JPS6135826A - Removal of malodor by activated humic substance - Google Patents

Removal of malodor by activated humic substance

Info

Publication number
JPS6135826A
JPS6135826A JP15696284A JP15696284A JPS6135826A JP S6135826 A JPS6135826 A JP S6135826A JP 15696284 A JP15696284 A JP 15696284A JP 15696284 A JP15696284 A JP 15696284A JP S6135826 A JPS6135826 A JP S6135826A
Authority
JP
Japan
Prior art keywords
humus
malodor
active
humic substance
activated humic
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
JP15696284A
Other languages
Japanese (ja)
Other versions
JPH0432688B2 (en
Inventor
Yusuke Ishida
有甫 石田
Yoshiro Senoo
妹尾 芳郎
Yasunori Kusunoki
楠 泰則
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.)
ENZAIMU KOGYO KK
Tokyu Construction Co Ltd
Original Assignee
ENZAIMU KOGYO KK
Tokyu Construction Co 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 ENZAIMU KOGYO KK, Tokyu Construction Co Ltd filed Critical ENZAIMU KOGYO KK
Priority to JP15696284A priority Critical patent/JPS6135826A/en
Publication of JPS6135826A publication Critical patent/JPS6135826A/en
Publication of JPH0432688B2 publication Critical patent/JPH0432688B2/ja
Granted legal-status Critical Current

Links

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
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Treating Waste Gases (AREA)

Abstract

PURPOSE:To effectively remove malodor by a simple treating process and to enable the regeneration of an additive after use while making it possible to use an activated humic substance as a soil conditioner at last, by contacting a malodor with a liquid activated humic substance before contacting the same with a solid activated humic substance. CONSTITUTION:The malodor from an excretion treatment plant and a fish factory or the malodor 2 at the time of the preparation of org. fertilizer is sent to a first deodorizing tank 3 and contacted with an activated humic substance solution B1, which was prepared by adding allophane clay mineral to an aqueous extract of a powdery activated humic substance, to collect volatile basic components such as NH3 and amines in the malodor. Subsequently, the malodor is sent to a second deodorizing tank 6 and contacted with a first packing layer C prepared by mixing an iron powder, FeSO4 or Fe2(SO4)3 with a solid activated humic substance to adsorb are remove H2S and sulfur-containing volatile components are further passed through a second packing layer D, wherein activated carbon was mixed with an activated humic substance, as a safe measure. Next, the oxidation odor of the activated humic substance is removed by water or an alkali aqueous solution E to be exhausted to the open air.

Description

【発明の詳細な説明】 [発明の目的1 上のJ 分野 本発明は、液状の活性腐植質並びに固形の活性腐植質に
より、し尿処理場や水産加工場等からの悪臭を効果的に
除去する方法に関するものである。
[Detailed Description of the Invention] [Objective of the Invention 1 J Field] The present invention effectively removes bad odors from human waste treatment plants, seafood processing plants, etc. using liquid active humus and solid active humus. It is about the method.

』」へW東 近年、公害関係で地域住民からの苦情件数は悪臭に関す
るものが最も多く、従来の悪臭除去方法には、例えば7
ミン酸ソーグ(石炭系)によるものが開発されている。
”W East In recent years, the number of complaints from local residents related to pollution has been mostly related to bad odors, and conventional methods of removing bad odors include, for example, 7
A product based on minic acid sorg (coal-based) has been developed.

免肛麩詐犬月束3,:t6   i しかし、上記のような従来の方法では、悪臭は除去でき
ても装置のイニシャルコストや運転経費が高くつくだけ
でなく、発生した酸化臭をジア塩素酸カルシウムや塩素
〃ス、又はオゾン等で後処理を必要としていた。
However, even if the above-mentioned conventional methods can remove bad odors, they not only increase the initial cost and operating costs of the equipment, but also eliminate the generated oxidized odors by using diachlorine. Post-treatment with calcium acid, chlorine, ozone, etc. was required.

