JPH09110570A - Production of organic fertilizer and apparatus therefor - Google Patents

Production of organic fertilizer and apparatus therefor

Info

Publication number
JPH09110570A
JPH09110570A JP26836095A JP26836095A JPH09110570A JP H09110570 A JPH09110570 A JP H09110570A JP 26836095 A JP26836095 A JP 26836095A JP 26836095 A JP26836095 A JP 26836095A JP H09110570 A JPH09110570 A JP H09110570A
Authority
JP
Japan
Prior art keywords
mixture
ammonia
organic fertilizer
nitrogen
treated
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
JP26836095A
Other languages
Japanese (ja)
Inventor
Yoshimasa Okamoto
嘉正 岡本
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.)
COMSON CORP
Original Assignee
COMSON CORP
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 COMSON CORP filed Critical COMSON CORP
Priority to JP26836095A priority Critical patent/JPH09110570A/en
Publication of JPH09110570A publication Critical patent/JPH09110570A/en
Pending 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
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Abstract

PROBLEM TO BE SOLVED: To produce an organic fertilizer by mixing organic matter to be treated such as sewage sludge with an acidic solution to maintain the pH level of the mixture at pH <7 followed by drying it under heating to retain the effective nitrogen therein, reduce ammonia-nitrogen in wastewater and mitigate the load on a water treatment installation. SOLUTION: First, organic matter to be treated such as dehydrated sludge cake is mixed with an acidic solution in a mixer to adjust the pH value of the mixture to <7. Subsequently, the mixture is dried under heating by use of a dryer to produce the objective organic fertilizer. The steam discharged from the dryer is condensed by a condenser and fed via an effluent tank to a water treatment installation to dispose of the ammonia contained in the condensed water, and the resultant water is discharged.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】この発明は、下水汚泥等の被
処理物から有機肥料を製造する有機肥料製造方法および
その装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an organic fertilizer manufacturing method and apparatus for manufacturing organic fertilizer from an object to be treated such as sewage sludge.

【0002】[0002]

【従来の技術】下水汚泥や産業廃棄物は、一般に、海洋
投棄されたり、焼却後埋め立てに使用されたりしてい
る。ところが、このような海洋投棄や焼却は、地球環境
を汚染し、公害の原因となるため、許されなくなってき
ている。
2. Description of the Related Art Sewage sludge and industrial waste are generally dumped in the ocean or used for landfill after incineration. However, such ocean dumping and incineration pollute the global environment and cause pollution, which is becoming unacceptable.

【0003】そこで、本願出願人は、下水汚泥等の汚泥
の農地利用を目的として、脱水された汚泥を加熱処理に
より乾燥することによって、有機肥料を製造することを
試みた。
Therefore, the applicant of the present application tried to produce an organic fertilizer by drying dehydrated sludge by heat treatment for the purpose of utilizing sludge such as sewage sludge on agricultural land.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、上記加
熱処理による乾燥過程では、汚泥中のアンモニア態窒素
が気相に放出されやすく、乾燥後の汚泥に留まるアンモ
ニア態窒素が減るため、肥料成分として有効で植物が利
用しやすい形態のアンモニア態窒素を有効に利用するこ
とができないという問題がある。
However, during the drying process by the above heat treatment, ammonia nitrogen in sludge is easily released to the gas phase, and the amount of ammonia nitrogen remaining in the sludge after drying is reduced, so that it is effective as a fertilizer component. However, there is a problem that it is not possible to effectively use ammonia nitrogen in a form that is easy for plants to use.

【0005】また、上記過熱処理の乾燥過程で気相に放
出されたアンモニア態窒素が、汚泥から蒸発した後の凝
縮水に移行し、その凝縮水を河川等に排水するために
は、富栄養化物質であるアンモニア態窒素を除去する必
要がある。ところが、上記アンモニア態窒素を排水中か
ら除去するのが困難なため、水処理設備の負荷が大きく
なるという問題がある。上記排水中の窒素は、リンとと
もに近年規制対象とされた項目であり、排水中の窒素を
除去する技術は未だ確立途上にある。
Further, in order to transfer the ammonia nitrogen released in the vapor phase in the drying process of the above-mentioned heat treatment to the condensed water after evaporating from the sludge and drain the condensed water to a river, etc. It is necessary to remove ammonia nitrogen, which is a chemical substance. However, since it is difficult to remove the ammonia nitrogen from the waste water, there is a problem that the load on the water treatment facility becomes large. Nitrogen in the wastewater is an item that has recently been regulated together with phosphorus, and a technique for removing nitrogen in the wastewater is still in the process of being established.

