturing process is complicated, and it has to go through many pretreatment and manufacturing processes. There was a problem such as.
따라서, 본 발명의 목적은 슬러지를 용이하게 재활용할 수 있으면서 일정 강도 이상의 건자재를 제조할 수 있을 뿐만 아니라 시멘트의 사용으로 인한 문제점을 해결할 수 있고, 무기물로만 이루어진 바인더를 사용함으로써 오염물의 배출이 없어 환경 오염을 유발하지 않고, 슬러지에 함유된 중금속이나 오염물질들이 강력하게 결합되어 있어 2차 오염의 문제가 없으며, 자연양생을 행함으로써 경제적인 슬러지를 이용한 건자재를 제공하는 데 있다.Accordingly, an object of the present invention is to be able to easily recycle the sludge and to produce a building material of a certain strength or more, and to solve the problems caused by the use of cement, and by using a binder composed only of inorganic material, there is no discharge of contaminants. Without causing pollution, heavy metals or contaminants contained in the sludge is strongly combined, there is no problem of secondary pollution, and by providing natural curing material to provide economical sludge.
본 발명의 다른 목적은 상기 목적의 건자재를 간단한 방법으로 용이하게 제조하는 방법을 제공하는 데 있다.Another object of the present invention is to provide a method for easily manufacturing a building material of the above object by a simple method.
상기 목적들 뿐만 아니라 용이하게 표출될 수 있는 또 다른 목적들을 달성하기 위하여 본 발명에서는 정수슬러지, 하수슬러지, 폐수슬러지, 퇴적슬러지 등과 같은 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%로 구성되어지되 바인더는 C 5 ∼ 71.7%, O 20 ∼ 86.7%, Mg 1 ∼ 67.7%, Al 1 ∼ 67.7%, Si 3 ∼ 69.7%, S 0.5 ∼ 67.2%, Cl 0.5 ∼ 67.2%, Ca 2 ∼ 68.7%, Ti 0.1 ∼ 66.8%, Mn 0.05 ∼ 66.75%, Fe 0.05 ∼ 66.75% 및 In 0.1 ∼ 66.8%의 원소 구성비를 갖는 광물질 분말 10 ∼ 90중량%와 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 클러스터화된 물에 투입하여 알칼리금속 및 알칼리토금속으로 구성되는 군으로부터 선택된 적어도 1종 이상의 알칼리금속 및 알칼리토금속을 용출시킨 용액에 희토류 원소를 전체 클러스터화된 물의 중량에 대하여 1중량% 미만 함유하는 물과 pH조절제를 혼합한 액상의 결합제 10 ∼ 90중량%로 구성되고, 상기 슬러지와 바인더를 준비하는 단계; 상기 슬러지와 바인더를 혼합하는 단계; 상기 슬러지와 바인더의 혼합물을 성형틀에 투입하는 단계; 상기 성형틀에 진동을 가한 후, 슬러지와과 바인더의 혼합물을 2차 투입한 다음 프레스 성형하는 단계; 탈형 후 자연양생하여 고화시키는 단계로 구성되는 방법으로 건자재를 제조함으로써 슬러지에 존재하는 무기물 및 바인더 내부의 무기물 용탈(dissolusion) → 아쿠아졸 형성(formation of aquasols) → 응축(condensation) → 겔 형성(gel formation) → 결정화(crystallization)하는 반응으로 강한 결합력이 발휘되기 때문에 일정 강도 이상의 건자재를 제조할 수 있을 뿐만 아니라 시멘트의 사용으로 인한 문제점을 해결할 수 있고, 무기물로만 이루어진 바인더를 사용함으로써 오염물의 배출이 없어 환경 오염을 유발하지 않고, 슬러지에 함유된 중금속이나 오염물질들이 강력하게 결합되어 있어 2차 오염의 문제가 없으며, 자연양생을 행함으로써 경제적일 뿐만 아니라 간단한 방법으로 건자재를 제조할 수 있다.In order to achieve the above objects as well as other objects that can be easily expressed in the present invention consists of 60 to 95% by weight sludge, such as purified sludge, sewage sludge, wastewater sludge, sediment sludge and 5 to 40% by weight binder The binder is C 5-71.7%, O 20-86.7%, Mg 1-67.7%, Al 1-67.7%, Si 3-69.7%, S 0.5-67.2%, Cl 0.5-67.2%, Ca 2 68.7% Selected from the group consisting of 10 to 90% by weight of mineral powder having an elemental composition ratio of 0.1 to 66.8%, Ti 0.05 to 66.75%, Fe 0.05 to 66.75%, and In 0.1 to 66.8%, and alkali metal chlorides and alkaline earth metal chlorides. The rare earth element is added to the weight of the total clustered water in a solution in which at least one compound is added to the clustered water to elute at least one alkali metal and alkaline earth metal selected from the group consisting of alkali metals and alkaline earth metals. W is composed of a first binder 10 to 90% by weight of the liquid phase a mixture of water and a pH adjusting agent containing less than% by weight, comprising the steps of preparing the sludge and a binder; Mixing the sludge and the binder; Injecting a mixture of the sludge and the binder into a mold; Applying vibration to the mold, and then press molding the mixture of sludge and binder; Dissolving the inorganic substances present in the sludge and forming the inorganic materials in the sludge by forming the solid materials after natural curing and solidifying after demolding → formation of aquasols → condensation → gel formation (gel) formation) Because strong binding force is exerted by the crystallization reaction, it is possible not only to manufacture building materials with a certain strength, but also to solve the problems caused by the use of cement. Without causing environmental pollution, heavy metals or pollutants contained in the sludge is strongly combined, there is no problem of secondary pollution, it is economical and can be manufactured in a simple way by performing natural curing.
