JPH1119692A - Sewage sludge treatment method - Google Patents
Sewage sludge treatment methodInfo
- Publication number
- JPH1119692A JPH1119692A JP17965797A JP17965797A JPH1119692A JP H1119692 A JPH1119692 A JP H1119692A JP 17965797 A JP17965797 A JP 17965797A JP 17965797 A JP17965797 A JP 17965797A JP H1119692 A JPH1119692 A JP H1119692A
- Authority
- JP
- Japan
- Prior art keywords
- bod
- sewage sludge
- organic substance
- fermenter
- fermentation
- 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.)
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- Treatment Of Sludge (AREA)
Abstract
(57)【要約】
【課題】 下水汚泥の脱水ケーキに水分調整材とカロリ
ー源としての有機物質を添加して発酵処理するに当り、
発酵槽への投入物の投入量を容易に制御して効率的な発
酵処理を行う。
【解決手段】 水分75〜85%の下水汚泥の脱水ケー
キに水分調整材及び有機物質を加え、発酵槽1内にて温
度を60〜80℃に維持し、撹拌機2で撹拌しながらエ
アパイプ3から通気して発酵させる。BOD槽容量負荷
が8kg−BOD/m3 ・日以上となるように添加量を
制御する。
(57) [Summary] [PROBLEMS] To add a water conditioner and an organic substance as a calorie source to a dewatered cake of sewage sludge and perform fermentation treatment.
Efficient fermentation treatment is performed by easily controlling the amount of input material to the fermenter. SOLUTION: A water conditioner and an organic substance are added to a dewatered cake of sewage sludge having a water content of 75 to 85%, the temperature is maintained at 60 to 80 ° C in a fermenter 1, and the air pipe 3 is stirred by a stirrer 2. Ferment with aeration from. The addition amount is controlled so that the BOD tank capacity load becomes 8 kg-BOD / m 3 · day or more.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、下水汚泥を発酵処
理する方法に係り、特に発酵反応を効率良く進行させる
よう改良された下水汚泥の処理方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for fermenting sewage sludge, and more particularly to a method for treating sewage sludge which is improved so that the fermentation reaction proceeds efficiently.
【0002】[0002]
【従来の技術】汚泥を発酵処理する方法として、汚泥に
おが屑を混ぜて水分を調節すると共に空隙率を高めて好
気性細菌の繁殖を促して発酵処理する方法が知られてい
る(特開昭55−90494号公報)。2. Description of the Related Art As a method of fermenting sludge, there is known a method of mixing sludge with sawdust to control the water content and increasing the porosity to promote the growth of aerobic bacteria, thereby performing fermentation treatment (Japanese Patent Application Laid-Open No. Sho. 55-90494).
【0003】また、このような汚泥の処理方法におい
て、有機物質量の不足による発酵反応速度の低下を防止
して、発酵処理効率を高める方法として、水分75〜8
5%の下水汚泥の脱水ケーキ100重量部におが屑10
〜50重量部及び米糠などのカロリー源となる有機物質
5〜30重量部を加え、発酵槽内にて温度を60〜80
℃に維持して発酵させるようにした方法も提案されてい
る(特開平9−85300号公報)。In such a method for treating sludge, a method for preventing a decrease in the fermentation reaction rate due to an insufficient amount of organic substances and improving the efficiency of fermentation treatment is described in US Pat.
Sawdust 10 per 100 parts by weight of dewatered cake of 5% sewage sludge
To 50 parts by weight and 5 to 30 parts by weight of an organic substance serving as a calorie source such as rice bran, and the temperature is adjusted to 60 to 80 in the fermenter.
A method has been proposed in which fermentation is performed while maintaining the temperature at 0 ° C (JP-A-9-85300).