本発明は、上記従来の欠点を解消するためになされたも
ので、その目的とするところは、処理工程が簡単なぽか
りでなく、使用後の添加剤の再生が可能で、最終的には
土壌改良・剤として使用できる活性腐植質を利用した悪
臭除去方法を提供するにある。
The present invention was made to eliminate the above-mentioned conventional drawbacks, and its purpose is to not only simplify the processing process but also to enable the regeneration of additives after use, and ultimately to An object of the present invention is to provide a method for removing bad odors using active humus that can be used as a soil improvement agent.

[発明の構成J ・1版嘉支邂海: t 6 r: dη硼[欠本発明は
、し尿処理場又は水産加工場からの臭気、並びに魚骨及
び内臓、大豆粕及び澱粉質相等による有機性肥料製造時
の臭気を液状の活性腐植質に接触せしめて、その中のア
ンモニア及びアミン類等の揮発性塩基成分を捕捉し、続
いて固形の活性腐植質により硫化水素及び含流揮発性成
分を吸着せしめて悪臭を除去するようにしたことを特徴
とするものであり、上記液状の活性腐植質は、動植物の
遺体より形成された天然腐植質及び/又は石炭系鉱物(
石炭、褐炭、亜炭、草炭等)の酸化分解物のうち水抽出
液のpHが4.0以下で酸化電位が(+’)150より
酸化型のヒューミン、7ルボ酸、腐植酸及び粘土鉱物を
主体とした混合物の人工腐植質の0.3〜70%水抽出
液に、アロ7ヱン質の粘土鉱物を0.3%以上添加した
もの、又は粘土鉱物に富む腐植質(水分50%)を3%
以上添加したものであり、また上記固形の活性腐植質は
、上記天然腐植質及び/又は人工腐植質に100〜30
0ノ・ノシュの鉄粉又は硫酸弟1若しくは第2鉄の粉体
を重量比で1()%以上混合し、ペレット状、球状又は
押出成形、並びにグラスウール等の支持体と混合又は積
層してハニカム又はボーラスな板状に成形し、その表面
に2価の酸化鉄を生成させたものである。
[Structure of the Invention J - 1st edition Kashiyenkai: t 6 r: dη 硼 [lack] The present invention is directed to odor from human waste processing plants or fisheries processing plants, and organic odors caused by fish bones and internal organs, soybean meal, starchy phase, etc. The odor from the production of natural fertilizer is brought into contact with liquid activated humus to capture volatile base components such as ammonia and amines, and then hydrogen sulfide and volatile components contained in solid activated humus are removed. The liquid active humus is made of natural humus formed from the remains of animals and plants and/or coal-based minerals (
Among the oxidized decomposition products of coal, lignite, lignite, grass coal, etc.), the pH of the aqueous extract is 4.0 or less and the oxidation potential is (+') 150. A 0.3 to 70% aqueous extract of artificial humus, which is the main mixture, with 0.3% or more of allo-7-based clay minerals added, or a humus rich in clay minerals (50% moisture) 3%
The above-mentioned solid active humus is added to the above-mentioned natural humus and/or artificial humus in an amount of 100 to 30%.
Mix 1% or more of iron powder or ferric sulfate powder or ferric sulfate powder at a weight ratio of 1% or more, form pellets, spheres, or extrusion molding, and mix or laminate with a support such as glass wool. It is formed into a honeycomb or bolus plate shape and has divalent iron oxide produced on its surface.