본 발명에 따른 슬러지를 이용한 건자재 및 이의 제조방법은 강한 결합력이 발휘되기 때문에 일정 강도 이상의 건자재를 제조할 수 있을 뿐만 아니라 시멘트의 사용으로 인한 문제점을 해결할 수 있고, 무기물로만 이루어진 바인더를 사용함으로써 오염물의 배출이 없어 환경 오염을 유발하지 않고, 슬러지에 함유된 중금속이나 오염물질들이 강력하게 결합되어 있어 2차 오염의 문제가 없으며, 자연양생을 행함으로써 경제적일 뿐만 아니라 간단한 방법으로 건자재를 제조할 수 있는 효과 가 있다.The building material using sludge according to the present invention and its manufacturing method can be used to produce a building material of a certain strength or more because of the strong binding force, and can solve the problems caused by the use of cement, by using a binder composed only of inorganic materials There is no emission, which does not cause environmental pollution, and the heavy metals or pollutants contained in the sludge are strongly combined, so there is no problem of secondary pollution, and it is economical and can be manufactured in a simple way by performing natural curing. There is an effect.
본 발명에 따른 슬러지를 이용한 건자재는 정수슬러지, 하수슬러지, 폐수슬러지, 퇴적슬러지 등과 같은 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%로 구성되어지되 바인더는 C 5 ∼ 71.7%, O 20 ∼ 86.7%, Mg 1 ∼ 67.7%, Al 1 ∼ 67.7%, Si 3 ∼ 69.7%, S 0.5 ∼ 67.2%, Cl 0.5 ∼ 67.2%, Ca 2 ∼ 68.7%, Ti 0.1 ∼ 66.8%, Mn 0.05 ∼ 66.75%, Fe 0.05 ∼ 66.75% 및 In 0.1 ∼ 66.8%의 원소 구성비를 갖는 광물질 분말 10 ∼ 90중량%와 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 클러스터화된 물에 투입하여 알칼리금속 및 알칼리토금속으로 구성되는 군으로부터 선택된 적어도 1종 이상의 알칼리금속 및 알칼리토금속을 용출시킨 용액에 희토류 원소를 전체 클러스터화된 물의 중량에 대하여 1중량% 미만 함유하는 물과 pH조절제를 혼합한 액상의 결합제 10 ∼ 90중량%로 구성되는 것으로 특징지워진다.The building material using the sludge according to the present invention is composed of sludge such as purified sludge, sewage sludge, wastewater sludge, sediment sludge, etc. 60 to 95% by weight and
또한, 본 발명에 따른 건자재 제조 방법은 정수슬러지, 하수슬러지, 폐수슬러지, 퇴적슬러지 등과 같은 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%로 구성되어지되 바인더는 C 5 ∼ 71.7%, O 20 ∼ 86.7%, Mg 1 ∼ 67.7%, Al 1 ∼ 67.7%, Si 3 ∼ 69.7%, S 0.5 ∼ 67.2%, Cl 0.5 ∼ 67.2%, Ca 2 ∼ 68.7%, Ti 0.1 ∼ 66.8%, Mn 0.05 ∼ 66.75%, Fe 0.05 ∼ 66.75% 및 In 0.1 ∼ 66.8%의 원소 구성비를 갖는 광물질 분말 10 ∼ 90중량%와 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 클러스터화된 물에 투입하여 알칼리금속 및 알칼리토금속으로 구성되는 군으로부터 선택된 적어도 1종 이상의 알칼리금속 및 알칼리토금속을 용출시킨 용액에 희토류 원소를 전체 클러스터화된 물의 중량에 대하여 1중량% 미만 함유하는 물과 pH조절제를 혼합한 액상의 결합제 10 ∼ 90중량%로 구성되는 바인더를 준비하는 단계; 상기 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%를 혼합하는 단계; 상기 슬러지와 바인더의 혼합물을 성형틀에 투입하는 단계; 상기 성형틀에 진동을 가한 후, 슬러지와과 바인더의 혼합물을 2차 투입한 다음 프레스 성형하는 단계; 탈형 후 자연양생하여 고화시키는 단계로 구성되는 것으로 특징지워진다.In addition, the method for manufacturing dry materials according to the present invention comprises 60 to 95% by weight of sludge such as purified sludge, sewage sludge, wastewater sludge, sediment sludge and 5 to 40% by weight of binder, but the binder is
