JPH07215786A - Treatment of dredging sludge and cleaning method of static water system - Google Patents

Treatment of dredging sludge and cleaning method of static water system

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Publication number
JPH07215786A
JPH07215786A JP6030866A JP3086694A JPH07215786A JP H07215786 A JPH07215786 A JP H07215786A JP 6030866 A JP6030866 A JP 6030866A JP 3086694 A JP3086694 A JP 3086694A JP H07215786 A JPH07215786 A JP H07215786A
Authority
JP
Japan
Prior art keywords
sludge
algae
water
dredging
layer
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.)
Pending
Application number
JP6030866A
Other languages
Japanese (ja)
Inventor
Tomoharu Takashima
伴治 高島
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.)
ASUKA KISEN KK
Original Assignee
ASUKA KISEN KK
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 ASUKA KISEN KK filed Critical ASUKA KISEN KK
Priority to JP6030866A priority Critical patent/JPH07215786A/en
Publication of JPH07215786A publication Critical patent/JPH07215786A/en
Pending legal-status Critical Current

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Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Landscapes

  • Cleaning Or Clearing Of The Surface Of Open Water (AREA)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

PURPOSE:To provide a treatment method capable of easily composting dredging sludge and a cleaning method of ponds, etc., utilizing this method. CONSTITUTION:Sludge-contg. water sucked together with sludge is subjected to a filter treatment using dry algae as filter media, by which the sludge is adhered to the dry algae and the dry algae stuck with the sludge are utilized as compost. Working regions 3a, 3b... are set at the pond 1 by sealingly enclosing these regions with pollution diffusion preventive films 2 hung down from the water surface. Recovering of dirt and dredging of the sludge by suction are progressed within these working regions. The sucked sludge-contg. water and the polluted water in the working region generated by diffusion of the sludge are subjected to a filter treatment using the dry algae as the filter media, by which the used dry algae stuck with the sludge are utilized as the compost.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、浚渫汚泥の処理方法及
びそれを利用した静止的水系の清掃方法、特に公園の池
のように景観の維持について要求の強い静止的水系に好
適な清掃方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating dredging sludge and a method for cleaning a static water system using the same, and particularly a cleaning method suitable for a static water system which is strongly required to maintain a landscape such as a pond in a park. Regarding

【0002】[0002]

【従来の技術】河川や湖沼などの水質保全のために底に
溜まっている汚泥の浚渫を行なう場合が少なくないが、
これに伴う浚渫汚泥の処理が問題になっている。即ち、
浚渫汚泥の多くは埋め立てなどで処理されているが、埋
め立て能力の限界との関係で問題を招き、また堆肥とし
て活用する試みも一部にあるものの、面倒な二次的な加
工を必要とするため実際性に乏しいのが現実である。
2. Description of the Related Art There are many cases where the sludge accumulated at the bottom is dredged to preserve the water quality of rivers and lakes.
Due to this, the treatment of dredging sludge has become a problem. That is,
Most of the dredged sludge is treated by landfill, but it causes problems due to the limit of landfill capacity, and although some attempts to use it as compost, it requires complicated secondary processing. Therefore, the reality is that it is not practical.

【0003】また、池や湖沼のような静止的水系、特に
公園のように多くの人が集まる場所にある池にあっては
空き缶や空きビン、さらには粗大ゴミなどが投棄などに
よりその底に溜まり勝ちで、景観を損ねる基になってい
る。このため一定のサイクルで汚泥の浚渫と共にゴミを
回収する清掃作業を行なう必要がある。そして、このよ
うな清掃作業についても浚渫した汚泥の処理を如何に行
なうかが問題となり、また清掃作業に伴って汚泥が拡散
することにより池の水が全体的に汚濁するのを如何に防
止するかも問題となっている。
[0003] In addition, in static water systems such as ponds and lakes, especially in ponds where a lot of people gather, such as in parks, empty cans and bottles, and even large-sized garbage are dumped at the bottom. It is the basis for damaging the landscape by winning the pool. For this reason, it is necessary to carry out a cleaning operation for collecting sludge with dredging of sludge in a certain cycle. In such cleaning work, how to treat the dredged sludge becomes a problem, and how to prevent the water in the pond from being totally polluted due to the sludge diffusion accompanying the cleaning work. Is also a problem.

