JPH10272496A - Sulfiding treatment of heavy metal-containing bottom mud - Google Patents

Sulfiding treatment of heavy metal-containing bottom mud

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Publication number
JPH10272496A
JPH10272496A JP7972997A JP7972997A JPH10272496A JP H10272496 A JPH10272496 A JP H10272496A JP 7972997 A JP7972997 A JP 7972997A JP 7972997 A JP7972997 A JP 7972997A JP H10272496 A JPH10272496 A JP H10272496A
Authority
JP
Japan
Prior art keywords
bottom mud
layer
layers
sand
gravel
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
Application number
JP7972997A
Other languages
Japanese (ja)
Other versions
JP3673054B2 (en
Inventor
Hiroshi Yamauchi
寛 山内
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hazama Corp
Original Assignee
Hazama Gumi Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hazama Gumi Ltd filed Critical Hazama Gumi Ltd
Priority to JP07972997A priority Critical patent/JP3673054B2/en
Publication of JPH10272496A publication Critical patent/JPH10272496A/en
Application granted granted Critical
Publication of JP3673054B2 publication Critical patent/JP3673054B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a sulfiding treatment method for heavy metal-contg. bottom mud capable of subjecting the bottom mud contg. harmful heavy metals, such as lead, cadmium, mercury, copper, zinc and hexad chromium, to sulfiding and insolubilizing treatments. SOLUTION: Fillings 10 are prepd. by laminating bottom mud layers 11, 11' contg. the hazardous heavy metals, sand layers 12, 12' and gravel layers 13. The respective sand layers 12, 12' are supplied and impregnated with prescribed chemical solns. from perforated pipes 14. The chemical solns. are forced to flow down and penetrate in the form of perpendicularly downward penetration flow into the lower bottom mud layers 11, 11', by which the harmful heavy metals are sulfided and insolubilized. The leaching water from the gravel layers 13 is released by impervious sheets 17 and channels 2. Rain guard sheets 18 are put on the fillings 10. The front surfaces of the respective bottom mud layers 11, 11' are provided with pack drains 16 where the chemical solns. easily penetrate to accelerate the infiltration of the chemical solns. into the respective bottom mud layers 11, 11'.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明が属する技術分野】本発明は重金属含有底泥の硫
化処理方法に関し、更に詳細には、鉛、カドミニウム、
水銀、銅、亜鉛、六価クロム等の有害な重金属を含有す
る主として河川・湖沼の底泥等を、当該重金属を硫化物
の形態で不溶化して浄化処理する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for sulfidizing heavy metal-containing bottom mud, and more particularly, to lead, cadmium,
The present invention relates to a method for purifying sediment of rivers and lakes mainly containing harmful heavy metals such as mercury, copper, zinc and hexavalent chromium by insolubilizing the heavy metals in the form of sulfides.

【0002】[0002]

【従来の技術】有害な重金属を含有する底泥の硫化処理
としては、従来から、底泥に対して硫化ナトリウムを含
む薬液を添加たし後、バックホー等の重機によって混合
して有害重金属を硫化・不溶化する方法が一般的に採用
されている。
2. Description of the Related Art Conventionally, as a sulfidation treatment of sediment containing harmful heavy metals, a chemical solution containing sodium sulfide is added to the sediment and mixed with a heavy machine such as a backhoe to sulfurize the harmful heavy metals. -The method of insolubilization is generally adopted.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、重機に
よる混合では、薬液と有害重金属とを均一且つ十分に反
応させることが困難であり、処理後の泥土に未反応の有
害重金属あるいは余剰の硫化ナトリウムが残り、例えば
処理土の再利用の妨げとなる等の問題があった。
However, it is difficult to make the chemical solution and the harmful heavy metal react uniformly and sufficiently by mixing with a heavy machine, and unreacted harmful heavy metal or excess sodium sulfide is added to the treated mud. There still remains a problem that, for example, it hinders the reuse of treated soil.

【0004】本発明の目的は、有害な重金属を含有する
底泥を確実に硫化(不溶化)処理することができる重金
属含有底泥の硫化処理方法を提供することにある。
[0004] It is an object of the present invention to provide a method of sulfurizing heavy metal-containing sediment, which can surely sulfurate (insolubilize) sediment containing harmful heavy metals.

