JPH04122490A - Synthetic treatment and utilization of environmental pollutant - Google Patents

Synthetic treatment and utilization of environmental pollutant

Info

Publication number
JPH04122490A
JPH04122490A JP2244277A JP24427790A JPH04122490A JP H04122490 A JPH04122490 A JP H04122490A JP 2244277 A JP2244277 A JP 2244277A JP 24427790 A JP24427790 A JP 24427790A JP H04122490 A JPH04122490 A JP H04122490A
Authority
JP
Japan
Prior art keywords
charcoal
waste
sludge
wastewater
water
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
JP2244277A
Other languages
Japanese (ja)
Inventor
Akio Onda
御田 昭雄
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP2244277A priority Critical patent/JPH04122490A/en
Publication of JPH04122490A publication Critical patent/JPH04122490A/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
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

PURPOSE:To synthetically treat and utilize an environmental pollutant by obtaining charcoal from solid waste containing org. matter and bringing the same into contact with waste water to separate and recover charcoal-containing sludge and purified water, and utilizing the sludge as fertilizer and a soil conditioned. CONSTITUTION:Solid waste containing org. matter is baked in a closed system to obtain charcoal which is, in turn, brought into contact with waste water to separate and recover charcoal-containing sludge, and purified water and the charcoal-containing sludge is utilized as fertilizer or a soil conditioner and, by reducing the generation amount of carbon dioxide, an environmental pollutant is synthetically treated and utilized. When charcoal of dust containing calcium oxide is used, phosphoric acid in waste water is adsorbed and immobilized and, when charcoal containing magnesium oxide is used, the removing capacity of ammonia and phosphoric acid in waste water is drastically enhanced. When sludge containing calcium carbonate and magnesium carbonate is used at the time of carbonization, charcoal of dust becomes a waste water treatment agent.

Description

【発明の詳細な説明】 〔技術分野〕 本発明は人類の生活及び活動に伴って発生し、地球環境
を汚染する固形廃棄物、排水又は及び排気を総合的に処
理し、利用する方法を提供する。
[Detailed Description of the Invention] [Technical Field] The present invention provides a method for comprehensively treating and utilizing solid waste, wastewater, or exhaust gas that is generated in the course of human life and activities and pollutes the global environment. do.

〔従来技術及び対策〕[Prior art and countermeasures]

人類は大量に消費する資源の涸渇に悩み、一方大量に発
生する廃棄物の対策と、環境問題に困惑している。
Humanity is worried about the depletion of the resources it consumes in large quantities, and at the same time is at a loss as to how to deal with the large amount of waste it generates and environmental problems.

従来排水と、固形廃棄物と排気は、それぞれ別個に処理
し、更に発生する2次公害に悩まされて来た。例えば都
市固形廃棄物は放置すれば腐敗し、はえが発生し、最終
的には二酸化炭素と水に分解する。これを埋立て処理に
切替えれば、はえの発生は無くなるが、地下水の汚染を
もたらし、メタンガスを発生し、最終的には二酸化炭素
と水に分解する。さらに焼却処理に切替えた場合、処理
は迅速に行えれるが、やはり二酸化炭素と水に分解され
る。これらの方法では世界規模で問題となっている地球
温暖化の原因とされる二酸化炭素やメタンガス発生の抑
止には役立っていないことがわかる。
Conventionally, wastewater, solid waste, and exhaust gas have been treated separately, and the resulting secondary pollution has been a problem. For example, if municipal solid waste is left unattended, it will rot, generate flies, and eventually decompose into carbon dioxide and water. If this process is switched to landfill, flies will no longer occur, but it will contaminate groundwater, generate methane gas, and eventually decompose into carbon dioxide and water. Furthermore, if the process is switched to incineration, the process can be carried out quickly, but it still decomposes into carbon dioxide and water. It can be seen that these methods are not effective in suppressing the generation of carbon dioxide and methane gases, which are the causes of global warming, which is a worldwide problem.

また地球の緑化による環境保全が広く訴えられているが
、農産廃棄物を放置したり、焼却したり、また堆肥とし
て施肥していたのでは、早暁これら有機物は二酸化炭素
と水にまで分解するし、植林を行って二酸化炭素を固定
しても森林の枯葉や枯枝も、さらには伐らずに置いた立
木でさえ、何時かは枯れて二酸化炭素と水に分解するの
で、これまで進められている緑化は地表の近くで二酸化
炭素から固定した有機物を分解するまでの短い時間(数
日〜数100年)止めて置くことしか期待出来なかった
In addition, environmental conservation through greening the earth has been widely advocated, but if agricultural waste is left alone, incinerated, or fertilized as compost, these organic substances will quickly decompose into carbon dioxide and water. Even if we fix carbon dioxide by planting trees, dead leaves and branches in the forest, and even standing trees left uncut, will eventually wither and decompose into carbon dioxide and water, so we have not been able to do so until now. The only hope of greening in the world was to stop it for a short period of time (several days to several hundred years) until organic matter fixed from carbon dioxide decomposed near the earth's surface.