【0004】特開平9−85300号公報記載の下水汚
泥の処理方法にあっては、米糠等のカロリー源となる有
機物質を添加するため、下水汚泥中の有機物質の分解が
進行しても、添加された該有機物質を微生物の栄養源と
して利用することにより微生物の有機物質分解反応熱を
十分に発生させ、発酵槽内の温度を60〜80℃に維持
し、下水汚泥の速やかな分解反応を継続させることがで
きる。これにより、下水汚泥を短時間の処理で大幅に減
容し、下水汚泥を原料とした肥料を効率良く生産するこ
とが可能となる。In the method of treating sewage sludge described in Japanese Patent Application Laid-Open No. 9-85300, an organic substance serving as a calorie source such as rice bran is added, so that even if the decomposition of the organic substance in the sewage sludge progresses, By utilizing the added organic substance as a nutrient source of the microorganism, the heat of the decomposition reaction of the organic substance of the microorganism is sufficiently generated, the temperature in the fermenter is maintained at 60 to 80 ° C., and the rapid decomposition reaction of the sewage sludge is performed. Can be continued. As a result, the volume of sewage sludge can be significantly reduced by a short-time treatment, and it becomes possible to efficiently produce fertilizer using sewage sludge as a raw material.
【0005】なお、カロリー源となる有機物質として用
いられている米糠は、通常の場合約300mg/gの高
BODであると共に、このBODは米糠中の油分に由来
し、易分解性である。また、嵩比重が約0.3、含水率
が約10〜15%といずれも低いことから、脱水ケーキ
とよく混ざり、脱水ケーキをほぐす効果を有する。[0005] Rice bran used as an organic substance serving as a calorie source usually has a high BOD of about 300 mg / g, and this BOD is derived from the oil content in the rice bran and is easily decomposable. In addition, since the bulk specific gravity is about 0.3 and the water content is as low as about 10 to 15%, it is well mixed with the dewatered cake and has an effect of loosening the dewatered cake.
【0006】[0006]
【発明が解決しようとする課題】米糠等のカロリー源と
なる有機物質を添加して発酵を行う方法では、該有機物
質の添加量に最適範囲があり、この添加量に過不足があ
ると、効率的な発酵を行えず、逆に発酵阻害が起こる場
合もある。In the method of fermenting by adding an organic substance serving as a calorie source such as rice bran, the amount of the organic substance to be added has an optimum range. In some cases, efficient fermentation cannot be performed, and fermentation inhibition may occur.
【0007】例えば、米糠の添加量が不足状態である
と、発酵槽内の微生物の栄養源として機能し得ず、この
ため発酵槽内の温度が上がらず、脱水ケーキの分解が進
行しなくなる。逆に、過剰添加であると、発酵槽内の微
生物が米糠を摂取して分解熱を発生し、発酵槽内温度を
上昇させるが、温度が上昇しすぎて80℃以上の高温と
なり、微生物の適正生育温度範囲を外れることで、脱水
ケーキの分解が進まなくなる。また、余剰の米糠はコン
ポスト製品中の有機物質を増加させ、土に施用した際、
植物に対して即効性の肥料として働き、生育を抑制する
恐れがある。また、米糠の過剰添加は当然のことなが
ら、米糠コストの高騰、ひいては処理コストの高騰につ
ながる。[0007] For example, if the amount of rice bran added is insufficient, the rice bran cannot function as a nutrient source for microorganisms in the fermenter, so that the temperature in the fermenter does not rise and decomposition of the dehydrated cake does not progress. Conversely, if it is excessively added, microorganisms in the fermenter ingest rice bran to generate decomposition heat and raise the temperature in the fermenter. By deviating from the appropriate growth temperature range, decomposition of the dehydrated cake does not proceed. In addition, surplus rice bran increases the organic matter in the compost product and when applied to soil,
It acts as a fast-acting fertilizer for plants and may inhibit growth. In addition, excessive addition of rice bran naturally leads to a rise in rice bran cost and, consequently, a processing cost.
【0008】このように、カロリー源としての有機物質
の添加量には好適範囲が存在することから、最小の添加
量で最大の効果を発揮させることが重要となる。従っ
て、有機物質の添加量制御は、発酵処理における重要な
管理項目となる。同様な理由から、発酵槽への脱水ケー
キや他の添加材の添加量も発酵処理における重要な管理
項目となる。As described above, since there is a suitable range for the amount of the organic substance added as a calorie source, it is important to exhibit the maximum effect with the minimum amount of addition. Therefore, control of the amount of addition of the organic substance is an important management item in the fermentation treatment. For the same reason, the amount of the dewatered cake and other additives added to the fermenter is also an important management item in the fermentation process.
