JP2945402B2 - Sludge deodorant - Google Patents
Sludge deodorantInfo
- Publication number
- JP2945402B2 JP2945402B2 JP63334860A JP33486088A JP2945402B2 JP 2945402 B2 JP2945402 B2 JP 2945402B2 JP 63334860 A JP63334860 A JP 63334860A JP 33486088 A JP33486088 A JP 33486088A JP 2945402 B2 JP2945402 B2 JP 2945402B2
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- deodorant
- odor
- added
- deodorizing
- 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
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は下水、し尿処理場、有機性産業排水等の有機
質汚泥から発生する悪臭除去用の脱臭剤に関する。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a deodorant for removing malodors generated from organic sludge such as sewage, human waste treatment plants, and organic industrial wastewater.
下水、し尿処理場及び有機性産業排水等から生じる有
機質汚泥は高分子凝集剤等を添加してスクリユーデカン
ター、ベルトプレス等で脱水する処理方法が行われてい
る。脱水処理されたケーキは焼却、及び埋め立て等によ
り処分される。しかし、有機質汚泥は溶存酸素がなくな
ると腐敗が始まり硫化水素、メチルメルカプタン等の硫
化物系の悪臭ガスを発生する。とりわけ、硫化水素はそ
の臭気もさることながら人体に対する毒性、機器に対す
る腐食が強く問題である。悪臭ガスの脱臭方法としては
現在次のような方法が用いられている。Organic sludge generated from sewage, human waste treatment plants, organic industrial wastewater, and the like is treated by adding a polymer flocculant or the like and dehydrating with a screw decanter, a belt press, or the like. The dehydrated cake is disposed of by incineration and landfill. However, when the dissolved oxygen is exhausted, the organic sludge starts to rot and generates sulfide-based malodorous gas such as hydrogen sulfide and methyl mercaptan. In particular, hydrogen sulfide is a serious problem not only because of its odor, but also because of its toxicity to the human body and its corrosion to equipment. The following methods are currently used as a method for deodorizing odorous gas.
(1) 酸、アルカリ等を用いる薬品洗浄法。(1) Chemical cleaning method using acid, alkali and the like.
(2) 活性炭、イオン交換樹脂を用いる吸着法。(2) Adsorption method using activated carbon and ion exchange resin.
(3) 直接燃焼法、触媒燃焼法等の燃焼法。(3) Combustion methods such as direct combustion method and catalytic combustion method.
(4) 酸化剤等を用いる薬品添加法。(4) A chemical addition method using an oxidizing agent or the like.
これらのうち(1)〜(3)の方法は高濃度臭気の処
理に適した方法であるが臭気をダクトで吸引収集して処
理装置に送る必要があることと脱水機周辺等が開放的で
ありまた容積も広いことからあまり効率的な方法といい
い難い。これに対し薬品添加法は汚泥中に薬品を添加す
るだけでよく、脱水機周辺等の脱臭に適した方法であ
る。Of these methods, methods (1) to (3) are suitable for treating high-concentration odors. However, it is necessary to collect the odors by a duct and send them to a processing device, and the area around the dehydrator is open. It is difficult to call it a very efficient method because of its large volume. On the other hand, the chemical addition method only needs to add a chemical to the sludge, and is a method suitable for deodorizing around the dehydrator.