【0004】この点を従来の方法についてみると、汚泥
の処理については、従来では浚渫した汚泥に脱水処理を
施した後に上記のような処分をしていた。このため上記
と同様の問題があり、また脱水処理に伴う汚濁水の還流
により長期間にわたる汚濁状態を招くという問題もあっ
た。一方、汚濁の拡散については、作業域の汚濁水に急
速濾過機による濾過を施すようにしていたが、汚泥や浮
遊物が多いために頻繁に逆洗を行なう必要があり、この
逆洗による汚濁水の還流で再び汚濁することになり、極
めて無駄の多い作業となっていた。
Regarding this point, regarding the conventional method, regarding the sludge treatment, conventionally, the dredged sludge was dehydrated and then disposed as described above. For this reason, there is a problem similar to the above, and there is also a problem that the polluted water is refluxed due to the dehydration treatment, resulting in a polluted state for a long period of time. On the other hand, for the diffusion of pollution, the contaminated water in the working area was filtered by a rapid filter, but since there is a lot of sludge and suspended solids, it is necessary to backwash it frequently. It was polluted again by the reflux of water, which was an extremely wasteful work.

【0005】[0005]

【発明が解決しようとする課題】本発明は、以上のよう
な事情を背景になされたもので、浚渫汚泥の堆肥化を簡
単に行なえる処理方法の提供を目的とし、また上記のよ
うな池の清掃を効率的に、しかも環境に優しく行なうこ
とのできる方法の提供を目的としている。
SUMMARY OF THE INVENTION The present invention has been made in view of the above circumstances, and an object thereof is to provide a treatment method capable of easily composting dredged sludge, and also to a pond as described above. The purpose of the present invention is to provide a method that enables efficient and environmentally friendly cleaning.

【0006】[0006]

【課題を解決するための手段】本発明による浚渫汚泥の
処理方法は、汚泥とともに吸引した汚泥含有水に乾燥藻
を濾材とした濾過処理を施することにより、乾燥藻に汚
泥を付着させ、この汚泥付着の乾燥藻を堆肥として利用
するようにしてなっている。
The method for treating dredged sludge according to the present invention is to apply sludge to dry algae by subjecting sludge-containing water sucked together with sludge to filtration treatment using dry algae. Dry algae attached to sludge is used as compost.

【0007】これは乾燥藻の特性に着目しこれを有効に
活用したものである。即ち、乾燥藻は、肥料取締法に基
づく特殊肥料の一つとして挙げられているようにそれ自
体に十分な肥料適性があり、また濾過に好ましい網状構
造を与え易くて濾過適性が高い、という特性がある。そ
して、この両特性を本発明の方法のようにして有効に利
用することにより、汚泥の堆肥化処理過程の大幅な簡略
化を図れる。つまり、濾過処理により汚泥含有水の浄化
と同時に汚泥と乾燥藻の一体化を図れるし、また汚泥付
着の乾燥藻であれば簡単な熟成処理を施すだけで堆肥と
することができる。この結果、浚渫汚泥の堆肥への活用
を実際的なものとすることができる。
This is an effective utilization of the characteristics of dried algae. That is, dry algae has sufficient fertilizer suitability for itself, as mentioned as one of the special fertilizers based on the Fertilizer Control Law, and it is easy to give a preferable net structure for filtration and has high filterability. There is. By effectively utilizing both of these characteristics as in the method of the present invention, the sludge composting process can be greatly simplified. That is, the sludge and the dried algae can be integrated at the same time as the purification of the sludge-containing water by the filtration treatment, and the dried algae with the sludge can be made into a compost by simply performing the aging treatment. As a result, the utilization of dredged sludge for compost can be made practical.