【0009】ところで、脱水ケーキの発酵処理におい
て、発酵槽投入物の投入量制御の指標として、投入後の
水分量、C/N比、BOD濃度等が考えられる。例え
ば、水分量については60%前後が好適とされ、含水率
の高い脱水ケーキに対しては添加材を大量に添加して水
分調整を図るが、単に水分量のみを指標としてもBOD
が不足し、発酵が進行しない場合がある。また、C/N
(C:易分解性有機物質と難分解性有機物質との合計炭
素量,N:窒素)比を指標とする場合、発酵で分解対象
としているものは、易分解性有機物質であるため、C/
N比のC値のうち易分解性有機物質の割合を分析する必
要があるが、適当な分析方法がなく、C/N比による制
御は実現困難である。更に、BOD濃度では、脱水ケー
キと添加材との混合割合の指標とはなるが、投入量の指
標とはならない。By the way, in the fermentation treatment of the dehydrated cake, the water content, the C / N ratio, the BOD concentration, and the like after the addition can be considered as indices for controlling the amount of the input to the fermenter. For example, the water content is preferably around 60%. For a dehydrated cake having a high water content, a large amount of additives are added to adjust the water content.
May be insufficient and fermentation may not proceed. Also, C / N
When the ratio (C: total carbon content of easily decomposable organic substance and hardly decomposable organic substance, N: nitrogen) is used as an index, since the substance to be decomposed in fermentation is an easily decomposable organic substance, /
It is necessary to analyze the ratio of the easily decomposable organic substance in the C value of the N ratio, but there is no appropriate analysis method, and it is difficult to control by the C / N ratio. Further, the BOD concentration serves as an index of the mixing ratio between the dehydrated cake and the additive, but does not serve as an index of the input amount.
【0010】このように、従来において、脱水ケーキに
水分調整材とカロリー源としての有機物質を添加して発
酵させる下水汚泥の処理方法において、発酵槽への投入
量を決定するための有効な指標はなかった。As described above, conventionally, in a method of treating sewage sludge in which a moisture control material and an organic substance as a calorie source are added to a dewatered cake and fermented, an effective index for determining an amount to be fed into a fermenter. There was no.
【0011】本発明は上記従来の問題点を解決し、水分
75〜85%の下水汚泥の脱水ケーキに、水分調整材と
カロリー源となる有機物質とを加え、発酵槽内にて温度
を60〜80℃に維持して発酵させる方法において、脱
水ケーキ、水分調整材及び有機物質の投入量制御を容易
に行って、効率的な発酵を行うことを可能とする下水汚
泥の処理方法を提供することを目的とする。The present invention solves the above-mentioned conventional problems, and adds a water conditioner and an organic substance serving as a calorie source to a dewatered cake of sewage sludge having a water content of 75 to 85%, and raises the temperature in a fermenter to 60%. Provided is a method for treating sewage sludge that enables easy control of the amounts of dewatered cake, moisture regulator, and organic substance in a method of fermenting while maintaining the temperature at 〜80 ° C., thereby enabling efficient fermentation. The purpose is to:
【0012】[0012]
【課題を解決するための手段】本発明の下水汚泥の処理
方法は、水分75〜85%の下水汚泥の脱水ケーキに、
水分調整材と、カロリー源となる有機物質とを加え、発
酵槽内にて温度を60〜80℃に維持して発酵させる下
水汚泥の処理方法において、該発酵槽のBOD槽容量負
荷を8kg−BOD/m3 ・日以上(好ましくは8〜1
5kg−BOD/m3 ・日)とすることを特徴とする。The method for treating sewage sludge of the present invention comprises the steps of:
In a method for treating sewage sludge in which a water conditioner and an organic substance serving as a calorie source are added and fermentation is performed in a fermenter while maintaining the temperature at 60 to 80 ° C., the BOD tank capacity load of the fermenter is set at 8 kg- BOD / m 3 · day or more (preferably 8 to 1
5 kg-BOD / m 3 · day).