しかし、従来の薬品添加法では添加した瞬間は効果が
あるが脱臭効果の持続性が乏しく、汚泥貯槽、脱水機、
脱水ケーキホツパー、トラツク搬出、埋め立て等の各工
程において効果的に脱臭することはできなかつた。又、
持続性が乏しいことから脱臭効果も不安性であり、コス
トも高くなつている。このため脱臭(消臭)剤として種
々の薬品及び処理方法が提案されており、例えば、L−
アスコルビン酸と2価の鉄化合物からなる物(特公昭61
−43091号公報)亜鉛化合物を用いる方法(特開昭63−2
05197号公報)、亜鉛と3価の鉄を主成分とする脱臭剤
(特開昭63−205198号公報)、アスコルビン酸またはエ
リソルビン酸と水溶性第二銅とを含有する化合物(特開
昭63−147543号公報)、次亜塩素酸塩と金属化合物を粒
状物に含浸させた化合物(特開昭63−178846号公報)が
知られている。However, the conventional chemical addition method is effective at the moment of addition, but the persistence of the deodorizing effect is poor, and sludge storage tanks, dehydrators,
In each process such as dewatering cake hopper, truck carry-out and landfill, deodorization could not be performed effectively. or,
Due to poor sustainability, the deodorizing effect is uneasy, and the cost is increasing. For this reason, various chemicals and treatment methods have been proposed as deodorizing (deodorizing) agents.
A substance consisting of ascorbic acid and a divalent iron compound (Japanese Patent Publication No. 61
No. 43091) A method using a zinc compound (JP-A-63-2)
05197), a deodorant containing zinc and trivalent iron as main components (JP-A-63-205198), and a compound containing ascorbic acid or erythorbic acid and water-soluble cupric acid (JP-A-63-195198). JP-A-147543) and a compound in which a hypochlorite and a metal compound are impregnated into a granular material (JP-A-63-178846) are known.
しかし提案されているいずれの方法も添加直後は効果
があるものの持続性が不充分である。又、特開昭63−17
8846号に記載された次亜塩素酸塩と金属化合物を水溶液
として混合すると次亜塩素酸塩の分解や金属水酸化物の
析出が起こるので、このような組合せからなるものは水
溶液として使用することができないものである。However, all of the proposed methods are effective immediately after the addition but have insufficient sustainability. Also, JP-A-63-17
Mixing hypochlorite and metal compounds described in No. 8846 as an aqueous solution will cause decomposition of hypochlorite and precipitation of metal hydroxide, so use such a combination as an aqueous solution. Is something that cannot be done.
本発明の目的は汚泥に対する添加が容易で持続性の優
れた汚泥脱臭剤を提供することにある。An object of the present invention is to provide a sludge deodorant which can be easily added to sludge and has excellent durability.
本発明の要旨は、水溶性亜鉛化合物、有機系水溶性腐
敗防止剤及び水からなる汚泥脱臭剤にある。The gist of the present invention resides in a sludge deodorant comprising a water-soluble zinc compound, an organic water-soluble rot inhibitor and water.
本発明において処理対象となる汚泥は高BOD排水の生
物処理等から発生する有機質汚泥であり、その例として
は下水・し尿処理場から発生する汚泥、食品工業、化学
工業等から発生する汚泥等を挙げることができる。Sludge to be treated in the present invention is organic sludge generated from biological treatment of high BOD wastewater, and examples thereof include sludge generated from sewage and human waste treatment plants, sludge generated from food industry, chemical industry, and the like. Can be mentioned.
本発明において汚泥脱臭剤の構成成分である水溶性亜
鉛化合物としては、酢酸亜鉛等の塩、塩化亜鉛等の塩化
物を挙げることができる。In the present invention, examples of the water-soluble zinc compound, which is a component of the sludge deodorant, include salts such as zinc acetate and chlorides such as zinc chloride.
又、有機系水溶性腐敗防止剤としては1,3,5−トリス
(βオキシエチル)ヘキサヒドロトリアジン等のトリア
ジン系化合物や有機酸の金属塩等で代表される工業用腐
敗防止剤、安息香酸、サリチル酸、デヒドロ酢酸、パラ
ヒドロキシ安息香酸の塩等で代表される食品用腐敗防止
剤あるいは塩化ベンザルコニウム、ベンジルアルコール
等で代表される医薬用腐敗防止剤として使用されている
ものであつて、水溶性のものを挙げることができる。Examples of the organic water-soluble rust preventive include triazine-based compounds such as 1,3,5-tris (β-oxyethyl) hexahydrotriazine and industrial rust preventives represented by metal salts of organic acids, benzoic acid, and the like. It is used as an antiseptic for foods represented by salicylic acid, dehydroacetic acid, salts of parahydroxybenzoic acid, etc. or as a pharmaceutical antiseptic represented by benzalkonium chloride, benzyl alcohol, etc. Can be mentioned.