【0005】[0005]

【課題を解決するための手段】本発明に係る重金属含有
底泥の硫化処理方法は、所定の薬液によって硫化・不溶
化する重金属を含有する底泥からなる底泥層と、砂又は
砂礫土からなる砂層又は砂礫層とを少なくとも最上層が
砂層又は砂礫層となるように積層し、前記薬液を互いに
隣接する、上方の砂層又は砂礫層に供給・浸透させて下
方の底泥層に流下・浸透させ、最下層からの浸出水を放
流することを特徴とする。
According to the present invention, there is provided a method of sulfurizing heavy metal-containing bottom mud according to the present invention, comprising a bottom mud layer comprising heavy metal containing bottom metal which is sulfurized and insolubilized by a predetermined chemical solution, and sand or gravel soil. A sand layer or a gravel layer is laminated so that at least the uppermost layer becomes a sand layer or a gravel layer, and the chemicals are supplied to and penetrate into the adjacent sand layer or the gravel layer adjacent to each other to flow down and permeate into the lower bottom mud layer. And characterized by discharging leachate from the bottom layer.

【0006】即ち、本方法では、所定の薬液を底泥層に
比べて透水係数の高い砂層又は砂礫層に供給・浸透させ
ることにより、薬液を鉛直下向きの浸透流として下方の
底泥層に対して流下・浸透させ、これを底泥層の一部を
適宜サンプリングして、有害重金属が完全に硫化・不溶
化するまで中長期的に繰り返すものであり、最下層から
の浸出水は適宜浄化して放流する。なお、底泥は粘土等
も含み、積層前にが含水比50〜100%程度まで脱水
される。
That is, in the present method, a predetermined chemical solution is supplied and permeated into a sand layer or a gravel layer having a higher water permeability than the bottom mud layer, so that the chemical solution is formed into a vertically downward permeation flow to the lower bottom mud layer. This is to repeat sampling over a medium to long term until the harmful heavy metals are completely sulfurized and insolubilized, and the leachate from the bottom layer is appropriately purified. Release. The bottom mud also contains clay and the like, and is dehydrated before lamination to a water content of about 50 to 100%.

【0007】底泥層と砂層及び/又は砂礫層との積層は
盛土状とすることが望ましく、最下層を砂礫層、最上層
及び中間層を砂層とすることが望ましい。
The lamination of the bottom mud layer and the sand layer and / or the gravel layer is preferably embankment-like, and the lowermost layer is preferably a gravel layer, and the uppermost layer and the intermediate layer are preferably sand layers.

【0008】所定の薬液としては、鉛、カドミニウム、
水銀、銅、亜鉛、六価クロム等の有害重金属を硫化物の
形態で不溶化する、硫化水素、硫化水素ナトリウム、メ
ルカプトエタノール、メルカプトプロピオン酸、トリメ
ルカプトトリアジン等の還元性硫黄化合物の水溶液を用
い、薬液のpH調整のため溶解性炭酸カルシウムを付加
する。
[0008] As the predetermined chemical, lead, cadmium,
Using an aqueous solution of reducing sulfur compounds such as hydrogen sulfide, sodium hydrogen sulfide, mercaptoethanol, mercaptopropionic acid and trimercaptotriazine to insolubilize harmful heavy metals such as mercury, copper, zinc and hexavalent chromium in the form of sulfides, Soluble calcium carbonate is added to adjust the pH of the drug solution.

【0009】本発明では、前記底泥層及び砂層及び/又
は砂礫層に対する雨水の浸入を防止する手段を設けるこ
とができ、かような手段の具体例としては遮水シート等
を挙げることができる。即ち、雨水は薬液を薄めたり、
最下層からの浸出水の処理を面倒とするため、遮水シー
ト等によって雨避けとするものである。なお、遮水シー
トは一般的に気体に対する不透過性をも有するため、空
気中の酸素の底泥層等への浸透による薬液の酸化をも防
止する。
In the present invention, means for preventing the infiltration of rainwater into the bottom mud layer, the sand layer and / or the gravel layer can be provided, and specific examples of such means include a water-blocking sheet. . That is, rainwater dilutes chemicals,
In order to complicate the treatment of leachate from the bottom layer, a rain barrier sheet is used to avoid rain. In addition, since the impermeable sheet generally has gas impermeability, it also prevents oxidation of the chemical solution due to permeation of oxygen in the air into the bottom mud layer or the like.