본 발명에서 사용되는 슬러지는 정수슬러지, 하수슬러지, 폐수슬러지, 퇴적슬러지로 구성되는 군으로부터 선택된 적어도 1종 이상을 사용할 수 있다. 슬러지는 반건조 또는 건조된 것을 사용하는 것이 효과적이며, 압축되어 고형화된 것 보다는 분말상으로 건조된 것이 바람직하고, 분쇄하여 사용하는 것이 효과적이다.The sludge used in the present invention may use at least one selected from the group consisting of purified sludge, sewage sludge, wastewater sludge and sediment sludge. It is effective to use a semi-dried or dried sludge, it is preferable to be dried in powder form rather than compressed and solidified, it is effective to use the crushed.
또한, 슬러지는 적어도 함수율이 20% 미만인 것을 사용하는 것이 제조되는 건자재의 건조시 효과적일 뿐만 아니라 건조 후 변형율을 감소시킬 수 있기 때문에 바람직하고, 분쇄하여 사용할 경우 슬러지의 입자는 50 ∼ 325메쉬(mesh)의 입도를 갖는 것을 사용하는 것이 효과적이며, 입도가 50메쉬 미만일 경우에는 제조되는 건자재의 강도가 만족스럽지 못한 문제점이 있고, 325메쉬를 초과할 경우에는 제조 원가가 상승되어 경제적이지 못하다. In addition, it is preferable that the sludge having at least a water content of less than 20% is not only effective in drying the manufactured materials to be manufactured, but also can reduce the strain after drying, and when used, the sludge particles are 50 to 325 mesh (mesh It is effective to use the one having a particle size of), and if the particle size is less than 50 mesh, there is a problem that the strength of the construction material to be manufactured is not satisfactory, and if it exceeds 325 mesh, the manufacturing cost is increased and it is not economical.
바인더에서 광물질 분말은 C 5 ∼ 71.7%, O 20 ∼ 86.7%, Mg 1 ∼ 67.7%, Al 1 ∼ 67.7%, Si 3 ∼ 69.7%, S 0.5 ∼ 67.2%, Cl 0.5 ∼ 67.2%, Ca 2 ∼ 68.7%, Ti 0.1 ∼ 66.8%, Mn 0.05 ∼ 66.75%, Fe 0.05 ∼ 66.75% 및 In 0.1 ∼ 66.8%의 원소 구성비를 갖는 것을 사용한다.The mineral powder in the binder is C 5-71.7%, O 20-86.7%, Mg 1-67.7%, Al 1-67.7%, Si 3-69.7%, S 0.5-67.2%, Cl 0.5-67.2%, Ca 2- 68.7%, 0.1 to 66.8% of Ti, 0.05 to 66.75% of Mn, 0.05 to 66.75% of Fe, and one having an element composition ratio of In 0.1 to 66.8% are used.
상기 광물질 분말에는 인체에 해를 끼치지 중금속이 함유되지 않는 것을 사 용하는 것이 바람직하며, 상기 성분 이외에 미량의 원소들이 함유될 수도 있고, 상기 성분들 중에서 일부가 함유되지 않거나 다른 성분들로 치환된 광물질도 사용 가능하다. 또한, 광물질 분말의 원소 구성비는 특별히 제한되는 것은 아니지만, C, O, Mg, Al, Si, S, Cl 및 Ca는 반드시 함유되어야 하며, 각각의 원소들의 기능이 명확하게 규명되지는 않았지만 상기의 원소들 각각이 함유되지 않았을 경우에는 본 발명에 의한 효과를 얻을 수 없다.It is preferable to use a mineral powder that does not contain heavy metals to harm the human body, and may contain trace elements in addition to the above components, some of which are not included or substituted with other components. Minerals can also be used. In addition, the elemental composition ratio of the mineral powder is not particularly limited, but C, O, Mg, Al, Si, S, Cl, and Ca must be included, and although the function of each element is not clearly identified, the above elements When each of these is not contained, the effect by this invention cannot be acquired.
