JP2000326000A - Dehydrating treatment of muddy water - Google Patents
Dehydrating treatment of muddy waterInfo
- Publication number
- JP2000326000A JP2000326000A JP11143250A JP14325099A JP2000326000A JP 2000326000 A JP2000326000 A JP 2000326000A JP 11143250 A JP11143250 A JP 11143250A JP 14325099 A JP14325099 A JP 14325099A JP 2000326000 A JP2000326000 A JP 2000326000A
- Authority
- JP
- Japan
- Prior art keywords
- muddy water
- water
- paddle
- dehydrating agent
- reaction tank
- 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.)
- Granted
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 49
- 238000011282 treatment Methods 0.000 title description 7
- 239000012024 dehydrating agents Substances 0.000 claims abstract description 22
- 238000003756 stirring Methods 0.000 claims abstract description 15
- 150000003839 salts Chemical class 0.000 claims abstract description 13
- 238000006243 chemical reaction Methods 0.000 claims abstract description 12
- 230000005484 gravity Effects 0.000 claims abstract description 8
- 229920006318 anionic polymer Polymers 0.000 claims description 15
- 229920006317 cationic polymer Polymers 0.000 claims description 15
- 238000000034 method Methods 0.000 claims description 13
- 230000015271 coagulation Effects 0.000 claims description 10
- 238000005345 coagulation Methods 0.000 claims description 10
- 238000002156 mixing Methods 0.000 claims description 6
- 125000002091 cationic group Chemical group 0.000 abstract description 4
- 125000000129 anionic group Chemical group 0.000 abstract description 3
- 238000009435 building construction Methods 0.000 abstract description 2
- 230000016615 flocculation Effects 0.000 abstract 2
- 238000005189 flocculation Methods 0.000 abstract 2
- 235000002639 sodium chloride Nutrition 0.000 description 13
- HRPVXLWXLXDGHG-UHFFFAOYSA-N Acrylamide Chemical compound NC(=O)C=C HRPVXLWXLXDGHG-UHFFFAOYSA-N 0.000 description 8
- 239000000701 coagulant Substances 0.000 description 7
- 239000000463 material Substances 0.000 description 6
- 239000003795 chemical substances by application Substances 0.000 description 5
- 229920001577 copolymer Polymers 0.000 description 5
- NIXOWILDQLNWCW-UHFFFAOYSA-M Acrylate Chemical compound [O-]C(=O)C=C NIXOWILDQLNWCW-UHFFFAOYSA-M 0.000 description 4
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 4
- 208000005156 Dehydration Diseases 0.000 description 4
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 4
- 229940048053 acrylate Drugs 0.000 description 4
- 230000002776 aggregation Effects 0.000 description 4
- 238000004220 aggregation Methods 0.000 description 4
- 150000001450 anions Chemical class 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 4
- 239000000084 colloidal system Substances 0.000 description 4
- 238000010276 construction Methods 0.000 description 4
- 230000018044 dehydration Effects 0.000 description 4
- 238000006297 dehydration reaction Methods 0.000 description 4
- PQUXFUBNSYCQAL-UHFFFAOYSA-N 1-(2,3-difluorophenyl)ethanone Chemical compound CC(=O)C1=CC=CC(F)=C1F PQUXFUBNSYCQAL-UHFFFAOYSA-N 0.000 description 3
- 229920006322 acrylamide copolymer Polymers 0.000 description 3
- 238000011161 development Methods 0.000 description 3
- 238000007865 diluting Methods 0.000 description 3
- -1 dimethylaminoethyl Chemical group 0.000 description 3
- 239000008394 flocculating agent Substances 0.000 description 3
- 229920000642 polymer Polymers 0.000 description 3
- 229940047670 sodium acrylate Drugs 0.000 description 3
- 239000002689 soil Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 229920001897 terpolymer Polymers 0.000 description 3
- IRLPACMLTUPBCL-KQYNXXCUSA-N 5'-adenylyl sulfate Chemical compound C1=NC=2C(N)=NC=NC=2N1[C@@H]1O[C@H](COP(O)(=O)OS(O)(=O)=O)[C@@H](O)[C@H]1O IRLPACMLTUPBCL-KQYNXXCUSA-N 0.000 description 2
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 2
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 2
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 2
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 2
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 description 2
- 235000019270 ammonium chloride Nutrition 0.000 description 2
- 238000009412 basement excavation Methods 0.000 description 2
- 239000001110 calcium chloride Substances 0.000 description 2
- 229910001628 calcium chloride Inorganic materials 0.000 description 2
- 235000011148 calcium chloride Nutrition 0.000 description 2