一方、人類は有機物からなる化石燃料を掘り出し、大気
中の酸素を奪い燃焼してエネルギーを取出すとともに、
二酸化炭素や二酸化硫黄を大気中に放出し公害を起して
来た。そのため今日まで多くの公害処理技術が発明され
た。脱硫技術の幾つかは完成し、先進工業国では実用に
供されているが、脱硫工程で副生ずる物質の用途に悩ま
されて来た。二酸化炭素の固定化は、その発生量が多い
だけに地球規模での環境改善に役立つような技術と、そ
の核になるような発明もまったく発表されなかった。
On the other hand, humans mined fossil fuels made of organic materials, deprived of oxygen from the atmosphere, burned them, and extracted energy.
They have been causing pollution by releasing carbon dioxide and sulfur dioxide into the atmosphere. Therefore, many pollution treatment techniques have been invented to date. Although some desulfurization technologies have been perfected and are in practical use in industrialized countries, the use of substances by-products of the desulfurization process has been problematic. As carbon dioxide fixation generates a large amount of carbon dioxide, no technology or inventions that could be at the core of this process have been announced that would help improve the environment on a global scale.

また人類が日常生活や産業活動をするのに伴って必要と
する水の量は急増し、それに伴って発生する排水の量も
急増している。先進国では排水を凝集沈澱法、メタン発
酵法、活性汚泥法等を用いて処理し、その中の毒性物質
や有機物を分解除去する排水の浄化技術が開発され、普
及しつつある。
Furthermore, the amount of water that humans require in their daily lives and industrial activities is rapidly increasing, and the amount of wastewater generated is also rapidly increasing. In developed countries, wastewater purification technologies have been developed and are becoming popular, in which wastewater is treated using methods such as coagulation sedimentation, methane fermentation, and activated sludge to decompose and remove toxic substances and organic matter.

しかし、生活様式の変化に伴って下水の中にはりん酸や
窒素の含有物が増加し、いわゆる富栄養化による青こや
、赤潮の原因となるとして活性炭による吸着等その対策
が研究された来た。しかし大量の水を扱うにはそれら処
理材の原料が資源的に足りなかったり、処理後の滓の捨
て場がないなど2次公害に悩まされ続けて来た。又一方
、りん酸やアンモニウム等はともに重要な肥料成分であ
り、特にりん酸の資源は鉱石として地球の一部地方に偏
在し、かつ資源量の不足が心配されているにも関わらず
、りん鉱石を採掘し、肥料や洗剤の製造に供していた。
However, as lifestyles change, sewage contains an increasing amount of phosphoric acid and nitrogen, causing so-called eutrophication, which causes green mold and red tide, and research has been conducted into countermeasures such as adsorption with activated carbon. It's here. However, in order to handle large amounts of water, there were insufficient raw materials for these treatment materials, and there was no place to dispose of the slag after treatment, resulting in secondary pollution. On the other hand, both phosphoric acid and ammonium are important fertilizer ingredients, and in particular, phosphoric acid resources are unevenly distributed in some regions of the earth as ore, and there are concerns about resource shortages. The ore was mined and used to make fertilizers and detergents.

肥料の活用に伴って生産される食糧や飼料は利用され、
排泄され、排泄物の多くは下水に流れ、洗濯排水等と共
に河川の富栄養化の原因となっていることは、前述のよ
うに分りながら、適切な技術がないため処理することも
出来ず、またりん酸の涸渇が人類の生存の危機であると
は知りながら回収もせずただ手を挑いていることしか出
来なかった。
Food and feed produced with the use of fertilizers are used,
As mentioned above, it is known that much of the excrement flows into the sewage system and causes eutrophication of rivers along with laundry wastewater, etc. However, due to lack of appropriate technology, treatment cannot be done. Even though they knew that the depletion of phosphoric acid was a threat to the survival of humanity, they did nothing but try to recover it.

最近化学肥料の連用により土壌の劣化と、それに伴うバ
イオマスの生産性の低下が心配されているが木炭を土壌
改良剤として用いることにより、吸湿性、保水性、通気
性等の物理性が改良され、土壌の有害細菌の生育を抑え
、有用細菌の生育に良環境をもたらす他、肥料の保持能
力が向上すると云う研究発表が相次ぎ、その効用が見直
されている。しかし広大な耕地に使用する木炭の原料を
供給しうる程の森林資源は地球上に見出し難くなってい
る。
Recently, there have been concerns about soil deterioration due to continuous use of chemical fertilizers and the resulting decline in biomass productivity, but by using charcoal as a soil conditioner, physical properties such as hygroscopicity, water retention, and air permeability can be improved. Its effectiveness is being reconsidered as a number of studies have been published showing that it suppresses the growth of harmful bacteria in the soil, provides a favorable environment for the growth of useful bacteria, and improves the ability to retain fertilizers. However, it is becoming difficult to find enough forest resources on earth to supply raw materials for the charcoal used on vast arable land.