상기 광물질 분말은 200 ∼ 325메쉬(mesh)의 입도를 갖는 것을 사용하는 것이 효과적이며, 입도가 200메쉬 미만일 경우에는 제조되는 건자재의 강도가 만족스럽지 못한 문제점이 있고, 325메쉬를 초과할 경우에는 제조 원가가 상승되어 경제적이지 못하다.The mineral powder is effective to use those having a particle size of 200 ~ 325 mesh (mesh), when the particle size is less than 200 mesh, there is a problem that the strength of the construction material to be manufactured is not satisfactory, if the excess exceeds 325 mesh It is not economic because of rising costs.
한편, 알칼리금속염화물 및 알칼리토금속염화물로는 Li ,Na, K, Rb, Cs, Si, Al, Fe, Ca, Na, K, Mg의 염화물을 의미하는 것으로 1종 이상이 사용되어야 하고, 클러스터화된 물에 의해서 미네랄 입자가 콜로이드 용액을 형성하고, 형성된 콜로이드 용액은 광물질 분말의 미네랄과 결합하여 바인더로서의 기능을 나타내게 된다.Meanwhile, alkali metal chlorides and alkaline earth metal chlorides refer to chlorides of Li, Na, K, Rb, Cs, Si, Al, Fe, Ca, Na, K, and Mg, and at least one of them should be used and clustered. The mineral particles form a colloidal solution by the purified water, and the formed colloidal solution combines with the minerals of the mineral powder to exhibit a function as a binder.
보통 물은 35개 내외의 물분자가 연결되어 대단히 큰 클러스터를 이루고 있으며, 아황산가스, 탄산가스, 일산화탄소, 염소 가스등이 물에 녹아 들어가면 이것들이 물분자의 클러스터 사이에 붙어 엉키게 될 뿐만 아니라 이들 가스류가 물에 용해되어 황산, 아황산, 탄산, 염산등으로 되면서 물을 산성화시키고, 수은, 납, 카드뮴, 알루미늄을 비롯한 유독중금속류도 클러스터에 엉키게 된다. 이렇게 물을 산성화시키는 가스류나 유독금속을 포함하고 있는 클러스터가 큰 물은 인체에 유해한 효과를 나타낼 뿐만 아니라 본 발명에서는 결합력의 저하 원인이 되어 본 발명에서 얻고자 하는 효과가 발현되지 않게 된다. Normally, water is composed of about 35 water molecules, forming a very large cluster. When sulfur dioxide, carbon dioxide, carbon monoxide, and chlorine gas are dissolved in water, they are not only entangled between clusters of water molecules but also entangled. As it is dissolved in water, sulfuric acid, sulfurous acid, carbonic acid, and hydrochloric acid are acidified, and toxic heavy metals such as mercury, lead, cadmium, and aluminum are entangled in clusters. Such a large water cluster containing gas streams or toxic metals to acidify the water not only has a harmful effect on the human body, but also causes a decrease in the binding force in the present invention, thereby preventing the effect to be obtained in the present invention.
따라서, 본 발명에서는 4 ∼ 14㎛대의 원적외선방사, 자화처리, 초음파처리 등을 통하여 물분자의 클러스터를 5 ∼ 6개의 분자로 세분화하여 물분자의 클러스터 사이에 엉키어있던 유독가스를 공중으로 날려보내고 중금속류는 침전시켜 상등액만을 취한 클러스터화된 물을 사용한다.Therefore, in the present invention, the clusters of water molecules are subdivided into 5-6 molecules through far-infrared radiation, magnetization, ultrasonication, etc. in the range of 4-14 μm to blow toxic gases entangled between the clusters of water molecules into the air. Heavy metals are precipitated using clustered water with supernatant only.
클러스터화된 물은 공지된 다양한 방법으로 제조 가능하고, 공지된 안정화 방법으로 안정화시킨 것을 사용하는 것이 바람직하며, 클러스터화되지 않은 물을 본 발명에서 사용할 경우에는 바인더의 결합력이 저하되는 문제점이 있다.The clustered water can be prepared by a variety of known methods, it is preferable to use a stabilized by a known stabilization method, there is a problem that the binding force of the binder is lowered when using the non-clustered water in the present invention.