- NEHMKBQYUWJMIP-UHFFFAOYSA-N chloromethane Chemical group ClC NEHMKBQYUWJMIP-UHFFFAOYSA-N 0.000 description 2
- 150000001875 compounds Chemical group 0.000 description 2
- 229920001519 homopolymer Polymers 0.000 description 2
- 229920000620 organic polymer Polymers 0.000 description 2
- 229920002401 polyacrylamide Polymers 0.000 description 2
- FGIUAXJPYTZDNR-UHFFFAOYSA-N potassium nitrate Chemical compound [K+].[O-][N+]([O-])=O FGIUAXJPYTZDNR-UHFFFAOYSA-N 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 239000011780 sodium chloride Substances 0.000 description 2
- VWDWKYIASSYTQR-UHFFFAOYSA-N sodium nitrate Chemical compound [Na+].[O-][N+]([O-])=O VWDWKYIASSYTQR-UHFFFAOYSA-N 0.000 description 2
- IXPNQXFRVYWDDI-UHFFFAOYSA-N 1-methyl-2,4-dioxo-1,3-diazinane-5-carboximidamide Chemical compound CN1CC(C(N)=N)C(=O)NC1=O IXPNQXFRVYWDDI-UHFFFAOYSA-N 0.000 description 1
- PAWQVTBBRAZDMG-UHFFFAOYSA-N 2-(3-bromo-2-fluorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=CC(Br)=C1F PAWQVTBBRAZDMG-UHFFFAOYSA-N 0.000 description 1
- QTBSBXVTEAMEQO-UHFFFAOYSA-M Acetate Chemical compound CC([O-])=O QTBSBXVTEAMEQO-UHFFFAOYSA-M 0.000 description 1
- 102100032566 Carbonic anhydrase-related protein 10 Human genes 0.000 description 1
- 229920001661 Chitosan Polymers 0.000 description 1
- 101000867836 Homo sapiens Carbonic anhydrase-related protein 10 Proteins 0.000 description 1
- 102100031083 Uteroglobin Human genes 0.000 description 1
- 108090000203 Uteroglobin Proteins 0.000 description 1
- 230000004931 aggregating effect Effects 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- YIOJGTBNHQAVBO-UHFFFAOYSA-N dimethyl-bis(prop-2-enyl)azanium Chemical compound C=CC[N+](C)(C)CC=C YIOJGTBNHQAVBO-UHFFFAOYSA-N 0.000 description 1
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 1
- VWPOBUVSGMLNCM-UHFFFAOYSA-L disodium prop-2-enoate Chemical compound [Na+].C(C=C)(=O)[O-].[Na+].C(C=C)(=O)[O-] VWPOBUVSGMLNCM-UHFFFAOYSA-L 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 238000005553 drilling Methods 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 238000007429 general method Methods 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 229910001629 magnesium chloride Inorganic materials 0.000 description 1
- 235000011147 magnesium chloride Nutrition 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 235000019341 magnesium sulphate Nutrition 0.000 description 1
- FQPSGWSUVKBHSU-UHFFFAOYSA-N methacrylamide Chemical compound CC(=C)C(N)=O FQPSGWSUVKBHSU-UHFFFAOYSA-N 0.000 description 1
- 229940050176 methyl chloride Drugs 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 229920001495 poly(sodium acrylate) polymer Polymers 0.000 description 1
- 239000001103 potassium chloride Substances 0.000 description 1
- 235000011164 potassium chloride Nutrition 0.000 description 1
- 239000004323 potassium nitrate Substances 0.000 description 1
- 235000010333 potassium nitrate Nutrition 0.000 description 1
- FJWSMXKFXFFEPV-UHFFFAOYSA-N prop-2-enamide;hydrochloride Chemical compound Cl.NC(=O)C=C FJWSMXKFXFFEPV-UHFFFAOYSA-N 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 235000010413 sodium alginate Nutrition 0.000 description 1
- 239000000661 sodium alginate Substances 0.000 description 1
- 229940005550 sodium alginate Drugs 0.000 description 1
- 239000004317 sodium nitrate Substances 0.000 description 1
- 235000010344 sodium nitrate Nutrition 0.000 description 1
- NNMHYFLPFNGQFZ-UHFFFAOYSA-M sodium polyacrylate Chemical compound [Na+].[O-]C(=O)C=C NNMHYFLPFNGQFZ-UHFFFAOYSA-M 0.000 description 1
- SONHXMAHPHADTF-UHFFFAOYSA-M sodium;2-methylprop-2-enoate Chemical compound [Na+].CC(=C)C([O-])=O SONHXMAHPHADTF-UHFFFAOYSA-M 0.000 description 1
- SKMHHHHLLBKNKR-UHFFFAOYSA-M sodium;prop-2-enamide;prop-2-enoate Chemical compound [Na+].NC(=O)C=C.[O-]C(=O)C=C SKMHHHHLLBKNKR-UHFFFAOYSA-M 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 230000003313 weakening effect Effects 0.000 description 1
Landscapes
- Treatment Of Sludge (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、土木、建設の工事
の際において排出される泥水や各種産業排水の処理によ
って生ずる泥水のうち、高濃度、高粘度の泥水を効率的
に脱水処理するための泥水の脱水処理法に関するもので
ある。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for efficiently dewatering high-concentration, high-viscosity mud among mud discharged during civil engineering and construction works and mud generated by various industrial wastewater treatments. And a method for dehydrating muddy water.