【0008】このような汚泥の処理方法を活用した本発
明による池の清掃方法は、水面から底まで垂らした汚濁
拡散防止膜により封鎖的に囲んで適宜の面積の作業領域
を設定し、この作業領域内でゴミの回収及び吸引による
汚泥の浚渫を進めるようにし、且つ吸引した汚泥含有水
及び汚泥の拡散により発生する作業領域内の汚濁水に乾
燥藻を濾材とした濾過処理を施し、これにより汚泥が付
着した使用済みの乾燥藻を堆肥化して利用するようにし
てなっている。
The method for cleaning a pond according to the present invention, which utilizes such a sludge treatment method, sets a work area of an appropriate area by sealingly surrounding it with a pollution diffusion prevention film hanging from the water surface to the bottom, and performing this work. The sludge is dredged by collecting and sucking the waste in the area, and the sludge-containing water that has been sucked in and the contaminated water in the work area that is generated due to the diffusion of the sludge are subjected to a filtering process using dry algae as a filter medium. Used dry algae with sludge attached is composted and used.

【0009】この方法によると、汚濁拡散防止膜により
封鎖的に設定した作業領域内で作業を進めるようにして
いるので、清掃作業に伴う汚濁の池の広い範囲への拡散
を防止できる。
According to this method, since the work is carried out within the work area which is set to be closed by the pollution diffusion preventing film, it is possible to prevent the diffusion of the pollution due to the cleaning work to a wide range of the pond.

【0010】また、汚泥の浚渫を吸引で行い、この吸引
した汚泥含有水を乾燥藻を濾材として濾過処理すると共
に使用済みの乾燥藻を堆肥化して再利用するようにして
いるので、上記従来の汚泥の脱水処理における汚濁水の
再発生のような問題を伴うことなく確実な汚泥の処理を
行なえ、従って効率的に作業を進めることができるし、
汚泥を堆肥の一成分として有効に活用できる。
Further, since dredging of sludge is carried out by suction and the sucked sludge-containing water is subjected to a filtering treatment with dried algae as a filter material, used dry algae is composted and reused. The sludge can be treated reliably without problems such as the re-generation of polluted water in the sludge dewatering treatment, and therefore the work can be efficiently carried out.
Sludge can be effectively used as a component of compost.

【0011】さらに、作業領域内の汚濁水にも汚泥含有
水と同様な処理を施すようにしているので、清掃作業に
伴う汚濁の後処理を汚泥含有水の場合と同様に効率的に
行なうことができるし、これにより発生する汚泥も同様
に堆肥の一成分として有効に活用できる。
Further, since the polluted water in the work area is treated in the same manner as the sludge-containing water, the post-treatment of the pollution associated with the cleaning work should be performed as efficiently as the sludge-containing water. The sludge generated thereby can also be effectively utilized as a component of compost.