클러스터화된 물에 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 투입하여 용해한다. 이 때 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물의 사용량은 클러스터화된 물의 중량에 대하여 1 ∼ 60중량%의 양을 사용하는 것이 효과적이며, 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물이 1중량% 미만으로 사용될 경우에는 광물질 분말로부터 유래되는 미네랄 성분과의 결합력이 저하되는 단점이 있고, 60중량%를 초과할 경우에는 첨가 상승 효과가 미약하다.At least one compound selected from the group consisting of alkali metal chlorides and alkaline earth metal chlorides is added to the clustered water for dissolution. At this time, the amount of the at least one compound selected from the group consisting of alkali metal chlorides and alkaline earth metal chlorides is effective to use the amount of 1 to 60% by weight based on the weight of the clustered water, alkali metal chloride and alkaline earth metal When at least one or more compounds selected from the group consisting of chlorides are used in less than 1% by weight, there is a disadvantage in that the binding strength with mineral components derived from the mineral powder is lowered. Weak
클러스터화된 물에 알칼리금속 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 용해시킨 용액에 희토류 원소를 전체 클러스터화된 물의 중량에 대하여 1중량% 미만 함유하는 물과 pH조절제를 혼합한 액상의 결합제를 제조한다.In a solution in which at least one or more compounds selected from the group consisting of alkali metals and alkaline earth metal chlorides are dissolved in clustered water, water containing a rare earth element with respect to the weight of the entire clustered water and a pH adjusting agent are mixed. Prepare a liquid binder.
희토류 원소로는 란탄늄, 세륨, 프라세오디뮴, 네오디뮴, 프로메튬, 사마륨, 유로피움, 가돌리늄, 테르비움, 디스프로슘, 홀미움, 에르비움, 투리움, 이트븀, 루테늄, 스칸듐, 이트륨 등이 사용 가능하며, 게르마늄도 사용 가능하다. 희토류 원소를 소량 함유하는 물은 알칼리금속 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물의 보조제로서의 기능을 수행함과 동시에 살균 및 정균 작용에 의하여 미네랄과 콜로이드 용액의 결합이 용이하게 이루어지도록 하는 기능을 한다. 희토류 원소의 함유량은 전체 클러스터화된 물의 중량에 대하여 1중량% 미만으로 사용하는 것이 효과적이며, 희토류 원소를 함유하는 물에서도 물은 클러스터화된 물을 사용한다.Rare earth elements include lanthanum, cerium, praseodymium, neodymium, promethium, samarium, europium, gadolinium, terbium, dysprosium, holmium, erbium, turlium, yttbium, ruthenium, scandium, yttrium, etc. Also available. Water containing a small amount of rare earth elements functions as an adjuvant of at least one or more compounds selected from the group consisting of alkali metals and alkaline earth metal chlorides, and at the same time facilitates the combination of minerals and colloidal solutions by sterilization and bacteriostatic action. Function. The content of the rare earth element is effective to use less than 1% by weight based on the total weight of the clustered water, and even in the water containing the rare earth element, water is used as the clustered water.
한편, 제조되는 액상의 결합제에 pH 조절제를 사용하여 제조되는 제품의 pH가 약알칼리성이 되도록 하며, pH 조절제의 사용량은 요구되는 pH에 따라 적절히 조절될 수 있다.On the other hand, by using a pH adjuster in the liquid binder to be prepared to make the pH of the product produced is slightly alkaline, the amount of the pH adjuster can be appropriately adjusted according to the required pH.
상기와 같이 제조되는 액상의 결합제와 광물질 분말은 각각 10 ∼ 90중량%의 양으로 혼합되어 바인더가 제조된다. 액상의 결합제가 10중량% 미만이거나 광물질 분말이 90중량%를 초과할 경우에는 경화 시간이 오래 소요되는 단점이 있으며, 액상의 결합제가 90중량%를 초과하거나 광물질 분말이 10중량% 미만일 경우에는 건자재로의 성형이 용이하지 못한 문제점이 있다.The liquid binder and the mineral powder prepared as described above are mixed in amounts of 10 to 90% by weight, respectively, to prepare a binder. If the liquid binder is less than 10% by weight or the mineral powder is more than 90% by weight, there is a disadvantage that the curing time is long, and if the liquid binder is more than 90% by weight or the mineral powder is less than 10% by weight of building materials There is a problem that the molding of the furnace is not easy.