〔発明の課題〕[Problem of invention]

本発明は人類の営みによって廃棄される固形廃棄物、排
水又は及び排気を処理し、処理によって副生ずる反応生
成物を用いて相互に反応させ又新らたな用途を作ること
で資源化し、地球の環境と資源の問題の改善を可能とす
る方法を提供することをその課題とする。
The present invention treats solid waste, waste water, or exhaust gas disposed of by human activities, and uses reaction products produced by the treatment to react with each other and create new uses, thereby converting it into resources and saving the earth. Its task is to provide methods that make it possible to improve environmental and resource problems.

〔課題を解決するための手段〕[Means to solve the problem]

本発明者は、前記課題を解決すべく鋭意研究を重ねた結
果、本発明を完成するに至った。
The present inventor has completed the present invention as a result of intensive research to solve the above problems.

即ち本発明によれば、排水の処理に有機物を含む廃棄物
を蒸し焼きにして得た炭(ごみの炭)を用いて清澄水を
得、一方汚染物質を吸着したごみの炭は、土壌改良剤と
して土壌に供給することを特徴とする固形廃棄物と排水
の総合的処理及び利用方法を提供する。
That is, according to the present invention, clear water is obtained by using charcoal (garbage charcoal) obtained by steaming waste containing organic matter for wastewater treatment, while garbage charcoal that has adsorbed pollutants is used as a soil conditioner. The present invention provides a method for comprehensive treatment and utilization of solid waste and wastewater, which is characterized in that it is supplied to the soil as wastewater.

また、本発明によれば酸化カルシウムを含むごみの炭を
用いることにより、排水中のりん酸を吸着固定し、酸化
マグネシウムを含む炭を用いればアンモニウムとりん酸
を不溶化し、りん酸アンモニウム、マグネシウムを生成
するため、排水中のアンモニアとりん酸の除去能力は飛
躍的に向」ニし、く溶性のりん酸とアンモニアの複合肥
料を含むごみの炭を得る方法が提供される。また、この
ような目的に用いるごみの炭は炭化の際に炭酸カルシウ
ム、炭酸マグネシウムを含むスラッジを用いることによ
り、炭と酸化カルシウム又は及び酸化マグネシウムが混
合物として得られ排水の処理剤として提供される。この
際分離回収する水は清澄であるがアルカリ性である。本
発明ではさらに硫酸アルミニウム又は塩化鉄を加えれば
中和でき、この際生ずる水酸化アルミニウム又は水酸化
鉄のフロックがりん酸と不溶性物質をつくり共沈し、窒
素、りん酸、鉄及びCODを痕跡程度にまで減らせる方
法を提供する。本発明では活性炭による排煙の脱硫で得
られる排煙脱硫硫酸でアルミニウムの空缶を処理するこ
とにより硫酸アルミニウムを取得する方法を提供する。
In addition, according to the present invention, by using garbage charcoal containing calcium oxide, phosphoric acid in waste water is adsorbed and fixed, and by using charcoal containing magnesium oxide, ammonium and phosphoric acid are insolubilized, and ammonium phosphate and magnesium phosphate are insoluble. As a result, the ability to remove ammonia and phosphoric acid from wastewater is dramatically improved, and a method for obtaining waste charcoal containing a complex fertilizer of soluble phosphoric acid and ammonia is provided. In addition, the waste charcoal used for this purpose is carbonized by using sludge containing calcium carbonate and magnesium carbonate to obtain a mixture of charcoal and calcium oxide or magnesium oxide, which can be used as a treatment agent for wastewater. . At this time, the water to be separated and recovered is clear but alkaline. In the present invention, neutralization can be achieved by further adding aluminum sulfate or iron chloride, and the flocs of aluminum hydroxide or iron hydroxide produced at this time create an insoluble substance with phosphoric acid and co-precipitate, leaving traces of nitrogen, phosphoric acid, iron, and COD. We provide a method to reduce this to a certain degree. The present invention provides a method for obtaining aluminum sulfate by treating an empty aluminum can with flue gas desulfurization sulfuric acid obtained by desulfurizing flue gas using activated carbon.