【0010】本発明では、前記底泥層に対する前記薬液
の浸透を補助する手段を設けることができ、かような手
段の具体例として、透水性を有する合成繊維等からなる
袋に砂を充填してなるパックドレイン(砂充填袋)等を
挙げることができる。即ち、薬液は底泥層に流下・浸透
することなく底泥層の上面から側方に流出するおそれが
るため、薬液が容易に浸透するパックドレインを底泥層
の上面から適宜埋設し、薬液をパックドレインを介して
底泥層へ浸透させるものである。
In the present invention, means for assisting the penetration of the chemical solution into the bottom mud layer can be provided. As a specific example of such means, a bag made of synthetic fibers having water permeability is filled with sand. Pack drain (sand-filled bag). That is, since the chemical liquid may flow out from the upper surface of the bottom mud layer without flowing down and permeating the bottom mud layer, the pack drain into which the chemical liquid easily penetrates may be appropriately buried from the upper surface of the bottom mud layer. Through the packed drain into the bottom mud layer.

【0011】[0011]

【実施例】以下、本発明の実施例を添付図面に基づいて
説明する。
Embodiments of the present invention will be described below with reference to the accompanying drawings.

【0012】図1は、有害重金属を含有し、含水率を概
ね70%以下となるように脱水した底泥からなる底泥層
11,11’と、砂からなる砂層12,12’と、砂礫
土からなる砂礫層13とを地盤1上に盛土状に積層した
もの(以下「盛土」という。)10を断面にて示す説明
図である。盛土10の最上層及び最下層には砂層12及
び砂礫層13が、中間層には一例として二層の底泥層1
1,11’がそれぞれ設けられる。なお、各層11,1
1’,12,12’,13の厚高を30〜100cmと
し、盛土10の全高を1.5〜2mとした。
FIG. 1 shows bottom mud layers 11 and 11 ′ made of bottom mud containing harmful heavy metals and dehydrated so as to have a water content of about 70% or less, sand layers 12 and 12 ′ made of sand, and sand and gravel. FIG. 2 is an explanatory diagram showing a cross section of an embankment layer 10 formed by laminating a gravel layer 13 made of soil on the ground 1 (hereinafter referred to as “embankment”). A sand layer 12 and a gravel layer 13 are formed on the uppermost and lowermost layers of the embankment 10, and a two-layered bottom mud layer 1 is formed on the intermediate layer as an example.
1, 11 'are provided respectively. In addition, each layer 11, 1
The thickness of 1 ', 12, 12', and 13 was set to 30 to 100 cm, and the total height of the embankment 10 was set to 1.5 to 2 m.

【0013】各砂層12,12’の上面又は内部上方に
は、薬液供給源である薬液調整タンク15に連通し、薬
液を砂層12,12’全域に供給するための有孔管14
が配設される。薬液調整タンク15は、薬液中の還元性
硫黄剤の空気中の酸素による酸化を防止するため、窒素
ガスによって曝気される。また、各底泥層11,11’
の上面から内部には、薬液浸透補助手段として、透水性
を有する合成繊維等からなる袋に砂を充填してなるパッ
クドレイン16が適宜な間隔毎に埋設される。
A perforated pipe 14 communicating with a chemical solution adjusting tank 15 serving as a chemical solution supply source for supplying a chemical solution to the entire area of the sand layers 12 and 12 'is provided on the upper surface or inside of each of the sand layers 12 and 12'.
Is arranged. The chemical liquid adjustment tank 15 is aerated with nitrogen gas in order to prevent oxidation of the reducing sulfur agent in the chemical liquid by oxygen in the air. In addition, each bottom mud layer 11, 11 '
Pack drains 16 formed by filling a bag made of synthetic fibers having water permeability with sand are buried at appropriate intervals from the upper surface to the inside as a chemical liquid permeation assisting means.