【0012】以上の各方法については、乾燥藻として乾
燥オオフサモを用いるのが好ましい。その理由は以下の
通りである。オオフサモは、アリノトウグサ科の多年草
で、その生活形態は通常の状態では抽水植物の形態をと
る。即ち、図4に模式化して示すように、空中葉Bを水
上に10〜20cm程度の長さで直立させる一方で、螺
旋状の主茎Kを水深に応じて数メートル以上にも水中や
水底の土中に伸ばし、この主茎の表面から多くの根rを
水底の土中に張って根付きするという生活形態をとって
いる。そして、隣り合う個体同士が互いの螺旋状主茎を
絡ませ合うことで流失などに抵抗できる群体を形成して
いる。特に、本願発明者の研究によると、その根を土中
に張れない状態にしてやることにより、自然の状態に較
べて格段に多くの根を生やして極めて優秀なフィルタ構
造を形成し、また主茎の伸長を物理的に妨害するような
条件を与えることにより、やはり主茎の螺旋状態が一層
高密になってフィルタ構造を形成する。また、オオフサ
モは上記のような構造でその表面積が大きいために乾燥
させ易い。従って、自生状態あるいはフィルタ構造を形
成し易い条件で栽培したオオフサモを適当に風乾させる
だけで、優秀な乾燥藻フィルタを簡単に得ることができ
る。しかも、オオフサモは、例えばT−Nが約13%、
T−P2 5 が約1%、T−K2 Oが約2%、T−Ca
Oが約1.7 %、T−MgOが約1%、T−Cが約292
%のように、特に窒素及び燐の含有率が大きく、肥料と
しての適性にも優れている。
[0012] In each of the above methods, it is preferable to use dried oaksamo as the dried algae. The reason is as follows. Ooafusamo is a perennial plant of the family Amaranthaceae, and its life form normally takes the form of a water-extracting plant. That is, as schematically shown in FIG. 4, the aerial leaf B is erected on the water at a length of about 10 to 20 cm, while the spiral main stem K is placed in the water or the water bottom for several meters or more depending on the water depth. It has a life form in which many roots r are stretched from the surface of the main stem into the soil at the bottom of the water and rooted. Then, adjacent individuals form a colony capable of resisting washout by entwining their spiral main stems with each other. In particular, according to the research conducted by the inventor of the present application, by making the roots in a state that cannot be submerged in the soil, much more roots are grown than in the natural state to form an extremely excellent filter structure, and the main stem By providing conditions that physically hinder the elongation of the stem, the spiral state of the main stem also becomes more dense and forms a filter structure. In addition, Oofusamo has a structure as described above and has a large surface area, so that it is easy to dry. Therefore, an excellent dried algae filter can be easily obtained only by appropriately air-drying the giant sardine that has been cultivated in a natural state or in a condition where a filter structure is easily formed. Moreover, for example, TN has about 13% TN,
T-P 2 O 5 is about 1%, T-K 2 O is about 2%, T-Ca
O about 1.7%, T-MgO about 1%, TC about 292
%, The nitrogen and phosphorus contents are particularly high, and it is also suitable as a fertilizer.

【0013】以上のようにして乾燥藻により汚泥の濾過
除去をした後にはさらに細かな懸濁物や悪臭成分の濾過
も行なうと、より好ましい。そのための濾材としては濾
過力が高く、しかも何らかのかたちで使用済み後の再利
用を可能とするものが望ましく、特に土壌改良材適性を
有する材料を用いた濾材が望ましい。そのような濾材の
代表的な例は、多孔質珪酸カルシウム水和物、木炭、さ
らにはモミガラくん炭などで、これらを適宜に組み合わ
せて用いるとさらに好ましい。
After filtering and removing sludge with dried algae as described above, it is more preferable to filter finer suspensions and malodorous components. As a filter medium for that purpose, a filter medium having a high filtering power and being capable of being reused after being used in some form is desirable, and a filter medium using a material having a soil improving agent suitability is particularly desirable. Typical examples of such a filter medium are porous calcium silicate hydrate, charcoal, and husk charcoal, and it is more preferable to use them in an appropriate combination.

【0014】従って、本方法に用いる濾過装置は、上流
から順に乾燥藻層、多孔質珪酸カルシウム水和物層、木
炭層、モミガラくん炭層、及び木炭粉層を積層した構造
とするのが望ましい態様となる。
Therefore, it is desirable that the filtration device used in this method has a structure in which a dried algae layer, a porous calcium silicate hydrate layer, a charcoal layer, a chaffed charcoal layer, and a charcoal powder layer are laminated in this order from the upstream side. Becomes

【0015】[0015]

【実施例】以下、本発明の一実施例として、例えば上野
公園の不忍池のような条件を持つ池の清掃を主に人力を
主体にして進める例について説明する。
EXAMPLES As an example of the present invention, an example will be described below in which cleaning of a pond having conditions such as Shinobazu Pond in Ueno Park is carried out mainly by human power.

【0016】先ず、図1に示すように池1の岸に沿って
汚濁拡散防止膜2で封鎖的に囲った複数の作業領域3
(3a、3b、……3x)を設定する。各作業領域の面
積は30〜40m2 とする。汚濁拡散防止膜2は、図2
に示すように、防水性の膜材2cの上端に浮き2fを下
端に錘(図示せず)をそれぞれ取り付けてなっており、
浮き2fにより吊り下げた状態で設置する。
First, as shown in FIG. 1, a plurality of work areas 3 are enclosed along a shore of a pond 1 by a pollution diffusion prevention film 2 in a closed manner.
(3a, 3b, ... 3x) is set. The area of each work area is 30 to 40 m 2 . The pollution diffusion prevention film 2 is shown in FIG.
As shown in FIG. 2, a float 2f is attached to the upper end of the waterproof membrane material 2c, and a weight (not shown) is attached to the lower end,
It is installed while suspended by the float 2f.