更に、本発明は、上記液状の活性腐植質と固形の活性腐
植質との間に、第2の液状活性腐植質の槽をもうけてこ
れに悪臭を接触せしめて、その中 、の酪酸、プロピオ
ン等の揮発性低級脂肪酸を除去しせしめるようにしたも
のであり、この第2の液状活性腐植質は、上記天然腐植
質及び/又は人工腐植質を約30%使用した0.5%規
定の苛性ソーダ溶液に、硫酸第1若しくは第2鉄及びゼ
オライトを各々5%以上添加し、空気を挿入して活性腐
植質の紙分T一量重合体及び水酸化第1若しくはfjS
2鉄混合溶液であることを特徴とするものである。
Furthermore, the present invention provides a second tank of liquid active humus between the liquid active humus and the solid active humus, and brings the bad odor into contact with the second liquid active humus. This second liquid active humus is made of 0.5% normal caustic soda containing about 30% of the above natural humus and/or artificial humus. Add 5% or more of each of ferrous or ferric sulfate and zeolite to the solution, and add air to the solution to form an active humus paper T monopolymer and hydroxide or fjS.
It is characterized by being a diiron mixed solution.

実』[側御 以下、本発明をその実施例について図面を参照しながら
説明する。
Preferred embodiments of the present invention will now be described with reference to the drawings.

第1図は本発明方法を実施する脱臭設備の一実施例を示
すものであって、1はし尿処理装置2からの悪臭を吸引
し第1脱臭槽3へ送気するブロアーである。該第1脱果
槽3にはポンプ4により活性腐植質溶液B1が循環供給
されている。
FIG. 1 shows an embodiment of deodorizing equipment for carrying out the method of the present invention, in which 1 is a blower that sucks bad odor from a human waste treatment device 2 and sends air to a first deodorizing tank 3. An active humus solution B1 is circulated and supplied to the first dehulling tank 3 by a pump 4.

該活性腐植質溶液B1は、粉状の活性腐植質の0.3〜
70%の水抽出液に、アロフェン質の粘土鉱物(以下単
に粘土鉱物と言う)を0.3%以上添加したものか、又
は上記粘土鉱物に富む活性腐植質(水分50%)を3%
以上加えたものである。
The active humus solution B1 contains powdery active humus of 0.3 to
70% aqueous extract with 0.3% or more of allophane clay minerals (hereinafter simply referred to as clay minerals), or 3% of active humus rich in the above clay minerals (50% moisture).
This is what has been added above.

上記第1脱臭槽3の活性腐植質溶液B1中に送気された
悪臭は、シャワー5に曝されなから°該活性腐植質溶液
B1と接触1てその中のアンモニア及びアミン類等の揮
発性塩基性成分を活性腐植質、アンモニウム又はアミン
等の複合体として捕捉される。
The bad odor blown into the active humus solution B1 of the first deodorizing tank 3 is not exposed to the shower 5, so that it comes into contact with the active humus solution B1 and is exposed to volatile substances such as ammonia and amines therein. Basic components are captured as complexes such as active humus, ammonium or amines.

上記第1脱臭WI3を出た悪臭は、続いて固形の活性腐
植質が充填されている第2脱臭槽6に送られる。該固形
の活性腐植質は、活性腐植質及び混和剤を直径、長さと
も3〜1016111のペレット状、直径3 ・= 1
0 mll1f)球状又は直径3−10mmで長さ3〜
1ocusの押出形、並びにグラスウール等の支持体と
混合又は積層してハニカム、ポーラスな板状に成型した
ものであり、その組成としては、第1光JRMcに於い
ては、活性腐植質を成型する前又は成型後に100〜3
00メツシユの鉄粉又は硫酸第1若しくは第2鉄の粉体
を重量比で10%以上混合し、表面に2価の酸化鉄をま
ぶして生成したものであり、また第2充填層りに於いて
は、活性腐植質を成型する前又は成型後に重量比で0゜
5%以上の100〜300メツシユの活性炭を混合した
ものである。
The malodor leaving the first deodorizing WI3 is then sent to the second deodorizing tank 6 filled with solid active humus. The solid active humus is made of active humus and an admixture in the form of pellets with a diameter and length of 3 to 1016111, with a diameter of 3.=1.
0ml1f) Spherical or 3-10mm in diameter and 3-10mm in length
1 ocus, or mixed or laminated with a support such as glass wool to form a honeycomb or porous plate shape.As for its composition, Daiichi Hikari JRMc molds active humus. 100-3 before or after molding
It is produced by mixing 00 mesh iron powder or ferrous or ferric sulfate powder at a weight ratio of 10% or more, and sprinkling divalent iron oxide on the surface. In this case, 100 to 300 meshes of activated carbon with a weight ratio of 0.5% or more is mixed before or after molding the activated humus.