以上本発明により固形廃棄物、排水及び排煙の処理物を
相互に反応させ副生物を利用可能にすることにより資源
化し、この間に有機物は蒸し焼きにして炭を得、排水中
の窒素、りん酸と共に土壌に供給するため殆ど永久に安
定に保存するため燃焼するのに比ベニ酸化炭素の発生量
を大きく削減しうる廃棄物の新らしい総合的処理及び利
用のシステムが提供しうる。
As described above, according to the present invention, solid waste, waste water, and flue gas treated products are reacted with each other and the by-products are made available for use as resources. At the same time, it is possible to provide a new comprehensive treatment and utilization system for wastes that can greatly reduce the amount of carbon dioxide produced compared to combustion, since it can be stably stored almost forever for supply to the soil.

本発明でごみの炭の原料となる固形廃棄物とはリグニン
、炭水化物、等天然有機物を含む紙屑、稲わら、籾殻、
芋づる、鋸屑、枯枝等の他、多くのプラスチック屑等が
挙げられ、またこれらの混合物である都市とみもその対
象となる。
In the present invention, the solid waste that is used as a raw material for garbage charcoal is waste paper, rice straw, rice husk, etc. containing natural organic substances such as lignin and carbohydrates.
In addition to potato vines, sawdust, dead branches, etc., there are many other types of plastic waste, and a mixture of these types of waste is also included.

炭化の際熱分解で酸化マグネシウム又は及び酸化カルシ
ウムを与える原料としては炭酸マグネシウム、白雲石及
び炭酸カルシラ11等の無機物も挙げられるが、パルプ
排水等のシーライム法処理で副生ずるマグネシウム、カ
ルシウムと有機物からなるスラッジや製糖の際副生する
カルシウムと有機物からなる石炭スラッジ等の廃棄物も
使用しうる。
Inorganic substances such as magnesium carbonate, dolomite, and calcilla carbonate 11 can be used as raw materials that yield magnesium oxide or calcium oxide through thermal decomposition during carbonization, but magnesium, calcium, and organic substances that are produced as by-products in the sea lime process such as pulp wastewater can be used as raw materials. It is also possible to use waste materials such as coal sludge consisting of calcium and organic matter produced by-product during sugar refining.

硫酸アルミニウムを自家製するときの原料としては、ア
ルミニウムの空き缶や排煙を活性炭によって脱硫する際
に売られる排煙脱硫々酸等が利用できる。
Raw materials for making aluminum sulfate in-house include empty aluminum cans and flue gas desulfurization acid, which is sold when flue gas is desulfurized using activated carbon.

又、本発明の各工程の反応条件について述へる。Also, the reaction conditions for each step of the present invention will be described.

炭化の条件は有機物を含む固形廃棄物に対し酸素を遮断
するか、もしくは割断しながら加熱し、250〜1 、
200°C1好ましくは300〜500℃に保持する。
The conditions for carbonization are to cut off oxygen to the solid waste containing organic matter, or to heat it while cutting it, at a temperature of 250~1,
The temperature is maintained at 200°C, preferably 300-500°C.

この際炭水化物の特に多い紙屑等は250〜400°C
で、リグニンが比較的多い枯枝等の場合は350〜50
0℃に保持することが望ましい。また含窒素或いは含塩
素化合物が混入し、これを分解させたいときは500〜
1,200°Cに保持することが望ましい。この際酸素
の供給量をゼロに近づければ炭の収率は上昇するが、特
にセルロースが多い場合、着火するまで空気の供給量を
多くし、その後空気の供給量を殆どゼロに近い状態に置
いてもセルロースの分解熱で炭化は進行する。
At this time, paper waste, etc., which is particularly high in carbohydrates, should be heated to 250 to 400°C.
In the case of dead branches etc. with relatively high lignin content, 350 to 50
It is desirable to maintain the temperature at 0°C. Also, if nitrogen-containing or chlorine-containing compounds are mixed in and you want to decompose them,
It is desirable to maintain the temperature at 1,200°C. At this time, the yield of charcoal will increase if the amount of oxygen supplied approaches zero, but especially when there is a large amount of cellulose, the amount of air supplied will be increased until ignition occurs, and then the amount of air supplied will be reduced to almost zero. Carbonization will continue due to the heat of decomposition of cellulose.

炭の収率は原料有機物に対し]5〜25%で、リグニン
等ベンゼン環構造を有する原料では一般に収率は高い。
The yield of charcoal is 5 to 25% based on the raw material organic matter, and the yield is generally high for raw materials having a benzene ring structure such as lignin.