本発明の汚泥脱臭剤において水溶性亜鉛化合物(A)
と有機系腐敗防止剤(B)の組成比A/Bは特に限定され
ないが、通常は99/1〜1/99(重量部)程度の範囲にあれ
ばよく、90/10〜50/50(重量部)の範囲にあることがよ
り好ましい。Water-soluble zinc compound (A) in the sludge deodorant of the present invention
The composition ratio A / B of the organic rot antioxidant (B) is not particularly limited, but usually may be in the range of about 99/1 to 1/99 (parts by weight), and may be 90/10 to 50/50 ( (Parts by weight) is more preferable.
又、水溶性亜鉛化合物と有機系腐敗防止剤(以下これ
らを合わせて「有効成分」という)と水との組成比も特
に限定されないが、汚泥脱臭剤中の有効成分の量はおよ
そ5〜60重量%程度であることが好ましい。Further, the composition ratio of the water-soluble zinc compound, the organic anti-rotting agent (hereinafter collectively referred to as “active ingredient”) and water is not particularly limited, but the amount of the active ingredient in the sludge deodorant is about 5 to 60. It is preferable that the amount is about% by weight.
このようなブレンド物からなる本発明の汚泥脱臭剤が
汚泥の脱臭に有効な理由は定かではないが、主に水溶性
亜鉛化合物が硫化水素等の既に生成した悪臭成分と反応
してこれを除去し、有機系腐敗防止剤が悪臭ガスの生成
を防止していると考えられる。It is not clear why the sludge deodorant of the present invention comprising such a blend is effective for deodorizing sludge, but mainly a water-soluble zinc compound reacts with already generated malodorous components such as hydrogen sulfide to remove this. However, it is considered that the organic putrefaction inhibitor prevents the generation of offensive odor gas.
次にこの汚泥脱臭剤の使用方法について説明する。 Next, a method of using the sludge deodorant will be described.
本発明の汚泥脱臭剤を使用するに際しその添加時期や
場所は特に限定されないが、脱臭効果を高めるためには
汚泥の腐敗が進行する以前の段階であることが好まし
い。従つて、通常は汚泥貯槽に汚泥を投入する時とほぼ
同時に添加されるが、汚泥脱臭剤単独で添加してもよく
高分子凝集剤溶液に混合した状態で添加してもよい。ま
た腐敗が激しい場合等は必要に応じて汚泥貯槽以前にあ
る汚泥濃縮槽に添加してもよい。尚、汚泥脱臭剤添加後
の反応時間は特に考慮しなくてよい。When the sludge deodorant of the present invention is used, the timing and place for adding the sludge deodorant are not particularly limited. However, in order to enhance the deodorizing effect, the sludge deodorant is preferably at a stage before the decay of the sludge proceeds. Therefore, the sludge is usually added almost simultaneously with the sludge being charged into the sludge storage tank. However, the sludge deodorant may be added alone or may be added in a state of being mixed with the polymer flocculant solution. If the decay is severe, the sludge may be added to a sludge thickening tank provided before the sludge storage tank, if necessary. The reaction time after the addition of the sludge deodorant does not need to be particularly considered.
以下に実施例により本発明を具体的に説明する。尚、
実施例において脱臭剤の添加量は汚泥に対する重量比で
ある。Hereinafter, the present invention will be described specifically with reference to Examples. still,
In the examples, the amount of the deodorant added is a weight ratio to the sludge.