従って、第2脱臭槽6に入った悪臭は、まず第1充填層
Cを通過する際に硫化水素及び含硫揮発性成分を吸着さ
れ、硫酸まで酸化して除去される。
Therefore, when the bad odor entering the second deodorizing tank 6 first passes through the first packed bed C, hydrogen sulfide and sulfur-containing volatile components are adsorbed, and the odor is oxidized to sulfuric acid and removed.

尚、第2充填層りはゝ安全措置として設けられているも
のである。
Note that the second filling layer is provided as a safety measure.

上記1jS2充填屑りがら出た悪臭の処理〃スは、ポン
プ7により循環される水又は1%のアルカリ性水溶液E
により、活性腐植質の酸化臭を除去されて大気中に排気
される。
The above-mentioned 1j treatment of the foul odor generated from the S2 filling debris is carried out using water circulated by the pump 7 or a 1% alkaline aqueous solution E.
This removes the oxidized odor of the active humus and exhausts it into the atmosphere.

第2図は、本発明の第2の方法を実施する脱臭設備の一
実施例を示すものであって、上記第1図に示す設備と異
なるところは、上記第1脱臭槽3と第2脱臭@6の間に
第3脱臭WI8を設けた点にある。該第3脱奥槽8には
ポンプ9により活性腐植質溶液B2が循環供給されてい
る。該活性腐植質溶液B2は、上記粉状の活性腐植質3
0%を使用゛した0、5%規定の苛性ソーダ溶液に硫酸
!51若しくは第2鉄及びゼオライトを各々5%以上添
加し、空気を押入して、活性゛腐植質の低分子パ蹴重合
体及び水酸化l若しくはfjS2鉄混合液としたもので
ある。
FIG. 2 shows an embodiment of deodorizing equipment for implementing the second method of the present invention, and the difference from the equipment shown in FIG. 1 is that the first deodorizing tank 3 and the second deodorizing tank The point is that the third deodorizing WI8 is provided between @6. An active humus solution B2 is circulated and supplied to the third depth removal tank 8 by a pump 9. The active humus solution B2 contains the powdered active humus 3.
Sulfuric acid in 0.5% caustic soda solution using 0%! 51 or ferric iron and zeolite are added in an amount of 5% or more each, and air is forced into the mixture to obtain a mixture of active humic low molecular weight polymer and hydroxide l or fjS2 iron.

第1脱臭1/g!3を出た悪臭は、上記第3脱臭槽8の
活性腐植質溶液B2中に送気されてシャワー1゜に曝さ
れながらこれと接触してその中の酪酸、プロピオン酸等
の揮発性低級脂肪酸が吸着除去され、次の第2脱臭槽6
に送られる。
First deodorization 1/g! The foul odor emitted from the 3 is removed by air being blown into the active humus solution B2 in the third deodorizing tank 8, exposed to a 1° shower, and comes into contact with the active humus solution B2, where volatile lower fatty acids such as butyric acid and propionic acid are removed. is adsorbed and removed, and the next second deodorizing tank 6
sent to.

1敗又−効〜朱犬」目明 i)シ尿処理場における臭気除去例 a、運転条件 臭気〃入流量:吸引ブロワ−100J! /min。1 loss again - effect ~ Shuinu” Mei i) Example of odor removal at a human waste treatment plant a. Operating conditions Odor input flow rate: Suction blower - 100J! /min.