また炭化の温度を上げたり塩化亜鉛や水蒸気で賦活すれ
ば炭の密度は上がり吸着能は向」―するが、より低温で
炭化すれは炭素の収率は上昇し、二酸化炭素の発生量を
減せるので望ましい。
In addition, raising the carbonization temperature or activating it with zinc chloride or steam will increase the density of the charcoal and improve its adsorption capacity, but carbonization at a lower temperature will increase the carbon yield and reduce the amount of carbon dioxide generated. This is desirable because it allows

なお炭化の際に発生するガス及び低沸点の液体は可燃性
で、他の燃料と混焼すれば2次公害の発生を防ぎ、熱エ
ネルギーの回収が可能となる。
Note that the gas and low-boiling point liquid generated during carbonization are flammable, so if they are mixed with other fuels, secondary pollution can be prevented and thermal energy can be recovered.

マグネシウム又は及びカルシウムを大量に含むスラッジ
等から酸化マグネシウム又は酸化カルシウムを取得する
場合は炭化の温度を上げるか焼却によって温度を上げる
必要がある。すなわち酸化マグネシウムを取得の目的と
するときは550〜1,100℃、好ましくは600〜
800°Cに酸化カルシウムを取得の目的とする場合は
900〜1,400℃、好ましくは950〜1 、20
0℃にそれぞれ保持する。ごみの炭に含まれる酸化マグ
ネシウム又は酸化カルシウムの量は合計で0.02〜2
rで処理する排水中のりん酸及びアンモニアの量によっ
て適量は大きく変るが、好ましくは0.05〜0.錦で
ある。求める含有量には通常のごみの炭との配合によっ
て調整するのが望ましい。
When obtaining magnesium oxide or calcium oxide from sludge or the like containing a large amount of magnesium or calcium, it is necessary to increase the carbonization temperature or increase the temperature by incineration. That is, when the purpose is to obtain magnesium oxide, the temperature is 550-1,100°C, preferably 600-1,100°C.
When the purpose is to obtain calcium oxide at 800°C, the temperature is 900 to 1,400°C, preferably 950 to 1,20°C.
Each was kept at 0°C. The total amount of magnesium oxide or calcium oxide contained in garbage charcoal is 0.02 to 2.
The appropriate amount varies greatly depending on the amount of phosphoric acid and ammonia in the wastewater to be treated with r, but preferably 0.05 to 0. It is brocade. It is desirable to adjust the desired content by mixing it with ordinary garbage charcoal.

ごみの炭(または酸化マグネシウム及び酸化カルシウム
を含む)による排水の処理は極めて容易である。両者の
接触の高温は広く、0〜100℃、好ましくは10〜5
0’Cである。両者の混合の割合は、排水により汚染の
程度によって大きく異るが、1m3当り、0.1−50
kg、好ましくは0.5−1.Okgである。
Treatment of wastewater with garbage charcoal (or containing magnesium oxide and calcium oxide) is extremely easy. The high temperature of contact between the two is wide, 0 to 100°C, preferably 10 to 5°C.
It is 0'C. The mixing ratio of the two varies greatly depending on the degree of pollution caused by wastewater, but it is 0.1-50% per m3.
kg, preferably 0.5-1. It is OK.

方法としては両者を混合し、静置することも撹拌し続け
ることも、またごみの炭を袋に入れて排水中吊すことも
、濾床として排水と接触することも可能である。接触後
清澄水と分離した排水中の7η染物質を含むごみの炭は
土壌改良剤として取得する。酸化マグネシウム又は酸化
力ルシウt1を含むごみの炭と接触することにより得ら
れるアルカリ性の清澄水は硫酸アルミニウム又は塩化鉄
で中和することにより最後まで残った少量のりん酸及び
COD物質も殆どゼロに近い状態まで除去される。
As for the method, it is possible to mix the two and leave it to stand still or to continue stirring it, to put garbage charcoal in a bag and suspend it during drainage, or to use it as a filter bed in contact with the drainage water. The waste charcoal containing 7η dyed substances in the wastewater separated from the clear water after contact is obtained as a soil conditioner. The alkaline clear water obtained by contacting garbage charcoal containing magnesium oxide or oxidizing lucium t1 is neutralized with aluminum sulfate or iron chloride, and the remaining small amounts of phosphoric acid and COD substances are reduced to almost zero. removed to a near state.

〔発明の効果〕〔Effect of the invention〕

]] 本発明は適用の範囲が極めて広く、実施が容易で、地球
の環境と資源保善と緑化とバイオマスの生産性の改善に
及ぼす効果が大きく期待される。
]] The present invention has an extremely wide range of application, is easy to implement, and is expected to have great effects on the earth's environment, resource conservation, greening, and improvement of biomass productivity.