【0002】[0002]
【従来の技術】トンネルの掘削、ボーリング、杭打ちな
どの土木工事や建設工事においては様々な性状の泥水が
排出されるため、泥水の発生源である現場において、短
時間に脱水減量して搬出可能な性状に変え、作業環境の
維持と搬出コストの削減が行われている。2. Description of the Related Art Since muddy water of various properties is discharged in civil engineering work and construction work such as tunnel excavation, boring, and pile driving, dewatering is reduced and carried out at a site where muddy water is generated in a short time. The work environment has been maintained and the cost of unloading has been reduced to the extent possible.
【0003】このような泥水の一般的な処理法は、泥水
に凝集剤を添加して適当な大きさのフロックに凝集させ
たのち、これを脱水して固液分離し、得られたケーキ
(汚泥固形分)と分離水は、泥水の種類や量により要す
れば爾後処理を行って最終的に一定強度の脱水ケーキと
し、これを埋め戻し用や路床材料、堤防および宅地造成
用などの土として、あるいは肥料として利用し、分離水
は河川その他に放流するようにしている。[0003] In such a general method of treating mud, a flocculant is added to the mud to aggregate into flocs of an appropriate size, which are then dewatered and separated into solids and liquids. (Sludge solids) and separated water are subjected to post-treatment if necessary depending on the type and amount of muddy water, and finally to a dehydrated cake with a certain strength, which is used for backfilling, subgrade materials, embankments and residential land development, etc. Used as soil or fertilizer, the separated water is discharged to rivers and other places.
【0004】この泥水の脱水に使用する凝集剤(以下、
単に「脱水剤」という)としては、たとえば、カチオン
性高分子凝集剤の単独使用、カチオン性高分子凝集剤と
アニオン性高分子凝集剤の併用など各種の脱水剤が挙げ
られ、また、その使用方法としても種々の方法が提案さ
れている。[0004] The coagulant used for dehydrating this mud (hereinafter, referred to as
Examples of the “dehydrating agent” include various types of dehydrating agents such as a single use of a cationic polymer flocculant and a combination of a cationic polymer flocculant and an anionic polymer flocculant. Various methods have been proposed as methods.
【0005】[0005]
【発明が解決しようとする課題】これらの高分子凝集剤
による脱水処理は、一般に、凝集力が充分でないため、
爾後の脱水処理に際して充分な脱水ができず、経済的で
はないという問題があると共に、建築工事現場などから
排出される泥水のうち、水分の少ない高濃度、高粘度の
泥水は、セメントなどの固化剤で処理して固めるか、泥
水に水を吸収させて希釈化したのち、アニオン性高分子
で凝集処理をしている。The dehydration treatment using these high-molecular coagulants generally has insufficient cohesive force.
In the subsequent dewatering process, sufficient dewatering is not possible, which is not economical, and high-concentration, high-viscosity mud with low water content among mud discharged from building construction sites, etc. After treatment with an agent and hardening, or after absorbing water in muddy water and diluting it, it is subjected to coagulation treatment with an anionic polymer.
【0006】しかしながら、固化剤による処理手段は、
泥水を固めるために固化剤を大量に使用する必要からコ
ストが嵩むという欠点を有し、希釈化手段は、泥水を希
釈するための水を必要とするため、水の供給が不便な場
所では適用が難しく、希釈のための施設を新たに必要と
すると共に、凝集力を弱めるため、減容率が小さく、経
済的でないなど解決すべき多くの課題を有している。[0006] However, the means for treating with a solidifying agent is as follows:
It has the drawback that the cost increases because it is necessary to use a large amount of a solidifying agent to solidify the muddy water, and the diluting means requires water for diluting the muddy water, so it is applicable in a place where water supply is inconvenient. However, there are many problems to be solved, such as requiring a new facility for dilution and weakening the cohesive force, resulting in a small volume reduction rate and not being economical.
【0007】本発明はかゝる現状に鑑み鋭意研究の結
果、カチオン性有機高分子凝集剤、アニオン性有機高分
子凝集剤及び水溶性塩からなる脱水剤を、高濃度、高粘
度の泥水に添加し、これを2軸の攪拌機によって攪拌混
合することによって迅速かつ高効率に混合、凝集できる
ことを見出したことにより完成されたものである。The present invention has been made in view of the above situation and as a result of intensive research, it has been found that a cationic organic polymer flocculant, an anionic organic polymer flocculant and a dehydrating agent comprising a water-soluble salt can be converted into high-concentration, high-viscosity muddy water. It has been completed by the fact that it has been found that mixing and aggregation can be performed quickly and efficiently by stirring and mixing with a twin-screw stirrer.
【0008】[0008]
【課題を解決するための手段】すなわち、本発明の泥水
の脱水処理法は、外周に多数の攪拌送り羽根を有する左
右一対のパドル軸をその羽根を互いに噛み合わせながら
相反方向に回転するよう設けたパドル型凝集反応槽に、
比重1.2以上の泥水を供給すると共に、カチオン性高
分子凝集剤、アニオン性高分子凝集剤および水溶性塩か
らなる脱水剤を添加し、パドル軸によって泥水と脱水剤
との攪拌混合を行い、フロックを形成させ脱水すること
を特徴とするものである。That is, the muddy water dewatering method of the present invention comprises a pair of left and right paddle shafts having a large number of stirring and feeding blades on the outer periphery thereof, which are rotated in opposite directions while engaging the blades with each other. Paddle-type coagulation reaction tank,
While supplying muddy water having a specific gravity of 1.2 or more, a dehydrating agent composed of a cationic polymer flocculant, an anionic polymer flocculant and a water-soluble salt is added, and the muddy water and the dehydrating agent are stirred and mixed by a paddle shaft. And dewatering by forming flocs.