吐出側60.1! /1Ilin 、活性腐植質溶液B、:10%以上腐植質水抽出液80
0Kj!に粘度鉱物を5kg以 上添加した溶液を充填した。
Discharge side 60.1! /1Ilin, active humus solution B,: 10% or more humus water extract 80
0Kj! was filled with a solution containing 5 kg or more of clay mineral.

第1光填層C:  腐植質粉体に5%の苛性ソーダを加
えたペレット360 kgに鉄粉1%以上を混合し たものを充填した。
First optical filling layer C: 360 kg of pellets made by adding 5% caustic soda to humic powder were filled with a mixture of 1% or more iron powder.

第2光槙層D:  腐植質ペレッ) 380kgに1%
以上の活性炭を混合、付 着させ充填した。
2nd light layer D: humus pellet) 1% per 380kg
The above activated carbon was mixed, adhered, and filled.

ii)水産加工場(フィツシュミール及び有機性肥料製
造工場) a、運転条件 臭気〃入流量:吸引ブロワー3001/論in。
ii) Fisheries processing plant (fish meal and organic fertilizer manufacturing plant) a. Operating conditions Odor Input flow rate: Suction blower 3001/in.

吐出111100ffi /1lIin活性腐植質溶液
B、:10%以上腐植質水抽出液400klに粘土鉱物
を5kg以上を 添加した溶液を充填した。
Discharge 111100ffi/1lIin Active humus solution B: Filled with a solution in which 5 kg or more of clay mineral was added to 400 kl of a 10% or more humus aqueous extract.

活性腐植質溶液B2:10%以上腐植質の0.5%規定
苛性ソーグ抽出物400klに硫 酸第1鉄及びゼオライト各5 kg以上を溶解し充填した。
Active humus solution B2: 5 kg or more each of ferrous sulfate and zeolite were dissolved and filled in 400 kl of 0.5% normal caustic sorg extract containing 10% or more humus.

第1充填層C:  腐植質粉体に5%苛性ソーダを加え
たベレットを60kgに鉄 粉1%以上を混合したものを 充填した。
First packed bed C: 60 kg of pellets prepared by adding 5% caustic soda to humic powder were filled with a mixture of 1% or more iron powder.

第2充填層D=  腐植質ペレッ) 380kgに1%
、以上の活性炭を混合し付着さ せ充填した。
2nd packed layer D = humic pellets) 1% to 380 kg
The above activated carbons were mixed, adhered, and filled.

■ づ 痙 [発明の効果1 以上のように本発明によれば、アロフェン質の粘土鉱物
により、活性腐植質の酸化力を°′弱め、揮  ・発性
含硫成分の過激な酸化による酸化臭の発生を防ぎ、従来
のような以後の脱臭工程における塩素系、オゾン又は過
マンガン酸カリ等の工程を不要にし得る。
■ Effect of the invention 1 As described above, according to the present invention, allophane clay minerals weaken the oxidizing power of active humus and reduce oxidative odor due to radical oxidation of volatile sulfur-containing components. The generation of chlorine, ozone, potassium permanganate, etc. in the conventional deodorizing process can be made unnecessary.

また本発明によれば、処理工程が簡単な°ばかりでな(
、使用後の添加剤の再生が可能で、最終的には土壌改良
剤として使用で軽る効果がある。
Furthermore, according to the present invention, the processing steps are not only simple (
It is possible to regenerate the additive after use, and the final use as a soil conditioner has a lightening effect.