【0006】そこで、この発明の目的は、被処理物の有
効窒素を留保できると共に、排水中のアンモニア態窒素
量を少なくして、水処理設備の負荷を軽減できる有機肥
料製造方法およびその装置を提供することにある。
[0006] Therefore, an object of the present invention is to provide an organic fertilizer manufacturing method and apparatus capable of retaining effective nitrogen of an object to be treated and reducing the amount of ammonia nitrogen in waste water to reduce the load of water treatment equipment. To provide.

【0007】[0007]

【課題を解決するための手段】上記目的を達成するた
め、請求項1の有機肥料製造方法およびその装置は、被
処理物と酸性溶液を混合して、上記被処理物と上記酸性
溶液との混合物のpH値が7以下になるようにするステ
ップと、上記混合物を加熱により乾燥するステップとを
備えたことを特徴としている。
In order to achieve the above object, the method and apparatus for producing organic fertilizer according to claim 1 mix an object to be treated and an acidic solution to obtain the object to be treated and the acidic solution. The method is characterized by comprising a step of adjusting the pH value of the mixture to 7 or less and a step of drying the mixture by heating.

【0008】上記請求項1の有機肥料製造方法によれ
ば、下水汚泥等の被処理物では、アンモニアとアンモニ
ウムイオンが解離平衡状態を保っており、被処理物のp
H値が7を越える場合、被処理物に酸性溶液を混合し
て、その混合物のpH値を7以下にすることによって、
解離定数が大きくなって、アンモニウムイオンが増大す
る一方、アンモニアが減少するので、上記混合物を加熱
により乾燥しても、アンモニアが気相にほとんど放出さ
れない。したがって、上記被処理物中のアンモニア態窒
素の減少を防ぎ、肥料中の窒素成分として分別される有
機体窒素とアンモニア態度窒素のうち、植物が利用しや
すい形態のアンモニア態窒素を乾燥後の処理物に留保で
きる。また、上記乾燥処理において、上記混合物から気
相に放出されるアンモニアが少なくなり、上記混合物か
ら蒸発した後の凝縮水に移行するアンモニア態窒素の量
が少なくなるので、アンモニア態窒素を除去する水処理
設備の負荷を軽減できる。
According to the method for producing an organic fertilizer according to the above-mentioned claim 1, in an object to be treated such as sewage sludge, ammonia and ammonium ions are in a dissociation equilibrium state, and p
When the H value exceeds 7, by mixing an acidic solution with the object to be treated and setting the pH value of the mixture to 7 or less,
Since the dissociation constant increases and the amount of ammonium ions increases, the amount of ammonia decreases, so that even if the mixture is dried by heating, almost no ammonia is released into the gas phase. Therefore, to prevent the reduction of ammonia nitrogen in the material to be treated, among organic nitrogen and ammonia attitude nitrogen that are separated as nitrogen components in the fertilizer, treatment after drying the ammonia nitrogen in a form that is easy for plants to utilize. Can be reserved for things. Further, in the drying treatment, less ammonia is released from the mixture to the gas phase, and the amount of ammonia nitrogen transferred to the condensed water after evaporation from the mixture is reduced, so that water for removing ammonia nitrogen is reduced. The load on processing equipment can be reduced.

【0009】また、請求項2の有機肥料製造装置は、被
処理物を供給する被処理物供給装置と、酸性溶液を供給
する酸性溶液供給装置と、上記被処理物供給装置からの
上記被処理物と上記酸性溶液供給装置からの上記酸性溶
液とを混合して混合物を生成すると共に、その混合物の
pH値が7以下になるようにする混合装置と、上記混合
装置からの上記混合物を加熱により乾燥する乾燥装置と
を備えたことを特徴としている。
The organic fertilizer manufacturing apparatus according to a second aspect of the present invention is an apparatus for supplying an object to be processed for supplying an object to be processed, an apparatus for supplying an acidic solution for supplying an acidic solution, and the object to be processed from the apparatus for supplying an object to be processed. And the acidic solution from the acidic solution supply device to form a mixture,
It is characterized by comprising a mixing device for adjusting the pH value to 7 or less, and a drying device for drying the above mixture from the above mixing device by heating.