【0009】[0009]
【発明の実施の形態】土木工事や建設工事において排出
される泥水、すなわち、土とセメント系懸濁液を混合し
て地中に壁体を作る地中連続壁工事で排出される泥水や
トンネル掘削工事において打設した推進管を通じて排出
される掘削泥水は、濃度や粘度が非常に高く、また、そ
の比重は概ね1.2〜1.7で、従来の方法では脱水が
非常に困難なものである。BEST MODE FOR CARRYING OUT THE INVENTION Muddy water discharged in civil engineering work or construction work, that is, muddy water or tunnel discharged in underground continuous wall construction in which soil and a cement suspension are mixed to form a wall in the ground Drilling mud discharged through a propulsion pipe installed during excavation work has a very high concentration and viscosity, and its specific gravity is generally 1.2 to 1.7, making dehydration extremely difficult with conventional methods. It is.
【0010】本発明において、上記脱水が非常に困難な
比重1.2以上の泥水の脱水処理に用いる脱水剤は、カ
チオン性高分子凝集剤、アニオン性高分子凝集剤および
水溶性塩、特に5重量%の水溶液のpHが4.5〜9.
0の水溶性塩からなるものである。In the present invention, the dehydrating agent used for dehydrating the mud having a specific gravity of 1.2 or more, which is extremely difficult to dehydrate, is a cationic polymer flocculant, an anionic polymer flocculant and a water-soluble salt, particularly 5 The pH of the aqueous solution of 4.5% by weight is 4.5 to 9.
0 is a water-soluble salt.
【0011】本発明に用いられるカチオン性高分子凝集
剤としては、具体的には、ジメチルアミノエチル(メ
タ)アクリレート、ジメチルアミノプロピル(メタ)ア
クリレート又はそれらの4級化物もしくは3級化物の単
独重合体およびこれらとアクリルアミド又はメタクリル
アミドとの共重合体、ポリアクリルアミドもしくはポリ
メタクリルアミドのマンニッヒ変性物又はその4級化
物、ポリアクリルアミドもしくはポリメタクリルアミド
のホフマン分解物、ジアリルジメチルアンモニウム塩の
単独重合体もしくはキトサンの酢酸塩など公知のものを
挙げることができる。Specific examples of the cationic polymer flocculant used in the present invention include dimethylaminoethyl (meth) acrylate, dimethylaminopropyl (meth) acrylate, and a quaternary or tertiary compound thereof. Copolymers and copolymers of these with acrylamide or methacrylamide, Mannich-modified polyacrylamide or polymethacrylamide or quaternized products thereof, Hoffman decomposition products of polyacrylamide or polymethacrylamide, homopolymers of diallyldimethylammonium or Known ones such as chitosan acetate can be mentioned.
【0012】これらのうち、特に、ジメチルアミノエチ
ル(メタ)アクリレートのメチルクロライド4級化物の
単独重合体もしくは該4級化物の80モル%以上を含む
アクリルアミド共重合体などのカチオン性の高分子凝集
剤が好適で、コロイド当量値として3.0〜5.2me
q/gの範囲のものが好ましく使用される。Among these, in particular, cationic polymer aggregation such as a homopolymer of quaternary methyl chloride of dimethylaminoethyl (meth) acrylate or an acrylamide copolymer containing at least 80 mol% of the quaternary compound. Agents are preferred and have a colloid equivalent value of 3.0 to 5.2 me.
Those having a range of q / g are preferably used.
【0013】アニオン性高分子凝集剤としては、具体的
には、ポリアクリル酸ナトリウム、(メタ)アクリルア
ミドと(メタ)アクリル酸ナトリウムとの共重合体、ポ
リ(メタ)アクリルアミドの部分加水分解物、アクリル
アミドと2−アクリルアミド−2−メチルプロパンスル
ホン酸ナトリウム(以下、AMPSという)との共重合
体、アクリルアミドとアクリル酸ナトリウム及びメタク
リル酸ナトリウムとの三元共重合体、(メタ)アクリル
アミドと(メタ)アクリル酸ナトリリウム及び前記AM
PSとの三元共重合体及びアルギン酸ナトリウムなどが
挙げられる。Specific examples of the anionic polymer coagulant include sodium polyacrylate, a copolymer of (meth) acrylamide and sodium (meth) acrylate, a partial hydrolyzate of poly (meth) acrylamide, Copolymer of acrylamide and sodium 2-acrylamide-2-methylpropanesulfonate (hereinafter referred to as AMPS), terpolymer of acrylamide with sodium acrylate and sodium methacrylate, (meth) acrylamide and (meth) Sodium sodium acrylate and said AM
And a terpolymer with PS and sodium alginate.