액상의 결합제와 광물질 분말이 혼합되면 급격하게 응축 및 경화가 발생하게 되므로 사용하기 직전에 혼합하는 것이 바람직하다.When the liquid binder and the mineral powder are mixed, the condensation and hardening occur rapidly, so it is preferable to mix immediately before use.
본 발명에 따른 건자재의 제조방법은 정수슬러지, 하수슬러지, 폐수슬러지, 퇴적슬러지 등과 같은 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%로 구성되어지되 바인더는 C 5 ∼ 71.7%, O 20 ∼ 86.7%, Mg 1 ∼ 67.7%, Al 1 ∼ 67.7%, Si 3 ∼ 69.7%, S 0.5 ∼ 67.2%, Cl 0.5 ∼ 67.2%, Ca 2 ∼ 68.7%, Ti 0.1 ∼ 66.8%, Mn 0.05 ∼ 66.75%, Fe 0.05 ∼ 66.75% 및 In 0.1 ∼ 66.8%의 원소 구성비를 갖는 광물질 분말 10 ∼ 90중량%와 알칼리금속염화물 및 알칼리토금속염화물로 구성되는 군으로부터 선택된 적어도 1종 이상의 화합물을 클러스터화된 물에 투입하여 알칼리금속 및 알칼리토금속으로 구성되는 군으로부터 선택된 적어도 1종 이상의 알칼리금속 및 알칼리토금속을 용출시킨 용액에 희토류 원소를 전체 클러스터화된 물의 중량에 대하여 1중량% 미만 함유하는 물과 pH조절제를 혼합한 액상의 결합제 10 ∼ 90중량%로 구성되는 바인더를 준비하는 단계; 상기 슬러지 60 ∼ 95중량%와 바인더 5 ∼ 40중량%를 혼합하는 단계; 상기 슬러지와 바인더의 혼합물을 성형틀에 투입하는 단계; 상기 성형틀에 진동을 가한 후, 슬러지와과 바인더의 혼합물을 2차 투입한 다음 프레스 성형하는 단계; 탈형 후 자연양생하여 고화시키는 단계로 구성된다.The manufacturing method of the construction material according to the present invention is composed of 60 to 95% by weight of sludge such as purified sludge, sewage sludge, wastewater sludge, sediment sludge and 5 to 40% by weight of the binder, but the binder is
본 발명의 건자재 제조 방법에 있어서 슬러지와 바인더의 혼합은 건식, 반건식, 습식으로 상기 설명한 조성 비율에 따라서 배합할 수 있으며, 슬러지의 함수율에 따라 조성 비율을 조절할 수 있다. In the dry material manufacturing method of the present invention, the mixture of the sludge and the binder can be blended according to the above-described composition ratio dry, semi-dry, and wet, and the composition ratio can be adjusted according to the water content of the sludge.
상기 슬러지와 바인더의 혼합물을 성형틀에 투입하는 단계; 상기 성형틀에 진동을 가한 후, 슬러지와 바인더의 혼합물을 2차 투입한 다음 프레스 성형하는 단계는 건자재를 균일하게 성형할 수 있는 방법이라면, 특별히 한정되지 않고, 본 발명이 속하는 기술 분야에서 통상적으로 사용되는 방법을 선택하여 적용할 수 있다. Injecting a mixture of the sludge and the binder into a mold; After the vibration is applied to the mold, the second step of adding a mixture of the sludge and the binder and then press molding is not particularly limited as long as it is a method capable of uniformly forming the building material, it is usually in the technical field to which the present invention belongs The method used can be selected and applied.
건자재로의 성형이 완료되면 탈형하고 자연 양생을 행한다. 바람직하게는 25 ∼ 80℃의 온도에서 양생하는 것이 효과적이지만, 실온에서 양생하되 온도에 따라 양생 기간을 조절할 수 있다.When molding to a building material is completed, it demolds and performs natural curing. Preferably curing at a temperature of 25 to 80 ℃, but curing at room temperature, the curing period can be adjusted according to the temperature.
본 발명에 의한 건자재로서의 성형에 대한 작용 기전은 명확히 밝혀지지는 않았지만 슬러지의 무기질 및 광물질 분말의 무기물이 클러스터화된 물과 함께 강하게 결합되어 높은 강도를 나타낼 뿐만 아니라 건자재 제조시 사용되는 공지의 결합제의 사용없이 무기질만으로 건자재의 제조가 가능해진다..Although the mechanism of action for molding as a building material according to the present invention is not clear, the inorganic material of the sludge and the inorganic material of the mineral powder are strongly bound together with the clustered water to show a high strength, and also known binders used in the manufacture of building materials. It is possible to manufacture building materials using only minerals without using.