【0013】発酵槽のBOD槽容量負荷が8kg−BO
D/m3 ・日以上となるように、発酵槽への脱水ケー
キ、水分調整材及びカロリー源としての有機物質の投入
量を調節することより、発酵槽内を発酵に最適な条件に
制御することができる。The BOD tank capacity load of the fermenter is 8 kg-BO
The inside of the fermenter is controlled to optimal conditions for fermentation by adjusting the amounts of the dehydrated cake, the water regulator, and the organic substance as a calorie source to the fermenter so as to be at least D / m 3 · day. be able to.
【0014】[0014]
【発明の実施の形態】以下に本発明の実施の形態を詳細
に説明する。Embodiments of the present invention will be described below in detail.
【0015】まず、本発明におけるBOD槽容量負荷の
算出方法を説明する。First, a method for calculating the BOD tank capacity load according to the present invention will be described.
【0016】BOD槽容量負荷を求めるためには、ま
ず、発酵槽に投入する脱水ケーキ、おが屑等の水分調整
材及び米糠等の有機物質(以下、これらを「投入物」と
称す場合がある。)と、これらの投入物を投入する前の
発酵槽内の内容物(以下、「投入前内容物」と称す場合
がある。)の各々の含水率及びBOD濃度を求め、これ
らの結果から、1日当りの投入物の合計BOD量を下記
方法で算出する。In order to determine the capacity load of the BOD tank, first, a dewatered cake to be fed into the fermentation tank, a moisture adjusting material such as sawdust, and an organic substance such as rice bran (hereinafter, these may be referred to as "inputs"). ) And the contents of the fermenter before the introduction of these inputs (hereinafter, may be referred to as “contents before input”). The total BOD amount of the input per day is calculated by the following method.
【0017】[0017]
【数1】 (Equation 1)
【0018】算出された1日当りの投入物の合計BOD
量[B](kg)を投入後の発酵槽容量(m3 )で除算
することによりBOD槽容量負荷(kg−BOD/
m3 )が求められる。Calculated total BOD of input per day
By dividing the amount [B] (kg) by the fermenter capacity (m 3 ) after input, the BOD tank capacity load (kg-BOD /
m 3 ) is required.
【0019】本発明では、このようにして求めたBOD
槽容量負荷が8kg−BOD/m3・日以上となるよう
に各投入物の投入量を制御する。この値が8kg−BO
D/m3 ・日未満では十分な発酵分解率が得られない。
しかし、BOD槽容量負荷が20kg−BOD/m3 ・
日を超えると発酵分解率が低下してくるため、BOD槽
容量負荷は8〜20kg−BOD/m3 ・日、特に8〜
15kg−BOD/m3 ・日とするのが好ましい。In the present invention, the BOD determined in this way is
The input amount of each input is controlled so that the tank capacity load is 8 kg-BOD / m 3 · day or more. This value is 8kg-BO
If it is less than D / m 3 · day, a sufficient fermentation decomposition rate cannot be obtained.
However, the capacity load of the BOD tank is 20 kg-BOD / m 3
Since the fermentation decomposition rate decreases after more than one day, the BOD tank capacity load is 8 to 20 kg-BOD / m 3 · day, especially 8 to
It is preferably 15 kg-BOD / m 3 · day.
【0020】本発明においては、上記BOD槽容量負荷
と共に、下記方法で算出される投入後の内容物の含水率
[C](%)も制御の指標とするのが好ましく、投入後
の内容物の含水率が50〜70%、特に約60%となる
ように投入量の制御を行うのが望ましい。In the present invention, the water content [C] (%) of the content after charging calculated by the following method is preferably used as an index of control together with the BOD tank capacity load. Is preferably controlled so that the water content is 50 to 70%, particularly about 60%.