【0014】これらのうち、弱アニオン〜強アニオンの
アニオン性高分子凝集剤が好適で、コロイド当量値とし
ては−0.7〜−5.5meq/gの範囲のものが好ま
しい。中でも、コロイド当量値として−0.7〜−3.
0meq/gの弱アニオン〜中アニオンのアニオン性高
分子凝集剤に該当するアクリルアミドとアクリル酸ナト
リウムとの共重合体、アクリルアミドとアクリル酸ナト
リリウム及び前記AMPSとの三元共重合体がよい。Of these, anionic polymeric flocculants having a weak anion to a strong anion are preferred, and those having a colloid equivalent value in the range of -0.7 to -5.5 meq / g are preferred. Among them, -0.7 to -3.
A copolymer of acrylamide and sodium acrylate, a terpolymer of acrylamide and sodium acrylate, and the above-mentioned AMPS, which is an anionic polymer flocculant having a weak anion to a medium anion of 0 meq / g, is preferable.
【0015】これらカチオン性高分子凝集剤及びアニオ
ン性高分子凝集剤と共に使用される水溶性塩としては、
5重量%水溶液のpHが4.5〜9.0であるものが好
ましく、具体的には、硫酸アンモニウム、塩化アンモニ
ウム、硝酸アンモニウム、硫酸マグネシウム、塩化マグ
ネシウム、塩化カルシウム、塩化ナトリウム、塩化カリ
ウム、硝酸ナトリウム、硝酸カリウムなどであり、これ
らのうちの塩化カルシウム、塩化アンモニウムが特に好
適である。The water-soluble salt used together with the cationic polymer flocculant and the anionic polymer flocculant includes:
It is preferable that the pH of the 5% by weight aqueous solution be 4.5 to 9.0, specifically, ammonium sulfate, ammonium chloride, ammonium nitrate, magnesium sulfate, magnesium chloride, calcium chloride, sodium chloride, potassium chloride, sodium nitrate, Potassium nitrate and the like, of which calcium chloride and ammonium chloride are particularly preferred.
【0016】この脱水剤におけるカチオン性高分子凝集
剤とアニオン性高分子凝集剤の好ましい配合比率として
は、カチオン性高分子凝集剤が20〜95重量%で、ア
ニオン性高分子凝集剤が80〜5重量%、より好ましく
はカチオン性高分子凝集剤が30〜90重量%、アニオ
ン性高分子凝集剤が70〜10重量%の範囲である。The preferred proportions of the cationic polymer flocculant and the anionic polymer flocculant in the dehydrating agent are 20 to 95% by weight of the cationic polymer flocculant and 80 to 95% by weight of the anionic polymer flocculant. 5% by weight, more preferably 30 to 90% by weight of the cationic polymer coagulant, and 70 to 10% by weight of the anionic polymer coagulant.
【0017】前記カチオン性とアニオン性の高分子凝集
剤に対する前記水溶性塩の好ましい配合量は、両者の高
分子凝集剤の合計量に対して1倍量(重量)以上、より
好ましくは5〜10倍量以上であり、1倍量未満では泥
水の粘性の低下が現れず、脱水性が悪化するおそれがあ
る。The preferred amount of the water-soluble salt to be added to the cationic and anionic polymer flocculants is at least 1 time (by weight), more preferably 5 to 5 times the total amount of both polymer flocculants. If the amount is 10 times or more, and if it is less than 1 time, the viscosity of the muddy water does not decrease, and the dewatering property may be deteriorated.
【0018】この脱水剤の泥水への添加は、対象となる
泥水の性状によって異なるが、泥水の固形分に対する各
高分子凝集剤のポリマーの量として、1〜5重量%程度
が使用される。The addition of the dehydrating agent to the mud depends on the properties of the mud to be treated, but about 1 to 5% by weight of the polymer of each polymer flocculant with respect to the solid content of the mud is used.
【0019】泥水と脱水剤との混合は、図1に示すよう
な泥水を受け入れる装置本体2と、該装置本体2の上部
開口部を閉止する蓋体9とからなるバドル型凝集反応槽
1において実施されるものである。装置本体2には長手
方向に沿って、多数の攪拌送り羽根3,3・・・・を外
周に突設した一対のパドル軸4a,4bを、前記羽根3
を互いに噛み合わせながら相反方向に回転するように配
置すると共に、いずれか一方のパドル軸4aに可変速モ
ータ5を連結し、他のバドル軸4bはギア6によってパ
ドル軸4aと同期して回転するよう構成してある。The mixing of the muddy water and the dehydrating agent is performed in a paddle-type coagulation reaction tank 1 comprising a main body 2 for receiving muddy water and a lid 9 for closing an upper opening of the main body 2 as shown in FIG. It is implemented. The device body 2 is provided with a pair of paddle shafts 4a, 4b having a large number of stirring and feeding blades 3, 3,.
