JPH0536393B2 - - Google Patents
Info
- Publication number
- JPH0536393B2 JPH0536393B2 JP5979183A JP5979183A JPH0536393B2 JP H0536393 B2 JPH0536393 B2 JP H0536393B2 JP 5979183 A JP5979183 A JP 5979183A JP 5979183 A JP5979183 A JP 5979183A JP H0536393 B2 JPH0536393 B2 JP H0536393B2
- Authority
- JP
- Japan
- Prior art keywords
- water hyacinth
- water
- hyacinth
- fermentation
- sludge
- 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.)
- Expired - Lifetime
Links
- 241000169203 Eichhornia Species 0.000 claims description 31
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims description 22
- 238000000855 fermentation Methods 0.000 claims description 14
- 230000004151 fermentation Effects 0.000 claims description 13
- 239000010802 sludge Substances 0.000 claims description 11
- 239000007788 liquid Substances 0.000 claims description 10
- 238000000034 method Methods 0.000 claims description 9
- 238000010564 aerobic fermentation Methods 0.000 claims description 6
- 238000009264 composting Methods 0.000 claims description 4
- 235000011389 fruit/vegetable juice Nutrition 0.000 claims description 4
- 239000007787 solid Substances 0.000 claims description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 12
- 239000002361 compost Substances 0.000 description 9
- 239000007789 gas Substances 0.000 description 7
- 239000002699 waste material Substances 0.000 description 5
- 238000000746 purification Methods 0.000 description 4
- 230000001079 digestive effect Effects 0.000 description 3
- 238000001035 drying Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241000196324 Embryophyta Species 0.000 description 2
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 239000011591 potassium Substances 0.000 description 2
- 229910052700 potassium Inorganic materials 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 239000003516 soil conditioner Substances 0.000 description 2
- 241001632576 Hyacinthus Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 230000006978 adaptation Effects 0.000 description 1
- 239000002921 fermentation waste Substances 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000011550 stock solution Substances 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Classifications
-
- 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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- 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
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Description
本発明は、水域の浄化に利用された水生植物の
処理に係り、特にホテイアオイに好適な処理方法
に関するものである。
近年、水域の浄化のため水生植物を栽培し水中
の栄養塩を摂取させるという方法が利用されてき
ており、ホテイアオイなどが特に有望視されてい
るが、採取されたホテイアオイは高含水率のた
め、放置すると腐つて悪臭を放ち、また繊維質の
ためそのままではコンポスト化が困難で処理に困
つていた。そのため、重油をかけて焼却したり、
乾燥し農地へまいたりしていたが、燃料費が嵩ん
だりまた農地で分解せずに蓄積するなどの欠点が
あつた。
しかし、ホテイアオイは放置すると腐敗しだす
ことに着目し、ホテイアオイを貯留槽において一
部腐敗せしめる。それにより搾汁液の有機物濃度
が増し、また嫌気性発酵の順致にもなる。ローラ
ープレス、スクリユープレスなどプレス機によつ
て搾ることにより、分離かすは平面的になり、表
面積が増し特に根の部分がよく細断され非常に乾
燥しやすくなる。ホテイアオイはそのままでは好
気性発酵させるのは困難であるが、乾燥し汚泥な
どを混合して含水率を40〜60%の範囲に調製する
ことにより、コンポスト化することができる。
本発明はこの点に着目してその処理に困つてい
るホテイアオイから有効な消化ガスを回収し且脱
水分離かすをコンポスト化するようになしたホテ
イアオイの処理再利用法を提案するものである。
即ち本発明は水域の浄化の目的で栽培され採取さ
れたホテイアオイの処理において、採取したホテ
イアオイを一時貯留し、一部腐敗せしめ、その
後、圧搾して固液分離し、その搾汁液を用いてメ
タン発酵を行ない、分離かすをメタン発酵槽から
排出される消化汚泥と混合し好気性発酵を行ない
コンポスト化することによつて、ホテイアオイか
ら消化ガスを回収し、良質なコンポストを得るこ
とを要旨とする。
以下本発明を図面に示すホテイアオイ処理、再
利用法のフローチヤートにより説明する。
水域の浄化等を行う池や河川・湖沼その他例え
ばホテイアオイ栽培池より不必要になつたホテイ
アオイを採取し、これを貯留ピツト等にそのまま
収容して一時貯留せしめる。この貯留時ホテイア
オイの茎菜部、根部に付着する微生物によりホテ
イアオイが腐敗し始める。このホテイアオイはそ
のままでは殆んどが繊維質で、搾汁しても搾汁液
の有機物濃度は低いが貯留により、高濃度の搾汁
液が得られ、同時に嫌気性消化の順致の過程とも
なる。
次にこの腐敗し始めたホテイアオイをスクリユ
ープレス、ローラープレス等の圧搾工程へ送り、
ここで固液分離を行う。
メタンガス発酵のためには、発酵液の流動性が
良いことが必要であるがこの圧搾工程にて固液分
離することにより、高濃度で性状の良い発酵原液
が得られる。一方、ホテイアオイは高含水率(95
%程度)であり、茎のうきの部分の嵩が大きく、
よく水を含むので乾燥に長期間を要する。しかし
圧搾機によつて形状を変化させると表面積が大き
くなり、乾燥期間が大幅に短縮され、特に分解し
にくい根の部分がよく寸断される。この固液分離
された固体即ち分離かすは乾燥工程へ送ると共に
搾汁液をメタン発酵槽へ送つて貯留し、ここでメ
タンガス即ち消化ガスを発生せしめるが、この得
られた消化ガスはその一部をメタン発酵槽の加温
用に使用し、該発酵槽より発生する消化汚泥は脱
水してコンポストの原料とし、発酵廃液は汚泥脱
離水と共にホテイアオイ栽培地に戻し浄化したの
ち放流する。消化汚泥の脱水ケーキは分離かすの
乾燥後のものと混合し、含水率を40〜60%に調整
し、これを好気性発酵槽等に送り、ここで強制通
気による急速好気性発酵を行なう。オテイアオイ
は、単独ではコンポスト化は困難であるが、乾燥
し、汚泥などと混合し含水率を40〜60%の範囲と
すれば発酵可能である。このようにして処理され
たホテイアオイはコンポストとなり優良な土壤改
良剤として使用される。このようにして得られた
ホテイアオイと脱水汚泥からなる肥料成分は表の
如くである。
The present invention relates to the treatment of aquatic plants used to purify water bodies, and particularly to a treatment method suitable for water hyacinth. In recent years, methods of cultivating aquatic plants and ingesting nutrients from the water have been used to purify water bodies, and water hyacinth is particularly promising, but the collected water hyacinth has a high water content. If left unattended, it would rot and emit a foul odor, and its fibrous nature would make it difficult to compost it, making it difficult to dispose of it. Therefore, they are incinerated by pouring heavy oil on them,