すなわち固形廃棄物としては有機物を含むものであれば
、紙屑等の都市とみ、稲わら、麦わら籾殻、いもづる等
の農産廃棄物、落葉、枯枝、鋸屑、開墾地の倒木等、林
産廃棄物等数10億tも地球上で発生するごみに本発明
が適用でき、排工水処理剤として有用なごみの炭が有機
物11当り200kg、地球上で年間数位1−1+得る
ことが可能となった。
In other words, if solid waste contains organic matter, it is considered urban waste such as paper waste, agricultural waste such as rice straw, wheat straw chaff, potato vine, fallen leaves, dead branches, sawdust, fallen trees in cleared land, forestry waste, etc. The present invention can be applied to billions of tons of waste generated on earth, and it has become possible to obtain 200 kg of waste charcoal useful as a waste water treatment agent per 11 organic substances, which is about 1-1+ per year on earth.

そのことにより従来行われて来た投棄、焼却、堆肥の製
造及びその施肥に比べ有機物1を当り約600瞳の二酸
化炭素の発生を減らすことが可能となった。
As a result, compared to the conventional methods of dumping, incinerating, producing compost, and fertilizing the same, it has become possible to reduce the amount of carbon dioxide produced by approximately 600 units per 1 organic substance.

本発明で得られたごみの炭を各種排工水の処理に用いれ
ば溶存する主として有機高分子物質と看色物質の吸着が
可能であり、酸化カルシウム又は酸化マグネシウムを含
むごみの炭を用いれば前者ではりん酸、後者ではりん酸
とアンモニア等の除去や可能となり、水処理後の炭は、
本来の吸水性、通気性及び保水性を土壌に与える他、窒
素、りん酸、マグネシウム及びカルシウム等植物の必須
成分や土壌の有用細菌の栄養となる有機物を補給するた
め、耕地、山林、開墾地等に施せば肥沃化を促し、バイ
オマスの生産性と地球の緑化に効果が期待できる。
If the waste charcoal obtained in the present invention is used to treat various types of waste water, it is possible to adsorb mainly dissolved organic polymer substances and color substances, and if the waste charcoal containing calcium oxide or magnesium oxide is used, The former makes it possible to remove phosphoric acid, and the latter makes it possible to remove phosphoric acid and ammonia, etc., and the charcoal after water treatment is
In addition to providing the soil with its natural water absorption, air permeability, and water retention properties, it is also used in cultivated land, forests, and cultivated land to replenish organic matter that nourishes essential plant components such as nitrogen, phosphoric acid, magnesium, and calcium, as well as beneficial bacteria in the soil. If applied to other areas, it can be expected to promote fertilization, increase biomass productivity, and green the earth.

酸化マグネシウム又は及び酸化カルシウムを含むごみの
炭で処理して得られる水はアルカリ性であるが、これを
硫酸アルミニウム、塩化鉄又は排煙脱硫硫酸でアルミニ
ウムの缶を処理した液で中和することにより、残留りん
酸のほぼ全量が除去でき、はとんど中性で清澄な水が得
られるに至った。
The water obtained by treating waste charcoal containing magnesium oxide or calcium oxide is alkaline, but by neutralizing it with a solution obtained by treating aluminum cans with aluminum sulfate, iron chloride, or flue gas desulfurization sulfuric acid. Almost all of the residual phosphoric acid was removed, resulting in almost neutral and clear water.

以上のように従来側々に処理しようとして来たため河川
の富栄養化や処理残滓等の2次公害の問題は本発明が固
形廃棄物は炭化し、排煙脱硫硫酸と空き缶で、中和剤を
作って互に反応させ反応生成物を利用する本発明によっ
て解決の途が開かれた。
As mentioned above, the problems of secondary pollution such as eutrophication of rivers and treatment residues have been solved because conventional methods have been attempted to treat them side by side.In the present invention, solid waste is carbonized, flue gas desulfurized sulfuric acid and empty cans are used to solve the problem of secondary pollution such as river eutrophication and processing residue. The present invention has opened the way to a solution by making and reacting with each other and utilizing the reaction products.

〔実施例〕〔Example〕

以下実施例をもって本発明を更に詳細に説明する。 The present invention will be explained in more detail with reference to Examples below.

実施例1 紙屑(固形分86.5%)500g、枯枝(固形分65
.2%)500g、稲わら(固形分87.4%)500
gを取り約5印に切断して混合し、炉の中に入れ、空気
の流入量を制限しながら最高温度450℃まで加熱し、
同温度に3時間保持し、ごみの炭30.]、g(対固形
分収率25.2%)を得た。
Example 1 500 g of paper waste (solid content 86.5%), dead branches (solid content 65%)
.. 2%) 500g, rice straw (solid content 87.4%) 500g
g, cut it into approximately 5 marks, mix it, put it in a furnace, and heat it to a maximum temperature of 450°C while restricting the amount of air flowing in.
Keep at the same temperature for 3 hours and use garbage charcoal for 30 minutes. ], g (yield based on solid content: 25.2%).