Are arranged so as to rotate in opposite directions while meshing with each other, the variable speed motor 5 is connected to one of the paddle shafts 4a, and the other paddle shaft 4b is rotated by the gear 6 in synchronization with the paddle shaft 4a. It is configured as follows.
【0020】他方の蓋体10には、前記装置本体2内に
泥水を供給するための供給管10および脱水剤を供給添
加するための供給管11とが接続されており、供給管1
0を通じて装置本体2内に供給された泥水は、多数の攪
拌送り羽根3,3・・・・によって供給管11を通して
供給添加された脱水剤と攪拌混合され、一方側から他方
側に所要の速度で送られ、脱水剤によって凝集固化して
形成されたフロック状泥土と分離された汚水は、共にオ
ーバーフロー部8を通じてべルトプレスなどの公知の脱
水機(図示せず)によって脱水して含水率の低下したケ
ーキ状のものとするものである。The other lid 10 is connected to a supply pipe 10 for supplying muddy water into the apparatus main body 2 and a supply pipe 11 for supplying and adding a dehydrating agent.
., Muddy water supplied into the apparatus main body 2 through the supply pipe 11 is stirred and mixed with the dehydrating agent supplied through the supply pipe 11 by a number of stirring feed blades 3, 3,. The flocculated mud formed by coagulation and solidification by the dehydrating agent and the separated sewage are both dewatered by a known dehydrator (not shown) such as a belt press through the overflow section 8 to reduce the water content. It should be a cake-like thing.
【0021】この構造のパドル型凝集反応槽1は、多数
の攪拌送り羽根3,3・・・・を外周に突設した一対の
パドル軸4a,4bを低速回転させることによって高濃
度、高粘度の泥水と脱水剤との攪拌を効率よく行い、同
時に泥分の凝集を生じさせてフロック化し、泥水を高能
率で凝集させることができるものである。なお、7は排
泥管である。The paddle-type coagulation reaction tank 1 of this structure has a high concentration and a high viscosity by rotating a pair of paddle shafts 4a and 4b having a large number of stirring and feeding blades 3, 3. The muddy water and the dehydrating agent can be efficiently agitated, and at the same time, the muddy water can be coagulated to form flocs, so that the muddy water can be coagulated with high efficiency. In addition, 7 is a drainage pipe.
【0022】[0022]
【作用】本発明の泥水の脱水処理法は、カチオン性高分
子凝集剤と、アニオン性高分子凝集剤および水溶性塩、
特に、5重量%の水溶液のpHが4.5〜9.0である
水溶性塩からなる脱水剤を用いて比重1.2以上の高濃
度、高粘性の泥水を凝集固化させるに際し、多数の攪拌
送り羽根を外周に突設した一対のパドル軸を具備したパ
ドル型凝集反応槽で行うことによって、泥水と脱水剤と
の攪拌混合がきわめて効率的に行われ、脱水をすること
ができる。The method for dehydrating mud of the present invention comprises a cationic polymer flocculant, an anionic polymer flocculant and a water-soluble salt,
Particularly, when a high-concentration, high-viscosity muddy water having a specific gravity of 1.2 or more is coagulated and solidified using a dehydrating agent composed of a water-soluble salt having a pH of 4.5 to 9.0 in a 5% by weight aqueous solution, a large number of By performing the stirring and feeding in a paddle type coagulation reaction tank having a pair of paddle shafts protruding from the outer periphery, the stirring and mixing of the muddy water and the dehydrating agent can be performed very efficiently, and dewatering can be performed.
【0023】その際、使用される上記脱水剤は、水溶解
性と水分散性に優れ、カチオン性基の加水分解が生じな
いため、得られる溶解液の安定性もよく、泥土の凝集性
および生成したフロックの脱水性に優れ、機器に対する
腐食性もない。At this time, the dehydrating agent used is excellent in water solubility and water dispersibility, and does not cause hydrolysis of the cationic group. The generated floc has excellent dewatering properties and does not corrode equipment.
【0024】[0024]
【実施例】以下、本発明の高濃度、高粘性の泥水の脱水
処理法を実施例によってより具体的に説明する。 <実施例1>カチオン性高分子凝集剤として、コロイド
当量値が3.0meq/gの2−メタクリロイルオキシ
メチルトリメチルアンモニウムクロライド−アクリルア
ミド共重合体90g、アニオン性高分子凝集剤として、
コロイド当量値が−2.7meq/gのアクリル酸ナト
リウム−アクリルアミド共重合体10g及び水溶性塩と
して塩化ナトリウム1kgを20リットルの蒸留水に溶
解した。この溶解液を脱水剤として、推進工法によって
シルト分を主として含み砂分および粘土分をそれぞれ少
量含有する土質から生じた比重1.5の高濃度の泥水1
00リットルに添加し、図1に示すパドル型凝集反応槽
1において攪拌し凝集させた。EXAMPLES The method for dehydrating high-concentration, high-viscosity mud according to the present invention will be described in more detail with reference to examples. <Example 1> As a cationic polymer coagulant, 90 g of a 2-methacryloyloxymethyltrimethylammonium chloride-acrylamide copolymer having a colloid equivalent value of 3.0 meq / g, and as an anionic polymer coagulant,
10 g of a sodium acrylate-acrylamide copolymer having a colloid equivalent value of -2.7 meq / g and 1 kg of sodium chloride as a water-soluble salt were dissolved in 20 liters of distilled water. Using this solution as a dehydrating agent, high-concentration mud water 1 with a specific gravity of 1.5 generated from soil containing mainly silt and small amounts of sand and clay, respectively, by the propulsion method.