Once dried, it was spread on farmland, but it had drawbacks such as high fuel costs and the fact that it accumulated on farmland without being decomposed. However, we focused on the fact that water hyacinth begins to rot if left unattended, so we allowed some of the water hyacinth to rot in a storage tank. This increases the concentration of organic matter in the juice and also makes it compatible with anaerobic fermentation. By squeezing with a press machine such as a roller press or a screw press, the separated waste becomes flat and has an increased surface area, and the roots in particular are shredded and become very easy to dry. It is difficult to aerobically ferment water hyacinth as it is, but it can be composted by drying it and mixing it with sludge etc. to adjust the moisture content to a range of 40 to 60%. The present invention focuses on this point and proposes a method for processing and reusing water hyacinth, which recovers effective digestive gas from water hyacinth, which is difficult to process, and composts the dehydrated residue.
That is, in the treatment of water hyacinth cultivated and collected for the purpose of purifying water bodies, the present invention temporarily stores the collected water hyacinth, allows it to partially rot, then presses it to separate solid and liquid, and uses the squeezed liquid to produce methane. The purpose is to recover digestive gas from water hyacinth and obtain high-quality compost by performing fermentation, mixing the separated residue with digested sludge discharged from a methane fermentation tank, performing aerobic fermentation, and composting. . The present invention will be explained below with reference to a flowchart of a water hyacinth treatment and recycling method shown in the drawings. Water hyacinth that is no longer needed is collected from ponds, rivers, lakes and marshes where water bodies are purified, etc., and from, for example, water hyacinth cultivation ponds, and is stored as is in a storage pit or the like for temporary storage. During this storage, the water hyacinth begins to rot due to microorganisms that adhere to the stems and roots of the water hyacinth. This water hyacinth is mostly fibrous as it is, and even if it is squeezed, the concentration of organic matter in the juice is low, but by storage, a high-concentration juice can be obtained, and at the same time it becomes a process of adaptation to anaerobic digestion. Next, this water hyacinth that has begun to rot is sent to a squeezing process such as a screw press or roller press.
Solid-liquid separation is performed here. For methane gas fermentation, it is necessary for the fermentation liquor to have good fluidity, and by separating solid and liquid in this squeezing step, a fermentation stock solution with high concentration and good properties can be obtained. On the other hand, water hyacinth has a high water content (95
%), and the volume of the stem part is large,
Because it contains a lot of water, it takes a long time to dry. However, changing the shape using a press increases the surface area, significantly shortens the drying period, and particularly shreds the roots, which are difficult to decompose. This solid-liquid separated solid, that is, separated waste, is sent to a drying process, and the squeezed liquid is sent to a methane fermentation tank and stored there, where methane gas, that is, digestion gas, is generated. It is used to heat the methane fermentation tank, and the digested sludge generated from the fermentation tank is dehydrated and used as a raw material for compost, and the fermentation waste liquid is returned to the water hyacinth cultivation area together with the sludge-removed water for purification and then released. The dehydrated cake of digested sludge is mixed with the dried separated sludge, the moisture content is adjusted to 40 to 60%, and the cake is sent to an aerobic fermentation tank where rapid aerobic fermentation is performed using forced ventilation. It is difficult to compost Oteia hyacinth alone, but it can be fermented if it is dried and mixed with sludge to bring the moisture content to a range of 40 to 60%. Water hyacinth treated in this way becomes compost and is used as an excellent soil conditioner. The fertilizer components consisting of water hyacinth and dehydrated sludge thus obtained are shown in the table below.