実施例1〜9,比較例1,2 pH;5.4、SS;2.05%、灼熱減量(以下「VTS」とい
う);67.5%、M−アルカリ度;900mg/なる性状の下水
混合生汚泥を500ml用ポリ瓶に300ml採取した。次に第1
表に示す組成と量の脱臭剤を添加し10回振とう後、気相
の悪臭ガス濃度をガス検知管にて測定し、悪臭の主成分
である硫化水素が検出限界以下になる添加量を求めた。Examples 1 to 9, Comparative Examples 1, 2 pH; 5.4, SS; 2.05%, loss on ignition (hereinafter referred to as "VTS"); 67.5%, M-alkalinity; 300 ml was collected in a poly bottle. Then the first
After adding the deodorant of the composition and amount shown in the table and shaking 10 times, measure the concentration of gaseous odor gas with a gas detector tube, and determine the amount of hydrogen sulfide that is the main component of odor below the detection limit. I asked.
この量を脱臭剤の添加量としてポリ瓶中の汚泥をその
まま密封保存し5日後まで脱臭効果の持続性を測定し
た。いずれの場合も汚泥に対する脱臭の持続効果は大変
良好であつた。ただし、比較例1及び2では、硫化水素
が検出限界以下になる添加量が多くを要した。Using this amount as the amount of deodorant added, the sludge in the plastic bottle was sealed and stored as it was, and the persistence of the deodorizing effect was measured until 5 days later. In each case, the sustained effect of deodorization on sludge was very good. However, Comparative Examples 1 and 2 required a large amount of hydrogen sulfide to be below the detection limit.
比較例3 脱臭剤を添加せず、その他の条件は実施例1と同様に
して臭気を測定した。その結果、日をおつて硫化水素、
メチルメルカプタンの量が著しく増加し、非常に悪臭を
放つ状態となつた。Comparative Example 3 The odor was measured in the same manner as in Example 1 except that no deodorant was added. As a result, hydrogen sulfide,
The amount of methyl mercaptan increased significantly, leading to a very foul odor.
比較例4〜12 脱臭剤として第1表の酸化剤又は金属塩を添加し、そ
の他の条件は実施例1と同様にして臭気を測定した。そ
の結果、添加直後は硫化水素、メチルメルカプタンが除
去され脱臭効果があつたが、経日的に悪臭ガスが著しく
増加し薬品無添加の場合と同様に多様の臭気成分が検出
された。Comparative Examples 4 to 12 As the deodorizing agents, the oxidizing agents or metal salts shown in Table 1 were added, and the odor was measured in the other conditions as in Example 1. As a result, immediately after the addition, hydrogen sulfide and methyl mercaptan were removed and the deodorizing effect was obtained. However, the odorous gas increased remarkably over time, and various odor components were detected as in the case where no chemical was added.
実施例10〜18,比較例13,14 実施例1と同様の汚泥を500ml用のビーカーに300ml採
取し、各脱臭剤を硫化水素が検出限界以下になる量まで
添加し1分間スパチユラにて混合した。次に、高分子凝
集剤ダイヤフロツクKP−201G(ダイヤフロツク株式会社
製、ジメチルアミノメタクリレート4級塩ホモポリマ
ー、分子量300万)を汚泥に対して150ppm添加して1分
間スパチユラにて撹拌混合してフロツクを生成させ、ベ
ルトプレス型脱水機により脱水した。Examples 10 to 18, Comparative Examples 13 and 14 300 ml of the same sludge as in Example 1 was collected in a 500 ml beaker, and each deodorant was added until the amount of hydrogen sulfide became below the detection limit, and mixed for 1 minute with a spatula. did. Next, a polymer flocculant Diafloc KP-201G (manufactured by Diafloc Co., Ltd., dimethylaminomethacrylate quaternary salt homopolymer, molecular weight 3,000,000) was added to sludge at 150 ppm, and the mixture was stirred and mixed with a spatula for 1 minute to remove the floc. It was formed and dehydrated by a belt press type dehydrator.