Then, the mixture was stirred and aggregated in a paddle-type aggregation reaction tank 1 shown in FIG.
【0025】このパドル型凝集反応槽1から取り出した
凝集物をベルトプレス脱水機にかけて脱水したところ、
含水率31%の脱水ケーキを得ることができた。得られ
た脱水ケーキは、埋め戻し材料や路床材料、堤防および
宅地造成用などの資材として充分に使用可能なものであ
り、濾過による水は河川その他に放流してもなんら問題
が生じない程度の澄んだものであった。The aggregate removed from the paddle-type aggregation reaction tank 1 was dehydrated by a belt press dehydrator.
A dehydrated cake having a water content of 31% was obtained. The obtained dewatered cake can be sufficiently used as backfill material, subgrade material, embankment and building land development, etc., so that the filtered water will not cause any problem even if it is discharged to rivers and other places. It was clear.
【0026】[0026]
【発明の効果】本発明の泥水の脱水処理法は、カチオン
性高分子凝集剤と、アニオン性高分子凝集剤および水溶
性塩、特に、5重量%の水溶液のpHが4.5〜9.0
の水溶性塩からなる脱水剤を使用し、比重1.2以上の
高濃度、高粘性の泥水を外周に多数の攪拌送り羽根を有
する左右一対のパドル軸をその羽根を互いに噛み合わせ
ながら相反方向に回転するよう設けたパドル型凝集反応
槽において攪拌混合させながら泥分の凝集を図り、得ら
れた凝集泥分を脱水することによって含水率の低い脱水
ケーキを得ることを可能とするもので、前記した特定の
脱水剤と、特定構造の機器との組み合わせによってきわ
めて効率よく脱水処理して脱水ケーキとすることができ
る点において優れたものである。According to the method for dehydrating muddy water of the present invention, the pH of a cationic polymer flocculant, an anionic polymer flocculant and a water-soluble salt, particularly, a 5% by weight aqueous solution is adjusted to 4.5 to 9.5. 0
Using a dehydrating agent consisting of a water-soluble salt of high concentration and high viscosity with a specific gravity of 1.2 or more, a pair of left and right paddle shafts having a large number of stirring and feeding blades on the outer periphery are engaged in opposite directions while engaging the blades with each other. It is possible to obtain a dewatered cake having a low water content by aggregating the mud while stirring and mixing in a paddle type coagulation reaction tank provided so as to rotate, and dewatering the obtained agglomerated mud. It is excellent in that a dehydration cake can be formed by performing dehydration treatment extremely efficiently by a combination of the above-mentioned specific dehydrating agent and a device having a specific structure.
【0027】この発明の泥水の脱水処理法で脱水された
脱水ケーキは、埋め戻し材料や路床材料、堤防および宅
地造成用などの資材として充分に使用可能なものであ
り、また、脱水で生じた水は河川その他に放流してもな
んら問題が生じない程度に清浄なものである。The dewatered cake dewatered by the muddy water dewatering method of the present invention can be sufficiently used as a material for backfilling materials, roadbed materials, embankments and residential land development, etc. The water is so clean that it does not cause any problems if discharged into rivers and other places.
【図1】この発明の泥水の脱水処理法における泥水の攪
拌・凝集に使用するパドル型凝集反応槽の分解斜視図で
ある。FIG. 1 is an exploded perspective view of a paddle-type coagulation reaction tank used for stirring and coagulating mud in the mud dewatering treatment method of the present invention.