【0017】全作業領域の設定が完了したら、ゴミの回
収作業と汚泥の浚渫やそれに伴う濾過処理作業とに分け
て各作業領域3a、3b、……3xについて順繰りに作
業を進める。具体的には、先ずゴミの回収作業担当者が
作業領域3a(人員に応じて3a、3b)についてゴミ
の回収作業を行なう。この間に浚渫や濾過処理の担当者
がその段取りを進める。そして、作業領域3aのゴミ回
収作業が完了したらゴミ回収作業担当者は次ぎの作業領
域3bに進み、浚渫や濾過処理の担当者が作業領域3a
について浚渫及び濾過処理を進める。
When the setting of all the work areas is completed, the work is proceeded in order for each work area 3a, 3b, ... 3x by dividing the work of collecting dust and the work of dredging sludge and the filtration process accompanying it. Specifically, first, a staff member for collecting dust collects dust in the work area 3a (3a, 3b depending on the number of personnel). During this time, the person in charge of dredging and filtering process will proceed with the setup. Then, when the dust collection work of the work area 3a is completed, the dust collection work person proceeds to the next work area 3b, and the person in charge of dredging and filtering processes the work area 3a.
Will proceed with the dredging and filtration process.

【0018】濾過処理に用いる濾過装置は、図3に示す
ように、上流側から順に乾燥オオフサモを充填した乾燥
藻層4、粒状の多孔質珪酸カルシウム水和物を充填した
多孔質珪酸カルシウム水和物層5、粒状の木炭を充填し
た木炭層6、モミガラくん炭を充填したモミガラくん炭
層7、及び粉状にした木炭を充填した木炭粉層8を積層
した構造とされ、その枠体9は木製とし内部に防水シー
ト(図示せず)を張ってある。その容積サイズは、縦、
横がそれぞれ2.5 mで高さが1.2 mの7.5 m3である。
また各層の厚みは上から順に、40cm、20cm、3
0cm、10cm、10cmとしている。
As shown in FIG. 3, the filtration device used for the filtration treatment is a dried algae layer 4 filled with dried oofsamom in order from the upstream side, and a porous calcium silicate hydrate filled with granular porous calcium silicate hydrate. The structure 9 has a structure in which a product layer 5, a charcoal layer 6 filled with granular charcoal, a chaffed charcoal layer 7 filled with chaff charcoal, and a charcoal powder layer 8 filled with powdered charcoal are laminated, and the frame body 9 thereof is It is made of wood and is covered with a waterproof sheet (not shown). Its volume size is vertical,
Beside it is 7.5 m 3 of 1.2 m height each 2.5 m.
The thickness of each layer is 40 cm, 20 cm, 3 in order from the top.
It is set to 0 cm, 10 cm, and 10 cm.

【0019】この濾過装置による濾過は吸引管10によ
り吸い上げた汚泥含有水や汚濁水を散水ノズル11によ
り上側から散水し、下側から濾過済み水を取り出して池
に戻すようにして行なう。散水速度は70〜100リッ
トル/分の条件とする。
Filtration by this filtration device is carried out by sprinkling sludge-containing water and polluted water sucked up by the suction pipe 10 from the upper side by the sprinkling nozzle 11, and taking out the filtered water from the lower side and returning it to the pond. The watering rate is set to 70 to 100 liters / minute.