즉, 무기질 및 슬러지의 무기물이 클로스터화된 물에 용탈(dissolusion) → 아쿠아졸 형성(formation of aquasols) → 응축(condensation) → 겔 형성(gel formation) → 결정화(crystallization)하는 반응으로 강한 결합력이 발휘되어 건자재에서 요구되는 강도 이상의 강도를 얻을 수 있으며, 유기 결합제의 사용으로 인한 문제점 및 합성수지재의 문제점을 해결할 수 있고, 무기물로만 이루어진 바인더를 사용함으로써 오염물의 배출이 없어 환경 오염을 유발하지 않고, 자연양생을 행함으로써 경제적일 뿐만 아니라 간단한 방법으로 슬러지를 제조할 수 있다.In other words, strong binding force is exerted by the reaction of dissolving → aquasol formation → condensation → gel formation → crystallization of mineral and sludge It is possible to obtain the strength more than the strength required in the building materials, solve the problems caused by the use of organic binders and synthetic resin materials, and by using a binder made only of inorganic materials, there is no discharge of pollutants, causing natural pollution, The sludge can be manufactured not only economically but also by a simple method.
특히, 슬러지에 함유된 중금속 등과 같은 환경 오염물질이 바인더와 강하게 결합되어 있고, 물에 용해되지 않아 2차적으로 슬러지로부터 오염물의 배출이 없어 친환경적으로 슬러지를 재활용할 수 있는 효과를 얻게 된다. In particular, environmental contaminants such as heavy metals contained in the sludge are strongly bound to the binder, and do not dissolve in water, so there is no discharge of contaminants from the sludge.
도 1은 본 발명에 따른 건자재의 성형 매카니즘을 설명하는 모식도이다.1 is a schematic diagram illustrating a molding mechanism of a building material according to the present invention.
Claims (3)
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR20090007310A KR101068008B1 (en) | 2009-01-30 | 2009-01-30 | Construction material using sludge and its manufacturing method |
PCT/KR2010/000556 WO2010087647A2 (en) | 2009-01-30 | 2010-01-29 | Construction product material using sludge, and method for producing same |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR20090007310A KR101068008B1 (en) | 2009-01-30 | 2009-01-30 | Construction material using sludge and its manufacturing method |
Publications (2)
Publication Number | Publication Date |
---|---|
KR20100088237A KR20100088237A (en) | 2010-08-09 |
KR101068008B1 true KR101068008B1 (en) | 2011-09-26 |
Family
ID=42396204
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR20090007310A KR101068008B1 (en) | 2009-01-30 | 2009-01-30 | Construction material using sludge and its manufacturing method |
Country Status (2)
Country | Link |
---|---|
KR (1) | KR101068008B1 (en) |
WO (1) | WO2010087647A2 (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108298854B (en) * | 2018-03-12 | 2023-06-09 | 美丽国土(北京)生态环境工程技术研究院有限公司 | Sludge solidification/stabilization curing agent and preparation method and application thereof |
CN109133548A (en) * | 2018-09-04 | 2019-01-04 | 张家港江苏科技大学产业技术研究院 | A kind of miberal powder preparation method using river domestic sludge |
CN114436622B (en) * | 2022-03-23 | 2022-08-19 | 湖南省交通科学研究院有限公司 | Subgrade filling material based on manganese tailing slag and preparation method and application thereof |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100226101B1 (en) | 1997-06-17 | 1999-10-15 | 안순철 | Construction Interior Material Using Paper Sludge and Manufacturing Method Thereof |
KR100340121B1 (en) | 2000-11-06 | 2002-06-10 | 김태현 | Cray brick, cray meterial brick footpath-roadway and manufacturing method of the same |
KR20020084975A (en) * | 2001-05-03 | 2002-11-16 | 소형석 | production of incinerated construction materials using wastewater sludge |
KR20060007720A (en) * | 2004-07-21 | 2006-01-26 | 조대연 | Composition of building materials using purified water sludge and its manufacturing method |
Family Cites Families (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
NL1016892C2 (en) * | 2000-12-15 | 2002-06-19 | Mega Tech Holding Bv | Composition intended as an additive for cement. |
ATE381519T1 (en) * | 2004-02-05 | 2008-01-15 | Optos Optimale Oszillationstec | METHOD FOR PRODUCING A BUILDING MATERIAL |
-
2009
- 2009-01-30 KR KR20090007310A patent/KR101068008B1/en not_active IP Right Cessation
-
2010
- 2010-01-29 WO PCT/KR2010/000556 patent/WO2010087647A2/en active Application Filing
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100226101B1 (en) | 1997-06-17 | 1999-10-15 | 안순철 | Construction Interior Material Using Paper Sludge and Manufacturing Method Thereof |
KR100340121B1 (en) | 2000-11-06 | 2002-06-10 | 김태현 | Cray brick, cray meterial brick footpath-roadway and manufacturing method of the same |