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

第1図は本発明の第1の方法を実施する悪臭除去設備の
概略説明図、第2図は第2の方法を実施する設備の概略
説明図である。 1・・・ブロアー、2・・・し尿処理装置、3・・・第
1脱臭槽、4・・・ポンプ、5・・・シャワー、6・・
・第2脱臭槽、7・・・ポンプ、8・・・第3脱奥槽、
9・・・ポンプ、10・・・シャワー、B、、B、・・
・活性腐植質溶液、C・・・第1充填層、D・・・第2
充填層、E・・・水溶液。
FIG. 1 is a schematic explanatory diagram of malodor removal equipment for implementing the first method of the present invention, and FIG. 2 is a schematic explanatory diagram of equipment for implementing the second method. 1... Blower, 2... Human waste processing device, 3... First deodorizing tank, 4... Pump, 5... Shower, 6...
・Second deodorizing tank, 7... pump, 8... third deodorizing tank,
9...pump, 10...shower, B,,B,...
・Active humus solution, C...first packed layer, D...second
Filled bed, E...aqueous solution.

Claims (5)

【特許請求の範囲】[Claims] (1)し尿処理場又は水産加工場からの臭気、並びに魚
骨及び内臓、大豆粕及び澱粉質粕等による有機性肥料製
造時の臭気を液状の活性腐植質に接触せしめて、その中
のアンモニア及びアミン類等の揮発性塩基成分を捕捉し
、続いて固形の活性腐植質により硫化水素及び含流揮発
性成分を吸着せしめて悪臭を除去するようにしたことを
特徴とする活性腐植質による悪臭除去方法。
(1) Odors from human waste treatment plants or fisheries processing plants, as well as odors from the production of organic fertilizers from fish bones and internal organs, soybean meal, starch meal, etc., are brought into contact with liquid active humus to remove ammonia therein. and volatile base components such as amines, etc. are captured, and then hydrogen sulfide and volatile components contained therein are adsorbed by solid activated humus to remove the malodor. Removal method.
(2)上記液状の活性腐植質が、動植物の遺体より形成
された天然腐植質及び/又は石炭系鉱物の酸化分解物の
うち水抽出液のpHが4.0以下で酸化電位が(+)1
50より酸化型のヒューミン、フルボ酸、腐植酸及び粘
土鉱物を主体とした混合物の人工腐植質の0.3〜70
%水抽出液に、アロフェン質の粘土鉱物を0.3%以上
添加したもの、又は粘土鉱物に富む腐植質(水分50%
)を3%以上添加したものであることを特徴とする前記
特許請求の範囲第1項記載の活性腐植質による悪臭除去
方法。
(2) The above-mentioned liquid active humus has an oxidation potential of (+) when the pH of the aqueous extract of natural humus formed from the remains of animals and plants and/or oxidized decomposition products of coal-based minerals is 4.0 or less. 1
50 to 0.3 to 70 of artificial humus, a mixture mainly composed of oxidized humin, fulvic acid, humic acid, and clay minerals.
% water extract with 0.3% or more of allophane clay minerals added, or humus rich in clay minerals (water 50%).
2. The method for removing bad odors using active humus according to claim 1, characterized in that 3% or more of humus is added to the active humus.
(3)上記固形の活性腐植質が、動植物の遺体より形成
された天然腐植質及び/又は石炭系鉱物の酸化分解物の
うち水抽出液のpHが4.0以下で酸化電位が(+)1
50より酸化型のヒューミン、フルボ酸、腐植酸及び粘
土鉱物を主体とした混合物の人工腐植質に100〜30
0メッシュの鉄粉又は硫酸第1若しくは第2鉄の粉体を
重量比で10%以上混合し、ペレット状、球状又は押出
成形、並びにグラスウール等の支持体と混合又は積層し
てハニカム又はポーラスな板状に成形し、その表面に2
価の酸化鉄を生成させたものであることを特徴とする前
記特許請求の範囲第1項記載の活性腐植質による悪臭除
去方法。