得られたケーキを250ml用のポリ瓶中に密封保存し経
時的に悪臭ガス濃度を測定し脱臭の持続効果を評価した
ところ、いずれの場合も脱水ケーキの脱臭持続効果は大
変良好であつた。The obtained cake was sealed and stored in a 250 ml plastic bottle, and the odor gas concentration was measured over time to evaluate the sustained effect of deodorization.
比較例13、14では、硫化水素が検出限界以下になる添
加量が多くを要し、しかもケーキの硫化水素発生量が経
時的に増大した。In Comparative Examples 13 and 14, a large amount of hydrogen sulfide was required to be below the detection limit, and the amount of hydrogen sulfide generated in the cake increased over time.
比較例15 薬品を添加せず、その他の条件は実施例10と全く同様
にしたところ、脱水直後はケーキの臭気が弱かつたが経
時的に悪臭ガスが発生し非常に臭くなつた。Comparative Example 15 When no other chemical was added and the other conditions were exactly the same as those in Example 10, the odor of the cake was weak immediately after dehydration, but the odorous gas was generated over time and became very odorous.
比較例16〜24 脱臭剤として第2表の酸化剤又は金属塩を添加し、そ
の他の条件は実施例12と同様にした。その結果、脱水直
後はケーキの臭気は弱かつたが経時的に悪臭ガスが発生
して非常に臭くなり臭気は薬品無添加の場合と殆ど同じ
であつた。Comparative Examples 16 to 24 The oxidizing agents or metal salts shown in Table 2 were added as deodorants, and the other conditions were the same as in Example 12. As a result, immediately after the dehydration, the odor of the cake was weak, but the odor gas was generated over time and became very odorous, and the odor was almost the same as in the case where no chemical was added.
実施例19 第1図のような下水の汚泥処理施設において脱臭剤の
試験を実施した。汚泥の性状はSS1.86%、pH5.4、VTS7
2.4%であつた。脱臭剤は汚泥貯槽に所定量投入し30分
間撹拌機で混合した。脱水機としては月島機械株式会社
製のベルトプレス型脱水機を用い、汚泥脱水用高分子凝
集剤としてはダイヤフロツクKP−201Gを使用した。Example 19 A test of a deodorant was carried out in a sewage sludge treatment facility as shown in FIG. Sludge properties are SS1.86%, pH5.4, VTS7
It was 2.4%. A predetermined amount of the deodorant was put into the sludge storage tank and mixed with a stirrer for 30 minutes. A belt press type dehydrator manufactured by Tsukishima Kikai Co., Ltd. was used as a dehydrator, and Diafloc KP-201G was used as a polymer flocculant for sludge dehydration.
その結果を第3表に示したが、汚泥貯槽から脱水ケー
キホツパーまでの脱臭状態は良好であつた。汚泥貯槽に
残留した汚泥を翌日に脱水しても脱臭効果が持続してい
た。又、2日後のケーキ搬出作業においてもケーキから
は悪臭ガスが発生しなかつた。このような本発明の汚泥
脱臭剤は持続効果が大変良好であり脱水機回り全体の臭
気の発生を防止できた。The results are shown in Table 3, and the deodorized state from the sludge storage tank to the dewatered cake hopper was good. Even if the sludge remaining in the sludge storage tank was dehydrated the next day, the deodorizing effect was maintained. Further, no odorous gas was generated from the cake even in the cake unloading operation two days later. Such a sludge deodorant of the present invention has a very good sustaining effect, and can prevent generation of odor around the dehydrator.
比較例25及26 脱臭剤として酸化剤、及び金属塩を単独に使用し、そ
の他の条件は実施例19と同様にして実施し、結果を第3
表に示した。脱水開始2時間迄は汚泥貯槽や脱水機内等
において悪臭の発生はなかつたが、その後は悪臭が発生
し臭くなつてきた。Comparative Examples 25 and 26 An oxidizing agent and a metal salt were used alone as a deodorizing agent, and the other conditions were carried out in the same manner as in Example 19.