1 2パドル型凝集反応槽 2 装置本体 3 攪拌送り羽根 4a,4b パドル軸 5 モータ 6 ギア 7 排泥管 8 オーバーフロー部 9 蓋体 10,11 供給管 DESCRIPTION OF SYMBOLS 1 2 Paddle type coagulation reaction tank 2 Device main body 3 Stirring sending blade 4a, 4b Paddle shaft 5 Motor 6 Gear 7 Drainage pipe 8 Overflow part 9 Lid body 10, 11 Supply pipe
フロントページの続き Fターム(参考) 4D015 BA11 BA28 BB08 BB17 CA10 DB03 DB05 DB07 DB10 DB12 DB32 DB33 DC07 DC08 EA02 EA06 EA39 4D059 AA03 AA09 BE08 BE16 BE57 BE59 BE60 BJ03 CC10 DA01 DA07 DA09 DA35 DA46 DB18 DB24 DB25 DB26 DB28 Continued on front page F-term (reference) 4D015 BA11 BA28 BB08 BB17 CA10 DB03 DB05 DB07 DB10 DB12 DB32 DB33 DC07 DC08 EA02 EA06 EA39 4D059 AA03 AA09 BE08 BE16 BE57 BE59 BE60 BJ03 CC10 DA01 DA07 DA09 DA35 DA46 DB18 DB24 DB25 DB28
Claims (1)
一対のパドル軸をその羽根を互いに噛み合わせながら相
反方向に回転するよう設けたパドル型凝集反応槽に、比
重1.2以上の泥水を供給すると共に、カチオン性高分
子凝集剤、アニオン性高分子凝集剤および水溶性塩から
なる脱水剤を添加し、パドル軸によって泥水と脱水剤と
の攪拌混合を行い、フロックを形成させ脱水することを
特徴とする泥水の脱水処理法。1. A muddy water having a specific gravity of 1.2 or more is supplied to a paddle-type coagulation reaction tank provided with a pair of left and right paddle shafts having a large number of stirring and feeding blades on the outer periphery so as to rotate in opposite directions while meshing the blades with each other. Supplying and adding a dehydrating agent consisting of a cationic polymer flocculant, an anionic polymer flocculant and a water-soluble salt, stirring and mixing the muddy water and the dehydrating agent with a paddle shaft to form a floc and dewater. A method for dehydrating muddy water.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP14325099A JP3705012B2 (en) | 1999-05-24 | 1999-05-24 | Muddy water dehydration |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP14325099A JP3705012B2 (en) | 1999-05-24 | 1999-05-24 | Muddy water dehydration |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JP2000326000A true JP2000326000A (en) | 2000-11-28 |
| JP3705012B2 JP3705012B2 (en) | 2005-10-12 |
Family
ID=15334387
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP14325099A Expired - Lifetime JP3705012B2 (en) | 1999-05-24 | 1999-05-24 | Muddy water dehydration |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3705012B2 (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005007371A (en) * | 2003-06-23 | 2005-01-13 | Harada Sogo Doboku:Kk | Muddy water treatment apparatus |
| JP2007007535A (en) * | 2005-06-30 | 2007-01-18 | Katayama Chem Works Co Ltd | Solid-liquid separation method of muddy water |
| JP2009106847A (en) * | 2007-10-30 | 2009-05-21 | Fukoku Kogyo Kk | Coagulation reactor |
| CN110894091A (en) * | 2019-09-30 | 2020-03-20 | 上海尔速机械设备有限公司 | A flocculation device |
| KR102646352B1 (en) * | 2023-08-08 | 2024-03-11 | 주식회사 그린개발 | Apparatus and method for separating water soil material |
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|---|---|---|---|---|
| JPS62289300A (en) * | 1986-06-09 | 1987-12-16 | Toagosei Chem Ind Co Ltd | Sludge dehydrating agent |
| JPH07136613A (en) * | 1993-11-19 | 1995-05-30 | Tokyo Kankyo Service Kk | Construction soil improvement method |
| JPH08117798A (en) * | 1994-10-21 | 1996-05-14 | Ube Ind Ltd | Soil solidification treatment pumping equipment |
| JPH09125873A (en) * | 1995-10-31 | 1997-05-13 | Masahiro Inoue | Device for mud-water treatment |
| JPH09168800A (en) * | 1995-10-17 | 1997-06-30 | Terunaito:Kk | Treatment method of high water content dredging sludge |
| JPH10272306A (en) * | 1997-03-31 | 1998-10-13 | Nitto Chem Ind Co Ltd | Wastewater dewatering method |
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1999
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|---|---|---|---|---|
| JPS62289300A (en) * | 1986-06-09 | 1987-12-16 | Toagosei Chem Ind Co Ltd | Sludge dehydrating agent |
| JPH07136613A (en) * | 1993-11-19 | 1995-05-30 | Tokyo Kankyo Service Kk | Construction soil improvement method |
| JPH08117798A (en) * | 1994-10-21 | 1996-05-14 | Ube Ind Ltd | Soil solidification treatment pumping equipment |
| JPH09168800A (en) * | 1995-10-17 | 1997-06-30 | Terunaito:Kk | Treatment method of high water content dredging sludge |
| JPH09125873A (en) * | 1995-10-31 | 1997-05-13 | Masahiro Inoue | Device for mud-water treatment |
| JPH10272306A (en) * | 1997-03-31 | 1998-10-13 | Nitto Chem Ind Co Ltd | Wastewater dewatering method |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005007371A (en) * | 2003-06-23 | 2005-01-13 | Harada Sogo Doboku:Kk | Muddy water treatment apparatus |
| JP2007007535A (en) * | 2005-06-30 | 2007-01-18 | Katayama Chem Works Co Ltd | Solid-liquid separation method of muddy water |
| JP2009106847A (en) * | 2007-10-30 | 2009-05-21 | Fukoku Kogyo Kk | Coagulation reactor |
| CN110894091A (en) * | 2019-09-30 | 2020-03-20 | 上海尔速机械设备有限公司 | A flocculation device |
| KR102646352B1 (en) * | 2023-08-08 | 2024-03-11 | 주식회사 그린개발 | Apparatus and method for separating water soil material |
Also Published As
| Publication number | Publication date |
|---|---|
| JP3705012B2 (en) | 2005-10-12 |
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