(3) The solid active humus has an oxidation potential of (+) when the pH of the aqueous extract of the natural humus formed from the remains of animals and plants and/or the oxidized decomposition product of coal-based minerals is 4.0 or less. 1
50 to 100 to 30 to artificial humus, a mixture mainly composed of oxidized humin, fulvic acid, humic acid, and clay minerals.
0 mesh iron powder or ferrous or ferric sulfate powder is mixed at a weight ratio of 10% or more and formed into pellets, spheres, or extrusion molding, and mixed or laminated with a support such as glass wool to form a honeycomb or porous shape. Form it into a plate shape and put 2 on the surface.
2. The method for removing malodor using active humus according to claim 1, wherein the activated humus is produced by producing iron oxide having a high valence.
(4)し尿処理場又は水産加工場からの臭気、並びに魚
骨及び内臓、大豆粕及び澱粉質粕等による有機性肥料製
造時の臭気を液状の活性腐植質に接触せしめて、その中
のアンモニア及びアミン類等の揮発性塩基成分を捕捉し
、続く第2の液状活性腐植質に接触せしめて、酪酸、プ
ロピオン等の揮発性低級脂肪酸を除去し、更に固形の活
性腐植質により硫化水素及び含流揮発性成分を吸着せし
めるようにしたことを特徴とする活性腐植質による悪臭
除去方法。
(4) Odors from human waste treatment plants or seafood processing plants, as well as odors from the production of organic fertilizers from fish bones and internal organs, soybean meal, starch meal, etc., are brought into contact with liquid active humus to remove ammonia therein. and volatile base components such as amines are captured, and then brought into contact with a second liquid activated humus to remove volatile lower fatty acids such as butyric acid and propion, and further hydrogen sulfide and other components are removed by the solid activated humus. A method for removing bad odors using active humus, which is characterized by adsorbing volatile components.
(5)上記第2の液状活性腐植質が、動植物の遺体より
形成された天然腐植質及び/又は石炭系鉱物の酸化分解
物のうち水抽出液のpHが4.0以下で酸化電位が(+
)150より酸化型のヒューミン、フルボ酸、腐植酸及
び粘土鉱物を主体とした混合物の人工腐植質を約30%
使用した0.5%規定の苛性ソーダ溶液に、硫酸第1若
しくは第2鉄及び/又はゼオライトを各々5%以上添加
し、空気を挿入して活性腐植質の低分子量重合体及び水
酸化第1若しくは第2鉄混合溶液であることを特徴とす
る前記特許請求の範囲第4項記載の活性腐植質による悪
臭除去方法。
(5) The second liquid active humus has an oxidation potential of ( +
) Approximately 30% artificial humus, a mixture mainly composed of oxidized humin, fulvic acid, humic acid, and clay minerals, from 150
To the 0.5% normal caustic soda solution used, 5% or more of each of ferrous or ferric sulfate and/or zeolite is added, and air is inserted to form a low molecular weight polymer of active humus and ferric or ferric hydroxide. The method for removing malodor using active humus according to claim 4, wherein the method is a ferric mixed solution.
JP15696284A 1984-07-27 1984-07-27 Removal of malodor by activated humic substance Granted JPS6135826A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15696284A JPS6135826A (en) 1984-07-27 1984-07-27 Removal of malodor by activated humic substance