実施例2 紙屑(固形分86.錦)500g、かんな屑(固形分8
7.1%)500g、籾殻(固形分87.1%) +o
og1.:、パルプ排水をシーライム法で処理して得た
スラッジ(固形分22゜2%、有機物=8.2%、 M
gO:4.5%、 CaO:1.3%)を15g加えて
混合し、空気の供給を制限しながら炉中で720℃で1
時間保持し、酸化マグネシウムを含むごみの炭2]、2
.6g(対固形分収率22.2%、 MgO:0.32
%)を得た。
Example 2 Paper waste (solid content 86. Nishiki) 500g, planer waste (solid content 86.
7.1%) 500g, rice husk (solid content 87.1%) +o
og1. :, Sludge obtained by treating pulp wastewater with the sea lime method (solid content 22.2%, organic matter = 8.2%, M
gO: 4.5%, CaO: 1.3%) was added and mixed, and the mixture was heated at 720 °C in a furnace with limited air supply.
Garbage charcoal containing magnesium oxide held for a period of time 2], 2
.. 6g (solid yield 22.2%, MgO: 0.32
%) was obtained.

実施例3 排煙脱硫硫酸(H,SO4: 151g/U 195m
Qを水で0.9Qに稀釈し、アルミニウムの空缶5.0
gを処理し、処理後水を注加し、硫酸アルミニウムの硫
酸酸性溶液(Al12(SO4)3:31.7g/Q、
H2SO4:2.2g#l)を1..000mD。
Example 3 Flue gas desulfurization sulfuric acid (H, SO4: 151g/U 195m
Dilute Q to 0.9Q with water and add 5.0Q to an empty aluminum can.
After treatment, water was added and a sulfuric acid acidic solution of aluminum sulfate (Al12(SO4) 3:31.7g/Q,
H2SO4: 2.2g #l) 1. .. 000mD.

を得た。I got it.

実施例4 都市下水を活性汚泥法で処理して得た水(BOD:22
0ppm、 N:40ppm、 P2O,:59ppm
)を1.OOOmQ取り、これに実施例1で得られたご
みの炭5.Ogを加え混合撹拌後置液分離し清澄水(B
OD:5ppm、N:0.8ppm)980mlと汚染
物質を吸着したごみの炭(乾燥物中N:0゜8%、 P
2O5:0.2%)を土壌改良剤として収得した。
Example 4 Water obtained by treating urban sewage with activated sludge method (BOD: 22
0ppm, N: 40ppm, P2O,: 59ppm
) to 1. Take OOOmQ and add waste charcoal obtained in Example 1 to it5. After adding Og and stirring, separate the liquid and clear water (B
OD: 5ppm, N: 0.8ppm) 980ml and garbage charcoal that adsorbed pollutants (N: 0°8% in dry matter, P
2O5:0.2%) was obtained as a soil conditioner.

実施例5 尿尿のメタン発酵残液(BOD:4,160ppm)を
活性汚泥処理した液(BOD:140ppm、 N:8
.Oppm、P2O,:1.40ppm)1,000+
nQに対し、実施例3て得た酸化マグネシウムを含むご
みの炭7gを加え混合撹拌後置液分離し、得られた清澄
水(BODニアppm、 P2O,:1.6ppm)の
1゜000m1lに対し実施例4で得た硫酸アルミニウ
ムの硫酸々性溶液  −を加え、生ずる沈澱を濾過し、
中性の清澄水(pH:6.9、COD:2ppm、 N
:0.8ppm、 P2O5:0.5ppm)を960
誰を得るとともに、汚泥物質を吸 着したごみの炭(乾燥物中 N+1.1%、 P、05:1.7%ヲ 土壌改良剤として回収した。
Example 5 Urine methane fermentation residual liquid (BOD: 4,160 ppm) was treated with activated sludge (BOD: 140 ppm, N: 8
.. Oppm, P2O,: 1.40ppm) 1,000+
To nQ, 7 g of garbage charcoal containing magnesium oxide obtained in Example 3 was added, mixed, stirred, and the after-liquid was separated, and added to 1°000 ml of the obtained clear water (BOD near ppm, P2O: 1.6 ppm). To this, add the sulfuric acid solution of aluminum sulfate obtained in Example 4, filter the resulting precipitate,
Neutral clear water (pH: 6.9, COD: 2ppm, N
:0.8ppm, P2O5:0.5ppm) to 960
At the same time, garbage charcoal that adsorbed sludge substances (N+1.1%, P, 05:1.7% in dry matter) was recovered as a soil conditioner.