【0020】濾過装置による汚泥の濾過はそのほとんど
が乾燥藻層4でなされ、多孔質珪酸カルシウム水和物層
5以下は主に微細な懸濁物の濾過や悪臭成分の濾過に機
能する。このため乾燥藻層4には処理の進行につれて目
詰まりを生じる。そこで、適当に見計らって乾燥藻層4
の乾燥オオフサモを入れ換える。使用済の乾燥オオフサ
モは、予め用意してある回収ボックスに投入して蓄えて
おき、最後に堆肥化処理場に運んで処理した後、堆肥と
して再利用する。ここで、回収ボックスへの貯蔵に際し
て汚泥の悪臭を防止するために脱臭剤を添加するのが望
ましいが、その脱臭剤としては例えば木酢液のように後
の堆肥化の際に障害とならないものを用いる。
Most of the sludge is filtered by the filter device in the dried algae layer 4, and the porous calcium silicate hydrate layer 5 and below mainly function to filter fine suspensions and malodorous components. Therefore, the dried algae layer 4 becomes clogged as the treatment progresses. Therefore, the dried algae layer 4 should be properly monitored.
Replace dried oofsamo. The used dried Oofusamo is thrown into a collection box prepared in advance and stored, and finally transported to a composting plant for processing, and then reused as compost. Here, it is desirable to add a deodorant in order to prevent the bad odor of the sludge during storage in the collection box, but as the deodorant, for example, a wood vinegar solution that does not hinder the subsequent composting is used. To use.

【0021】[0021]

【発明の効果】本発明による浚渫汚泥の処理方法は、以
上説明したように、乾燥藻を濾材に用いて汚泥の堆肥化
を図るようにしているので、汚泥の堆肥化処理を格段に
簡易化でき、汚泥の堆肥への活用を実際的なものとする
ことができる。
As described above, the method for treating dredging sludge according to the present invention is intended to facilitate the composting of sludge by using dried algae as the filter medium. It is possible to make practical use of sludge for compost.

【0022】また本発明による池の清掃方法は、以上説
明したように、汚濁拡散防止膜による封鎖的な作業領域
の設定と汚泥含有水や汚濁水の乾燥藻による濾過とを組
み合わせるようにしているので、清掃作業に伴う汚濁の
池の広い範囲への拡散を防止でき、また汚泥や汚濁水の
処理を効率的に行なえ、さらに汚泥の後処理を無駄なく
行なえ、環境に優しい処理とすることができる。
Further, in the pond cleaning method according to the present invention, as described above, the setting of a closed work area by the pollution diffusion preventing membrane and the filtration of sludge-containing water or polluted water with dry algae are combined. Therefore, it is possible to prevent the spread of pollution due to cleaning work over a wide area of the pond, to efficiently treat sludge and polluted water, and to perform post-treatment of sludge without waste, making it an environmentally friendly treatment. it can.

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

【図1】本発明による作業領域の設置状態を示す説明
図。
FIG. 1 is an explanatory view showing an installation state of a work area according to the present invention.

【図2】図1に示す作業領域の縦断面図。FIG. 2 is a vertical sectional view of a work area shown in FIG.

【図3】濾過装置の縦断面図。FIG. 3 is a vertical cross-sectional view of a filtration device.

【図4】オオフサモの生活形態図。FIG. 4 is a diagram of a life form of a giant sardine.

【符号の説明】[Explanation of symbols]

1 池 2 汚濁拡散防止膜 3 作業領域 4 乾燥藻層 5 多孔質珪酸カルシウム水和物層 6 木炭層 7 モミガラくん炭層 8 木炭粉層 1 Pond 2 Pollution Diffusion Prevention Membrane 3 Working Area 4 Dry Algae Layer 5 Porous Calcium Silicate Hydrate Layer 6 Charcoal Layer 7 Rice Hull Coal Layer 8 Charcoal Powder Layer