【0021】[0021]
【数2】 (Equation 2)
【0022】本発明において、下水汚泥としては水分7
5〜85%となるように脱水した脱水ケーキを用いる。
水分が85%よりも高いと、水分調整材の添加量が過大
となり、好ましくない。また、水分を75%よりも低く
することは脱水処理コストが嵩み、好ましくない。In the present invention, the sewage sludge contains water 7
Use a dehydrated cake dehydrated to 5 to 85%.
If the water content is higher than 85%, the amount of the water conditioning material added becomes excessive, which is not preferable. Further, making the water content lower than 75% is not preferable because the dewatering treatment cost increases.
【0023】水分調整材としては、おが屑、もみがら、
古紙等を用いることができる。このうち、おが屑として
は、杉、松、栂、檜などの針葉樹、桜、ブナ、椎、栗、
欅、桂、樟、桐などの広葉樹、米材、北洋材、ラワン、
レッドラワン、ホワイトラワン、イエローラワン等の南
洋材など各種の木材のおが屑を用いることができる。As the moisture adjusting material, sawdust, rice husk,
Used paper and the like can be used. Of these, sawdust includes conifers such as cedar, pine, toga, and hinoki, cherry, beech, shii, chestnut,
Broad-leaved trees such as zelkova, katsura, camphor, paulownia, rice, northern timber, lauan,
Various kinds of wood sawdust such as southern lumber such as red lauan, white lauan and yellow lauan can be used.
【0024】カロリー源となる有機物質としては、米糠
や、ナタネ油カス、綿実油カス、ダイズ油カス、ニシン
カス、イワシカス、蚕よう油カスなどの油カスが好適で
ある。特に好ましくは米糠を用いる。As organic substances serving as calorie sources, rice bran and oily scum such as rapeseed oil scum, cottonseed oil scum, soybean oil scum, herring sardine, sardine sprouts, silkworm oil scum and the like are suitable. Particularly preferably, rice bran is used.
【0025】水分調整材及び有機物質は、前述の如く、
BOD槽容量負荷が8kg−BOD/m3 ・日以上、好
ましくは8〜15kg−BOD/m3 ・日で、投入後内
容物の含水率が50〜70%程度となるように添加され
る。通常の場合、水分調整材の配合割合は、脱水ケーキ
100重量部に対し5〜50重量部とりわけ8〜30重
量部が好ましい。この範囲よりも水分調整材がも少ない
と、被処理物の水分が多すぎ、微生物の繁殖に適さな
い。また、水分調整材が50重量部を超えると、コスト
高であると共に、水分が過少となり、やはり微生物の繁
殖に適さない。また、米糠等のカロリー源となる有機物
質の配合割合は、脱水ケーキ100重量部に対し5〜3
0重量部とりわけ5〜20重量部が好適である。この有
機物質が5重量部よりも少ないと、発酵槽内を長時間6
0〜80℃に維持できず、30重量部よりも多いと、逆
に有機物質の分解に時間がかかると共に、材料コストも
嵩む。As described above, the moisture adjusting material and the organic substance
It is added so that the capacity load of the BOD tank is 8 kg-BOD / m 3 · day or more, preferably 8 to 15 kg-BOD / m 3 · day, and the water content of the content is about 50 to 70% after being charged. In a normal case, the mixing ratio of the moisture adjusting material is preferably 5 to 50 parts by weight, particularly preferably 8 to 30 parts by weight, per 100 parts by weight of the dewatered cake. If the amount of the water conditioning material is smaller than this range, the water content of the object to be treated is too large, and is not suitable for the propagation of microorganisms. On the other hand, if the water content exceeds 50 parts by weight, the cost is high and the water content is too low, which is not suitable for the propagation of microorganisms. In addition, the mixing ratio of the organic substance serving as a calorie source such as rice bran is 5 to 3 with respect to 100 parts by weight of the dehydrated cake.
0 parts by weight, especially 5 to 20 parts by weight, is suitable. If this organic substance is less than 5 parts by weight, the fermenter will need
If it cannot be maintained at 0 to 80 ° C. and exceeds 30 parts by weight, on the contrary, it takes time to decompose the organic substance, and the material cost increases.