KR20020084975A (en) * | 2001-05-03 | 2002-11-16 | 소형석 | production of incinerated construction materials using wastewater sludge |
KR20060007720A (en) * | 2004-07-21 | 2006-01-26 | 조대연 | Composition of building materials using purified water sludge and its manufacturing method |
Also Published As
Publication number | Publication date |
---|---|
WO2010087647A3 (en) | 2010-11-25 |
KR20100088237A (en) | 2010-08-09 |
WO2010087647A2 (en) | 2010-08-05 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
KR100860017B1 (en) | Soil aggregate composition for civil engineering and building materials using process sludge and sludge and its manufacturing method | |
KR101112719B1 (en) | The solidification block composition and its manufacturing method that using the sludge and inorganic waste resources | |
CN100522854C (en) | Solidifying agent for solidifying and stabilizing treatment of generated dewatered sludge in sewage plant | |
KR100919620B1 (en) | The artificial soil composition and its manufacturing method that using the industrial by-product for recovering an abandoned quarry mining | |
KR101002547B1 (en) | Eco-friendly clay brick recycled dredged sand and sludge and its manufacturing method | |
KR100812828B1 (en) | Solidifying agent (parafix) to solidify sewage and wastewater sludge and cover material manufactured using the same | |
EP1697272A1 (en) | Porous particulate material for fluid treatment, cementitious composition and method of manufacture thereof | |
KR100796722B1 (en) | Sewage Sludge Solidification Method | |
KR101334533B1 (en) | sludge solidification removal composite and using the covering landfill production method | |
KR101495599B1 (en) | The manufacturing method of block using industrial byproducts | |
KR100771490B1 (en) | Manufacturing method of solidification agent for organic or inorganic waste resources | |
US20170369376A1 (en) | Process for complete conversion of multiple industrial wastes to sustainable alternatives and usable products | |
KR101235251B1 (en) | Cement using waterworks sludge and mathod for manufacturing the same | |
KR101010011B1 (en) | High function sludge hardener and preparation method thereof | |
KR101068008B1 (en) | Construction material using sludge and its manufacturing method | |
KR101400483B1 (en) | Echo-functional compositions of blocks | |
Dahhou et al. | Reusing drinking water sludge: physicochemical features, environmental impact and applications in building materials: a mini review | |
KR100690692B1 (en) | Process for producing solidifying agent using fluoric acid wastewater | |
KR20160135506A (en) | Method of water treatment using a constant sludge | |
JP2006247645A (en) | Modification treatment agent, modification treatment method of heat history silicate and binding shape body modified it | |
KR100948658B1 (en) | Method for solidifying sewage sludge | |
KR101279960B1 (en) | the mortar with soil and by-product and the input underwater therewith and the block for shore protection therewith | |
KR100966784B1 (en) | Manufacturing method solidfication agent for oganic or inorganic waste resouce of useing retreat mathod | |
CN111661993A (en) | Sludge curing agent and preparation method and use method thereof | |
JP2005041750A (en) | Industrial waste regenerated aggregate and method of producing the same |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
PA0109 | Patent application |
Patent event code: PA01091R01D Comment text: Patent Application Patent event date: 20090130 |
|
PA0201 | Request for examination | ||
PG1501 | Laying open of application | ||
E902 | Notification of reason for refusal | ||
PE0902 | Notice of grounds for rejection |
Comment text: Notification of reason for refusal Patent event date: 20110207 Patent event code: PE09021S01D |
|
E701 | Decision to grant or registration of patent right | ||
PE0701 | Decision of registration |
Patent event code: PE07011S01D Comment text: Decision to Grant Registration Patent event date: 20110804 |
|
GRNT | Written decision to grant | ||
PR0701 | Registration of establishment |
Comment text: Registration of Establishment Patent event date: 20110920 Patent event code: PR07011E01D |
|
PR1002 | Payment of registration fee |
Payment date: 20110920 End annual number: 3 Start annual number: 1 |
|
PG1601 | Publication of registration | ||
LAPS | Lapse due to unpaid annual fee |