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15696284A JPS6135826A (en) 1984-07-27 1984-07-27 Removal of malodor by activated humic substance

Publications (2)

Publication Number Publication Date
JPS6135826A true JPS6135826A (en) 1986-02-20
JPH0432688B2 JPH0432688B2 (en) 1992-06-01

Family

ID=15639119

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15696284A Granted JPS6135826A (en) 1984-07-27 1984-07-27 Removal of malodor by activated humic substance

Country Status (1)

Country Link
JP (1) JPS6135826A (en)

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2662333A1 (en) * 1990-05-25 1991-11-29 Nat Energy Council AGENT HAVING BACTERIOSTATIC AND BACTERICIDAL ACTIVITY.
US5578114A (en) * 1994-03-04 1996-11-26 Grontmij Advies & Techniek Bv Biological filter provided with a pelletized biologically active compost carrier material and method for the production of a pelletized biologically active compost carrier material
KR20020034123A (en) * 2002-04-04 2002-05-08 서영진 Malodor Removing method of malodor
KR100424157B1 (en) * 2001-08-23 2004-03-30 서희동 Composting method for organic waste substrate by using activated humic substances and humification bacteria
KR100435506B1 (en) * 2002-04-12 2004-06-12 서희동 The artificial manufacturing method of activated humus soil by using zeolite and peat
KR100453560B1 (en) * 2001-08-01 2004-10-20 서희동 Artificial manufacturing method of activated humic substances
KR100463122B1 (en) * 2002-11-11 2004-12-29 서희동 Manufacturing method of magnetic minerals
KR100467118B1 (en) * 2002-10-29 2005-01-24 서희동 Manufacturing method for the pellet of magnetized oceanic humic acid colloidal micelle
KR100469989B1 (en) * 2002-06-20 2005-02-05 서희동 Cultivation and application method of the effective micro-organisms by using oceanic humic acid colloidal micelle and activated minerals
KR100472971B1 (en) * 2002-12-10 2005-03-10 서희동 Treatment method of drinking water for domestic animals
KR100472972B1 (en) * 2002-12-10 2005-03-10 서희동 Treatment method of sewage and waste water
JP2013244450A (en) * 2012-05-25 2013-12-09 Taiheiyo Cement Corp Method for treating waste water containing sulfur component and selenium
JP2015110760A (en) * 2013-10-31 2015-06-18 恭子 柿澤 Composition for cleaning

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Publication number Priority date Publication date Assignee Title
CN108640764A (en) * 2018-07-24 2018-10-12 郑新民 A kind of carbon containing organic fertilizer and production technology having bactericidal effect

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4961062A (en) * 1972-10-16 1974-06-13
JPS5239570A (en) * 1975-09-26 1977-03-26 Betsuku:Kk Process for deodorising malodorous gas

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4961062A (en) * 1972-10-16 1974-06-13
JPS5239570A (en) * 1975-09-26 1977-03-26 Betsuku:Kk Process for deodorising malodorous gas

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2662333A1 (en) * 1990-05-25 1991-11-29 Nat Energy Council AGENT HAVING BACTERIOSTATIC AND BACTERICIDAL ACTIVITY.
US5578114A (en) * 1994-03-04 1996-11-26 Grontmij Advies & Techniek Bv Biological filter provided with a pelletized biologically active compost carrier material and method for the production of a pelletized biologically active compost carrier material
KR100453560B1 (en) * 2001-08-01 2004-10-20 서희동 Artificial manufacturing method of activated humic substances
KR100424157B1 (en) * 2001-08-23 2004-03-30 서희동 Composting method for organic waste substrate by using activated humic substances and humification bacteria
KR20020034123A (en) * 2002-04-04 2002-05-08 서영진 Malodor Removing method of malodor
KR100435506B1 (en) * 2002-04-12 2004-06-12 서희동 The artificial manufacturing method of activated humus soil by using zeolite and peat
KR100469989B1 (en) * 2002-06-20 2005-02-05 서희동 Cultivation and application method of the effective micro-organisms by using oceanic humic acid colloidal micelle and activated minerals
KR100467118B1 (en) * 2002-10-29 2005-01-24 서희동 Manufacturing method for the pellet of magnetized oceanic humic acid colloidal micelle
KR100463122B1 (en) * 2002-11-11 2004-12-29 서희동 Manufacturing method of magnetic minerals
KR100472971B1 (en) * 2002-12-10 2005-03-10 서희동 Treatment method of drinking water for domestic animals
KR100472972B1 (en) * 2002-12-10 2005-03-10 서희동 Treatment method of sewage and waste water
JP2013244450A (en) * 2012-05-25 2013-12-09 Taiheiyo Cement Corp Method for treating waste water containing sulfur component and selenium
JP2015110760A (en) * 2013-10-31 2015-06-18 恭子 柿澤 Composition for cleaning

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