It is shown in the table. Until 2 hours after the start of dehydration, no odor was generated in the sludge storage tank or dehydrator, but after that, a bad odor was generated and became odorous.
また、ケーキホツパーの脱臭はできなかつた。汚泥貯
槽に残留した汚泥を翌日に脱水した際には脱臭効果がな
くなつており、高濃度の硫化水素、メチルメルカプタン
が発生した。また2日後のケーキ搬出においてはケーキ
からの悪臭ガスが充満し、非常に高濃度の硫化水素、メ
チルメルカプタンを検出した。Also, the cake hopper could not be deodorized. When the sludge remaining in the sludge storage tank was dehydrated the next day, the deodorizing effect was lost, and high concentrations of hydrogen sulfide and methyl mercaptan were generated. Two days later, when the cake was discharged, the odorous gas from the cake was filled, and very high concentrations of hydrogen sulfide and methyl mercaptan were detected.
〔発明の効果〕 本発明の汚泥脱臭剤は脱臭効果の持続性が高く、本剤
を汚泥に添加しておくだけで汚泥の脱水設備全体の脱臭
が可能であり、著しく環境を改善することができる。 [Effect of the Invention] The sludge deodorizing agent of the present invention has a high persistence of the deodorizing effect, and it is possible to deodorize the entire sludge dewatering equipment only by adding the present agent to the sludge, thereby significantly improving the environment. it can.
第1図は下水処理場のフローシートであり、点線内が汚
泥脱水処理施設である。FIG. 1 is a flow sheet of a sewage treatment plant, and a dotted line indicates a sludge dewatering facility.
───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.6,DB名) C02F 11/00 - 11/20 B01J 20/22 A61L 9/01 ──────────────────────────────────────────────────続 き Continued on the front page (58) Field surveyed (Int. Cl. 6 , DB name) C02F 11/00-11/20 B01J 20/22 A61L 9/01
Claims (1)
剤及び水からなる汚泥脱臭剤。1. A sludge deodorant comprising a water-soluble zinc compound, an organic water-soluble rot inhibitor and water.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63334860A JP2945402B2 (en) | 1988-12-28 | 1988-12-28 | Sludge deodorant |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63334860A JP2945402B2 (en) | 1988-12-28 | 1988-12-28 | Sludge deodorant |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH02180698A JPH02180698A (en) | 1990-07-13 |
JP2945402B2 true JP2945402B2 (en) | 1999-09-06 |
Family
ID=18282029
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP63334860A Expired - Lifetime JP2945402B2 (en) | 1988-12-28 | 1988-12-28 | Sludge deodorant |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2945402B2 (en) |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5480860A (en) * | 1988-12-23 | 1996-01-02 | Petrolite Corporation | Methods for reducing sulfides in sewage gas |
CA2087166A1 (en) * | 1990-07-24 | 1992-01-25 | Baker Hughes Incorporated | Methods for reducing sulfides in sewage gas |
JPH0523698A (en) * | 1991-07-17 | 1993-02-02 | Ebara Infilco Co Ltd | Method and agent for deodorizing sludge |
JP2796932B2 (en) * | 1994-02-07 | 1998-09-10 | 株式会社荏原製作所 | Sludge deodorization method |
JP3619278B2 (en) * | 1995-02-06 | 2005-02-09 | ダイヤニトリックス株式会社 | Sludge deodorant |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS503087A (en) * | 1973-05-15 | 1975-01-13 | ||
JPS6054793A (en) * | 1983-09-06 | 1985-03-29 | Kurita Water Ind Ltd | Transporting method of odorous substance |
JPS63205197A (en) * | 1987-02-20 | 1988-08-24 | Nittetsu Mining Co Ltd | Deodorizing method |
JPS63315200A (en) * | 1987-06-15 | 1988-12-22 | Jiyoriibu:Kk | Deodorizer for cattle feces and urine |
-
1988
- 1988-12-28 JP JP63334860A patent/JP2945402B2/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
---|---|
JPH02180698A (en) | 1990-07-13 |
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