【表】
一般に消化汚泥など汚泥のコンポストは、窒
素、リンは充分であつてもカリ成分が少ないがホ
テイアオイに多量に含有するカリ成分のため生成
コンポストはN:P:Kの比率が好適になる。
而して本発明によれば、水の浄化に使用された
ホテイアオイはメタン発酵と好気性発酵の両方の
材料として使用され消化ガス及びコンポストとい
う有用な資源に交換され、その際メタン発酵より
排出される消化汚泥はコンポスト化の原料とな
り、消化ガスの一部がメタン発酵槽の加温用に使
用され、その廃液は少し加温されておりそのまま
ホテイアオイの栽培池に戻されて浄化されたのち
放流されるがこの時加温廃液によつてホテイアオ
イの栽培が促進されると共に本発明は廃棄物のな
いクローズドシステムであり、水域の浄化に利用
したホテイアオイを有効に利用でき、特に分離か
すは従来の如く燃料費をかけて焼却するかわりに
そのまま農地に乾燥して還元すると難分解で土壤
に蓄積し、問題となつていたがコンポスト化する
ことにより、優良な土壤改良剤となる等の利点を
有する。[Table] In general, compost made from sludge such as digested sludge has a sufficient amount of nitrogen and phosphorus but is low in potassium components, but because water hyacinth contains a large amount of potassium components, the resulting compost has a suitable N:P:K ratio. . According to the present invention, water hyacinth used for water purification is used as a material for both methane fermentation and aerobic fermentation, and is exchanged into useful resources such as digestive gas and compost, and at this time, the water hyacinth used for water purification is used as a material for both methane fermentation and aerobic fermentation. Digested sludge is used as raw material for composting, part of the digested gas is used to heat the methane fermentation tank, and the waste liquid is slightly heated and returned to the water hyacinth cultivation pond where it is purified and then released. However, at this time, the cultivation of water hyacinth is promoted by the heated waste liquid, and the present invention is a closed system without waste, and the water hyacinth used for water purification can be effectively used. Instead of incinerating it at the expense of fuel, it would be difficult to decompose and accumulate in the soil if it was dried and returned to farmland, which caused problems, but by composting it, it has the advantage of becoming an excellent soil conditioner. .
図面は本発明ホテイアオイの処理、再利用法を
示すフローチヤートである。
The drawing is a flowchart showing the method for processing and reusing water hyacinth according to the present invention.
Claims (1)
め、その後、圧搾して固液分離し、その搾汁液を
用いてメタン発酵を行い、分離かすをメタン発酵
槽から排出される消化汚泥と混合し好気性発酵を
行いコンポスト化することを特徴とするホテイア
オイの処理方法。1 Water hyacinth is temporarily stored and partially rotted, then squeezed to separate solid and liquid, the juice is used for methane fermentation, and the separated residue is mixed with digested sludge discharged from the methane fermentation tank. A method for processing water hyacinth characterized by performing aerobic fermentation and composting.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58059791A JPS59184783A (en) | 1983-04-04 | 1983-04-04 | Treatment and regeneration of eichhornia crassipes |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58059791A JPS59184783A (en) | 1983-04-04 | 1983-04-04 | Treatment and regeneration of eichhornia crassipes |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS59184783A JPS59184783A (en) | 1984-10-20 |
JPH0536393B2 true JPH0536393B2 (en) | 1993-05-28 |
Family
ID=13123454
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP58059791A Granted JPS59184783A (en) | 1983-04-04 | 1983-04-04 | Treatment and regeneration of eichhornia crassipes |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS59184783A (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3843670C1 (en) * | 1988-12-23 | 1990-09-13 | Vertikum Magas- Es Melyepitmenyjavito Kisszoevetkezet, Budapest, Hu | |
WO2005080297A1 (en) * | 2004-01-23 | 2005-09-01 | Simon Njoroge Mwaura | Method of converting aquatic plants especially hyacinth into useful products |
CN101928157B (en) * | 2010-05-10 | 2012-09-19 | 浙江大学 | Process for producing organic liquid fertilizer by degrading water hyacinth by hydrothermal treatment process |
CN101935244B (en) * | 2010-08-23 | 2012-08-22 | 江苏省农业科学院 | Salt fertilization of water hyacinth fermentation liquor and application thereof |
-
1983
- 1983-04-04 JP JP58059791A patent/JPS59184783A/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPS59184783A (en) | 1984-10-20 |
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