【0014】地盤1の盛土10周囲には浸出水を放流す
るための溝2が設けられ、砂礫層13及び溝2の各底部
には遮水シート17が敷設される。また、盛土10の上
面及び各法面には雨水浸入防止手段として簡易な遮水シ
ート18が被せられる。遮水シート18は空気中酸素の
盛土10内への浸透をも防止して、盛土10内における
薬液の酸化を防止する。
A groove 2 for discharging leachate is provided around the embankment 10 of the ground 1, and a water-blocking sheet 17 is laid at each bottom of the gravel layer 13 and the groove 2. Further, a simple water-impervious sheet 18 is put on the upper surface and each slope of the embankment 10 as rainwater intrusion prevention means. The water-blocking sheet 18 also prevents oxygen in the air from penetrating into the embankment 10 and prevents oxidation of the chemical solution in the embankment 10.

【0015】盛土10に対しては、薬液調整タンク15
から各有孔管14を介して各砂層12,12’に薬液を
供給する。各砂層12,12’は浸透する薬液によって
飽和される一方、薬液は鉛直下向きの浸透流となって各
底泥層11,11’に流下・浸透する。この際、薬液の
一部は底泥層11,11’の上面から直接浸透し、薬液
の他の部分はパックドレイン15に浸透して飽和した
後、底泥層11,11’へ浸透する。砂礫層13からの
浸出水は、遮水シート17上から溝2に流出した後、放
流されるが、浸出水に低濃度の有害重金属が含まれる場
合、放流前に浄化処理を行う。
For the embankment 10, a chemical solution adjusting tank 15
Supplies a chemical solution to each of the sand layers 12, 12 'through each perforated pipe 14. Each of the sand layers 12, 12 'is saturated with the penetrating chemical solution, while the chemical solution flows down and permeates into the bottom mud layers 11, 11' as a vertically downward penetrating flow. At this time, a part of the chemical liquid directly permeates from the upper surfaces of the bottom mud layers 11 and 11 ′, and another part of the chemical liquid penetrates into the pack drain 15 and is saturated, and then permeates into the bottom mud layers 11 and 11 ′. The leachate from the gravel layer 13 is discharged after flowing into the groove 2 from above the impermeable sheet 17, but when the leachate contains a low concentration of harmful heavy metals, a purification treatment is performed before the release.

【0016】以上の薬液供給を底泥層11,11’の一
部をサンプリンしながら、有害重金属が完全に硫化・不
溶化するまで例えば一週間等の適宜間隔毎に繰り返すこ
とにより、大量の底泥を確実に浄化処理することができ
る。
The above-mentioned chemical solution supply is repeated at appropriate intervals, for example, for one week, until the harmful heavy metal is completely sulfurized and insolubilized while sampling a part of the bottom mud layers 11, 11 'while sampling. Can be reliably purified.

【0017】[0017]

【発明の効果】以上述べたように、本発明に係る重金属
含有底泥の硫化処理方法では、所定の薬液を底泥層に比
べて透水係数の高い砂層又は砂礫層に供給・浸透させる
ことにより、薬液を鉛直下向きの浸透流として下方の底
泥層に対して流下・浸透させることができ、これを適宜
繰り返すことにより、大量の底泥を確実に一括硫化・不
溶化処理することができる。
As described above, in the method for sulfurating heavy metal-containing bottom mud according to the present invention, a predetermined chemical solution is supplied and permeated to a sand layer or a gravel layer having a higher water permeability than the bottom mud layer. In addition, the chemical solution can flow down and permeate into the lower bottom mud layer as a vertically downward permeation flow, and by repeating this as appropriate, a large amount of bottom mud can be surely subjected to collective sulfurization and insolubilization treatment.

【図面の簡単な説明】[Brief description of the drawings]

【図1】底泥層と砂層と砂礫層とを積層してなる盛土を
断面にて示す説明図である。
FIG. 1 is an explanatory diagram showing a cross section of an embankment formed by laminating a bottom mud layer, a sand layer, and a gravel layer.