Claims (5)

【特許請求の範囲】[Claims] (1)有機物を含む固形廃棄物を蒸し焼きにして炭を得
、この炭を排水に接触させた後炭を含むスラッジと浄化
した水とを分離回収し、炭を含むスラッジは肥料又は土
壌改良剤として利用し、二酸化炭素の発生量を減らすこ
とを特徴とする環境汚染物質の総合的処理利用方法。
(1) Solid waste containing organic matter is steamed to obtain charcoal, and after contacting this charcoal with wastewater, the sludge containing charcoal and purified water are separated and collected, and the sludge containing charcoal is used as a fertilizer or soil conditioner. This is a comprehensive treatment and utilization method for environmental pollutants, which is characterized by using them as carbon dioxide and reducing the amount of carbon dioxide generated.
(2)炭に酸化マグネシウムを加えて排水を処理する請
求項1の方法。
(2) The method according to claim 1, wherein the wastewater is treated by adding magnesium oxide to the charcoal.
(3)炭化の際炭酸マグネシウム又はマグネシウムを含
む物質を加えて熱分解し、酸化マグネシウムを含む炭を
得、排水の処理に用いる請求項2の方法。
(3) The method according to claim 2, wherein magnesium carbonate or a substance containing magnesium is added during carbonization and thermally decomposed to obtain charcoal containing magnesium oxide, which is used for treating wastewater.
(4)炭と酸化マグネシウム又は及び酸化カルシウムの
混合物で排水を処理し、得られたアルカリ性の液に硫酸
アルミニウム又は塩化鉄を加えて中和し、生ずる沈殿と
水を分離収得し、沈殿は肥料又はその原料として用いる
請求項2及び3の方法。
(4) Treat wastewater with a mixture of charcoal and magnesium oxide or calcium oxide, neutralize the resulting alkaline liquid by adding aluminum sulfate or iron chloride, separate and collect the resulting precipitate and water, and use the precipitate as fertilizer. or the method according to claims 2 and 3, which is used as a raw material thereof.
(5)アルミニウム屑に排煙脱硫硫酸を反応させて得ら
れる硫酸アルミニウムを用いる請求項4の方法。
(5) The method according to claim 4, wherein aluminum sulfate obtained by reacting aluminum scrap with flue gas desulfurization sulfuric acid is used.
JP2244277A 1990-09-14 1990-09-14 Synthetic treatment and utilization of environmental pollutant Pending JPH04122490A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2244277A JPH04122490A (en) 1990-09-14 1990-09-14 Synthetic treatment and utilization of environmental pollutant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2244277A JPH04122490A (en) 1990-09-14 1990-09-14 Synthetic treatment and utilization of environmental pollutant

Publications (1)

Publication Number Publication Date
JPH04122490A true JPH04122490A (en) 1992-04-22

Family

ID=17116356

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2244277A Pending JPH04122490A (en) 1990-09-14 1990-09-14 Synthetic treatment and utilization of environmental pollutant

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Country Link
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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05192567A (en) * 1991-12-27 1993-08-03 Kunnetsupu Sekkai Kogyo Kk Filter medium and production thereof
JP2002514505A (en) * 1998-05-14 2002-05-21 ヴィルバイト トーマス Method for treating water, soil, sediment and / or silt
JP2007053966A (en) * 2005-08-24 2007-03-08 Jfe Engineering Kk Method for suppressing nitrous oxide emission from soil
US8222182B2 (en) 2003-12-05 2012-07-17 Nisshoku Corporation Anion adsorbing carbon material, as well as manufacturing method and manufacturing facilities for same
CN107470324A (en) * 2017-08-15 2017-12-15 刘联仓 A kind of recycling municipal solid waste processing method
CN111454100A (en) * 2020-03-20 2020-07-28 厦门大学 Preparation method of slow-release phosphate fertilizer
CN111876173A (en) * 2020-07-14 2020-11-03 大连理工大学 Preparation method of iron-containing sludge-based biochar material and application of iron-containing sludge-based biochar material in anaerobic digestion

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05192567A (en) * 1991-12-27 1993-08-03 Kunnetsupu Sekkai Kogyo Kk Filter medium and production thereof
JP2002514505A (en) * 1998-05-14 2002-05-21 ヴィルバイト トーマス Method for treating water, soil, sediment and / or silt
US8222182B2 (en) 2003-12-05 2012-07-17 Nisshoku Corporation Anion adsorbing carbon material, as well as manufacturing method and manufacturing facilities for same
JP2007053966A (en) * 2005-08-24 2007-03-08 Jfe Engineering Kk Method for suppressing nitrous oxide emission from soil
CN107470324A (en) * 2017-08-15 2017-12-15 刘联仓 A kind of recycling municipal solid waste processing method
CN111454100A (en) * 2020-03-20 2020-07-28 厦门大学 Preparation method of slow-release phosphate fertilizer
CN111876173A (en) * 2020-07-14 2020-11-03 大连理工大学 Preparation method of iron-containing sludge-based biochar material and application of iron-containing sludge-based biochar material in anaerobic digestion

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