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 河川や湖沼などから浚渫した汚泥を処理
する方法において、汚泥とともに吸引した汚泥含有水に
乾燥藻を濾材とした濾過処理を施することにより、乾燥
藻に汚泥を付着させ、この汚泥付着の乾燥藻を堆肥とし
て利用するようにしたことを特徴とする浚渫汚泥の処理
方法。
1. A method for treating sludge dredged from rivers, lakes and marshes, wherein sludge-containing water sucked together with sludge is subjected to a filtration treatment using dried algae as a filter medium to attach the sludge to the dried algae. A method for treating dredged sludge, characterized in that dried algae attached to sludge is used as compost.
【請求項2】 乾燥藻として乾燥オオフサモを用いる請
求項1に記載の浚渫汚泥の処理方法。
2. The method for treating dredged sludge according to claim 1, wherein dried officinalis is used as the dried algae.
【請求項3】 乾燥藻の他に土壌改良材適性を有する材
料を用いた濾材を付加的に用いる請求項1又は請求項2
に記載の浚渫汚泥の処理方法。
3. The method according to claim 1 or claim 2, wherein a filter medium made of a material having a soil conditioner suitability is additionally used in addition to the dried algae.
The method for treating dredging sludge described in.
【請求項4】 上流側から順に乾燥藻層、多孔質珪酸カ
ルシウム水和物層、木炭層、モミガラくん炭層、及び木
炭粉層を積層してなる濾過装置を用いる請求項3に記載
の浚渫汚泥の処理方法。
4. The dredging sludge according to claim 3, wherein a filter device is used in which a dried algae layer, a porous calcium silicate hydrate layer, a charcoal layer, a rice charcoal layer and a charcoal powder layer are laminated in this order from the upstream side. Processing method.
【請求項5】 池や湖沼のような静止的水系について汚
泥の浚渫や底に溜まっているゴミの回収などを行なう清
掃方法において、水面から底まで垂らした汚濁拡散防止
膜により封鎖的に囲んで適宜の面積の作業領域を設定
し、この作業領域内でゴミの回収及び吸引による汚泥の
浚渫を進めるようにし、且つ吸引した汚泥含有水及び汚
泥の拡散により発生する作業領域内の汚濁水に乾燥藻を
濾材とした濾過処理を施し、これにより汚泥が付着した
使用済みの乾燥藻を堆肥として利用するようにしたこと
を特徴とする静止的水系の清掃方法。
5. A cleaning method for dredging sludge or collecting dust accumulated at the bottom of a static water system such as a pond or a lake, which is enclosed by a pollution diffusion prevention film hanging from the water surface to the bottom. Set a work area with an appropriate area, and proceed with dredging of sludge by collecting and sucking dust in this work area, and dry the polluted water in the work area that is generated by diffusion of sucked sludge-containing water and sludge. A static water-based cleaning method, wherein a filtration treatment using algae as a filter medium is performed so that used dry algae having sludge attached thereto is used as compost.
JP6030866A 1994-02-03 1994-02-03 Treatment of dredging sludge and cleaning method of static water system Pending JPH07215786A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6030866A JPH07215786A (en) 1994-02-03 1994-02-03 Treatment of dredging sludge and cleaning method of static water system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6030866A JPH07215786A (en) 1994-02-03 1994-02-03 Treatment of dredging sludge and cleaning method of static water system

Publications (1)

Publication Number Publication Date
JPH07215786A true JPH07215786A (en) 1995-08-15

Family

ID=12315658

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6030866A Pending JPH07215786A (en) 1994-02-03 1994-02-03 Treatment of dredging sludge and cleaning method of static water system

Country Status (1)

Country Link
JP (1) JPH07215786A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103964968A (en) * 2014-05-27 2014-08-06 华中农业大学 Sludge organic fertilizer for promoting vegetation restoration as well as preparation method and applications thereof
CN105800892A (en) * 2016-05-13 2016-07-27 安徽金农惠民生物技术有限公司 Blue-green algae and excess sludge resourceful treatment method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103964968A (en) * 2014-05-27 2014-08-06 华中农业大学 Sludge organic fertilizer for promoting vegetation restoration as well as preparation method and applications thereof
CN103964968B (en) * 2014-05-27 2015-10-14 华中农业大学 A kind of promote vegetation repair organic fertilizer produced from sludge generated and preparation method and application
CN105800892A (en) * 2016-05-13 2016-07-27 安徽金农惠民生物技术有限公司 Blue-green algae and excess sludge resourceful treatment method

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