【0026】本発明では、脱水ケーキ、水分調整材及び
カロリー源となる有機物質を発酵槽に投入し、通気しな
がら撹拌し、微生物による分解反応を進行させる。この
発酵槽としては、撹拌装置と空気吹込装置を備えた各種
のものを用いることができる。In the present invention, the dehydrated cake, the water conditioner and the organic substance serving as a calorie source are charged into the fermenter, and the mixture is stirred while being ventilated, thereby allowing the decomposition reaction by the microorganisms to proceed. As this fermenter, various types equipped with a stirring device and an air blowing device can be used.
【0027】発酵槽内の容量を100体積部とした場
合、脱水ケーキ、水分調整材及び有機物質の混合物が1
0〜40体積部程度となるように発酵槽内にこれらを間
欠的に(好ましくは1〜3日に1回程度の割合で)投入
するのが好ましい。When the volume in the fermenter is 100 parts by volume, the mixture of the dewatered cake, the water conditioner and the organic substance is 1 part.
It is preferable to introduce these into the fermenter intermittently (preferably at a rate of about once every 1 to 3 days) so as to be about 0 to 40 parts by volume.
【0028】槽内への通気量は、基本的には槽内の温度
が60〜80℃を維持し、かつ、上記含水率を維持する
ように調整される。Basically, the amount of ventilation into the tank is adjusted so that the temperature in the tank is maintained at 60 to 80 ° C. and the water content is maintained.
【0029】[0029]
【実施例】以下に実施例を挙げて本発明をより具体的に
説明する。The present invention will be described more specifically with reference to the following examples.
【0030】実施例1 図1に示す縦型スクープ式発酵装置を用いて下水汚泥脱
水ケーキの処理を行なった。この縦型スクープ式発酵装
置は、鋼板製又はコンクリート製の発酵槽(堆積高さ
1.5〜2.5m)1内にロータリ式撹拌機2が移動自
在に設置されており、槽1内にエアパイプ3から空気を
供給しながら該撹拌機2を水平方向に移動させ、槽1内
の材料をかき混ぜるようにしたものである。Example 1 A sewage sludge dewatered cake was treated using the vertical scoop fermentation apparatus shown in FIG. In this vertical scoop fermentation apparatus, a rotary agitator 2 is movably installed in a steel plate or concrete fermentation tank (deposition height 1.5 to 2.5 m) 1. The stirrer 2 is moved in the horizontal direction while supplying air from the air pipe 3 to mix the material in the tank 1.
【0031】用いた脱水ケーキは、オキシデーションデ
ィッチ法の下水汚泥をベルトプレス脱水したものであ
り、その含水率及びBOD量は表1に示す通りである。The dewatered cake used was obtained by subjecting sewage sludge of the oxidation ditch method to belt press dehydration. The water content and the BOD amount are as shown in Table 1.
【0032】水分調整材及び有機物質としては、それぞ
れ表1に示す含水率及びBOD量のおが屑(広葉樹(な
ら))及び米糠を用いた。Sawdust (broadleaf tree (Nara)) and rice bran having a water content and a BOD amount shown in Table 1 were used as the moisture regulator and the organic substance, respectively.
【0033】これらの投入物の投入前の槽内容物の含水
率及びBOD量は表1に示す通りである。Table 1 shows the water content and the BOD content of the tank contents before the introduction of these materials.
【0034】[0034]
【表1】 [Table 1]
【0035】脱水ケーキ、おが屑、米糠を槽1上部より
それぞれ400kg、40kg、40kg投入した。投
入前内容物は700kgであった。Dewatered cake, sawdust and rice bran were charged from the upper part of the tank 1 at 400 kg, 40 kg and 40 kg, respectively. The content before charging was 700 kg.
【0036】なお、切り返しを2〜3回/1日の割合で
行い、取り出しは切り返しを行いながら、一部を槽外に
搬出することで行った。通気量は100〜200L/m
in(発酵槽1m3 当り)とした。Switching was performed at a rate of 2 to 3 times / day, and removal was performed by carrying out a part of the processing while carrying out the switching. Aeration rate is 100 to 200 L / m
in (per 1 m 3 of fermentation tank).