【符号の説明】[Explanation of symbols]

1 地盤 2 溝 10 盛土 11,11’ 底泥層 12,12’ 砂層 13 砂礫層 14 有効管 15 薬液調整タンク 16 パックドレイン 17,18 遮水シート DESCRIPTION OF SYMBOLS 1 Ground 2 Groove 10 Embankment 11, 11 'Bottom mud layer 12, 12' Sand layer 13 Gravel layer 14 Effective pipe 15 Chemical liquid adjustment tank 16 Pack drain 17, 18 Waterproof sheet

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 所定の薬液によって硫化・不溶化する重
金属を含有する底泥からなる底泥層と、砂又は砂礫土か
らなる砂層又は砂礫層とを少なくとも最上層が砂層又は
砂礫層となるように積層し、前記薬液を互いに隣接す
る、上方の砂層又は砂礫層に供給・浸透させて下方の底
泥層に流下・浸透させ、最下層からの浸出水を放流する
ことを特徴とする重金属含有底泥の硫下処理方法。
1. A bottom mud layer made of a bottom mud containing a heavy metal which is sulfurized and insolubilized by a predetermined chemical solution, and a sand layer or a gravel layer made of sand or gravel so that at least the uppermost layer becomes a sand layer or a gravel layer. A heavy metal-containing bottom, characterized in that the chemical liquids are stacked and supplied and permeated into an upper sand layer or a gravel layer adjacent to each other, and allowed to flow down and permeate into a lower bottom mud layer, thereby discharging leachate from the lowest layer. Sulfur treatment method for mud.
【請求項2】 前記底泥層及び砂層及び/又は砂礫層に
対する雨水の浸入を防止する手段を設ける請求項1に記
載の重金属含有底泥の硫下処理方法。
2. The method according to claim 1, further comprising a step of preventing rainwater from entering the bottom mud layer, the sand layer and / or the gravel layer.
【請求項3】 前記底泥層に対する前記薬液の浸透を補
助する手段を設ける請求項1又は請求項2に記載の重金
属含有底泥の硫化処理方法。
3. The method for sulfurating heavy metal-containing bottom mud according to claim 1, further comprising means for assisting penetration of the chemical solution into the bottom mud layer.
JP07972997A 1997-03-31 1997-03-31 Sulfurization treatment method for heavy metal-containing bottom mud Expired - Fee Related JP3673054B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP07972997A JP3673054B2 (en) 1997-03-31 1997-03-31 Sulfurization treatment method for heavy metal-containing bottom mud

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP07972997A JP3673054B2 (en) 1997-03-31 1997-03-31 Sulfurization treatment method for heavy metal-containing bottom mud

Publications (2)

Publication Number Publication Date
JPH10272496A true JPH10272496A (en) 1998-10-13
JP3673054B2 JP3673054B2 (en) 2005-07-20

Family

ID=13698303

Family Applications (1)

Application Number Title Priority Date Filing Date
JP07972997A Expired - Fee Related JP3673054B2 (en) 1997-03-31 1997-03-31 Sulfurization treatment method for heavy metal-containing bottom mud

Country Status (1)

Country Link
JP (1) JP3673054B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100464910C (en) * 2007-05-24 2009-03-04 上海交通大学 Pyrolytic treatment method for chromium slag
CN102617011A (en) * 2012-04-17 2012-08-01 重庆大学 Infiltration chamber system for infiltrating, drying and digesting sludge
CN106391692A (en) * 2016-09-20 2017-02-15 北京高能时代环境技术股份有限公司 Remediation method for chromium slag or chromium contaminated soil
CN112301943A (en) * 2019-11-28 2021-02-02 海南发控智慧环境建设集团有限公司 Ecological island reef with bottom mud restoration function

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100464910C (en) * 2007-05-24 2009-03-04 上海交通大学 Pyrolytic treatment method for chromium slag
CN102617011A (en) * 2012-04-17 2012-08-01 重庆大学 Infiltration chamber system for infiltrating, drying and digesting sludge
CN106391692A (en) * 2016-09-20 2017-02-15 北京高能时代环境技术股份有限公司 Remediation method for chromium slag or chromium contaminated soil
CN112301943A (en) * 2019-11-28 2021-02-02 海南发控智慧环境建设集团有限公司 Ecological island reef with bottom mud restoration function

Also Published As

Publication number Publication date
JP3673054B2 (en) 2005-07-20

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