【0037】このときのBOD槽容量負荷は8kg−B
OD/m3 ・日であり、投入後内容物の含水率は55%
であった。At this time, the capacity load of the BOD tank is 8 kg-B
OD / m 3 · day, water content of the contents is 55%
Met.
【0038】これにより発酵槽内温度は60〜80℃に
維持することができた。Thus, the temperature in the fermenter could be maintained at 60 to 80 ° C.
【0039】BOD槽容量負荷を下記の通りに変更した
こと以外は同様に行ってBOD槽容量負荷と有機物分解
率(投入物中の乾物の滞留1日当りの分解率(%/日)
で代替した。)との関係を求め、結果を図2に示した。The same procedure was followed except that the BOD tank capacity load was changed as follows, and the BOD tank capacity load and organic matter decomposition rate (decomposition rate of dry matter in the input material per day (% / day)
Was replaced by ) Was obtained, and the results are shown in FIG.
【0040】実施例2〜6、比較例1 比較のため、脱水ケーキ、おが屑及び米糠の投入量を変
え表2に示すBOD負荷量としたこと以外は実施例1と
同様に行って、結果を図2に示した。Examples 2 to 6 and Comparative Example 1 For comparison, the same procedure as in Example 1 was carried out except that the amounts of dehydrated cake, sawdust and rice bran were changed and the BOD load shown in Table 2 was used. As shown in FIG.
【0041】[0041]
【表2】 [Table 2]
【0042】図2より明らかなように、BOD槽容量負
荷8kg−BOD/m3 ・日付近で乾物分解率の最大値
が得られ、従って、このBOD槽容量負荷付近で有機物
質分解率が最大値となる。As is clear from FIG. 2, the maximum value of the dry matter decomposition rate was obtained around the capacity load of the BOD tank of 8 kg−BOD / m 3 · day. Value.
【0043】[0043]
【発明の効果】以上の通り、本発明の下水汚泥の処理方
法によれば、発酵槽への脱水ケーキ、水分調整材及びカ
ロリー源としての有機物質の添加量を容易に制御して効
率的な発酵処理を行える。As described above, according to the method for treating sewage sludge of the present invention, the amounts of the dewatered cake, the water regulator and the organic substance as a calorie source to the fermentation tank can be easily controlled to increase the efficiency. Fermentation treatment can be performed.
【図1】縦型スクープ式発酵装置の概略的な断面図であ
る。FIG. 1 is a schematic sectional view of a vertical scoop fermentation apparatus.
【図2】実施例1〜6及び比較例1の結果を示すグラフ
である。FIG. 2 is a graph showing the results of Examples 1 to 6 and Comparative Example 1.
1 発酵槽 2 ロータリ式撹拌機 3 エアパイプ Reference Signs List 1 fermenter 2 rotary stirrer 3 air pipe
Claims (1)
キに、水分調整材と、カロリー源となる有機物質とを加
え、発酵槽内にて温度を60〜80℃に維持して発酵さ
せる下水汚泥の処理方法において、 該発酵槽のBOD槽容量負荷を8kg−BOD/m3 ・
日以上とすることを特徴とする下水汚泥の処理方法。1. A dewatered cake of sewage sludge having a water content of 75 to 85%, to which a water conditioner and an organic substance serving as a calorie source are added, and the temperature is maintained at 60 to 80 ° C. in a fermentation tank for fermentation. In the method for treating sewage sludge, the BOD tank capacity load of the fermentation tank is set to 8 kg-BOD / m 3.
A method for treating sewage sludge, wherein the treatment time is at least one day.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17965797A JPH1119692A (en) | 1997-07-04 | 1997-07-04 | Sewage sludge treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17965797A JPH1119692A (en) | 1997-07-04 | 1997-07-04 | Sewage sludge treatment method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH1119692A true JPH1119692A (en) | 1999-01-26 |
Family
ID=16069611
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP17965797A Pending JPH1119692A (en) | 1997-07-04 | 1997-07-04 | Sewage sludge treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH1119692A (en) |
-
1997
- 1997-07-04 JP JP17965797A patent/JPH1119692A/en active Pending
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