【0010】上記請求項2の有機肥料製造装置によれ
ば、上記混合装置により被処理物供給装置からの被処理
物と酸性溶液供給装置からの酸性溶液とを混合して混合
物を生成すると共に、その混合物のpH値を7以下にす
る。そして、上記混合装置からの混合物を乾燥装置によ
り加熱して、被処理物中に含まれる水を蒸発させて乾燥
する。このとき、上記混合物のpH値を7以下にしてい
るので、解離定数が大きくなって、アンモニウムイオン
が増大する一方、アンモニアが減少し、乾燥処理におい
てアンモニアが気相にほとんど放出されない。したがっ
て、上記被処理物中のアンモニア態窒素の減少を防ぎ、
乾燥後の処理物にアンモニア態窒素を留保できる。ま
た、上記乾燥処理において、上記混合物から気相に放出
されるアンモニアが少なくなり、混合物から蒸発した後
の凝縮水に移行するアンモニア態窒素の量が少なくなる
ので、アンモニア態窒素を除去する水処理設備の負荷を
軽減できる。
According to the organic fertilizer producing apparatus of the second aspect, the mixture is mixed with the object to be treated from the object supplying apparatus and the acidic solution from the acidic solution supplying apparatus to form a mixture, The pH value of the mixture is 7 or less. Then, the mixture from the above-mentioned mixing device is heated by a drying device to evaporate water contained in the object to be processed and dry it. At this time, since the pH value of the mixture is set to 7 or less, the dissociation constant increases and the ammonium ion increases, while the ammonia decreases, and the ammonia is hardly released to the gas phase during the drying treatment. Therefore, preventing the decrease of ammonia nitrogen in the above-mentioned processed material,
Ammonia nitrogen can be retained in the dried product. Further, in the drying treatment, the amount of ammonia released from the mixture to the gas phase is reduced, and the amount of ammonia nitrogen transferred to the condensed water after evaporation from the mixture is reduced, so that a water treatment for removing ammonia nitrogen is performed. The load on the equipment can be reduced.

【0011】[0011]

【発明の実施の形態】以下、この発明の有機肥料製造方
法およびその装置を図示の実施の形態により詳細に説明
する。
BEST MODE FOR CARRYING OUT THE INVENTION The method for producing an organic fertilizer and the apparatus therefor according to the present invention will be described in detail below with reference to the embodiments shown in the drawings.

【0012】図1はこの発明の実施の形態の有機肥料製
造装置の概略構成図であり、1は下水汚泥を脱水した脱
水汚泥ケーキを供給する被処理物供給装置としての汚泥
受入ホッパー、2はpH調整用の硫酸溶液を貯蓄した硫
酸タンク、3は上記汚泥受入ホッパー1からの脱水汚泥
ケーキと上記硫酸タンク2からの硫酸溶液とを混合する
混合装置としての混練機、4は上記混練機3からの混合
物と後述する油タンク7からの植物油(以下、油という)
とを撹拌する撹拌調整タンク、5は上記撹拌調整タンク
4からの上記混合物と油とを加熱により乾燥させる乾燥
装置としての油圧減圧式乾燥装置、6は上記油温減圧式
乾燥装置5で加熱処理された汚泥と油とを分離する遠心
分離機、7は上記遠心分離機6で分離された油を溜める
と共に、上記撹拌調整タンク4と油温減圧式乾燥装置5
にポンプ22により油を供給する油タンクである。ま
た、8は上記油温減圧式乾燥装置5からの蒸気を冷却す
るコンデンサ、9は上記コンデンサ8内を循環させる水
を冷却するクーリングタワー、10は上記コンデンサ8
内の凝縮水を排水するポンプ、11は上記コンデンサ8
からポンプ10を介して排出された水を溜める排水タン
ク、12は上記排水タンク11からの排水を処理する水
処理設備、13は上記コンデンサ8を介して油温減圧式
乾燥装置5内を大気圧以下に減圧する真空ポンプであ
る。
FIG. 1 is a schematic configuration diagram of an organic fertilizer manufacturing apparatus according to an embodiment of the present invention, in which 1 is a sludge receiving hopper as a processed material supply apparatus for supplying a dehydrated sludge cake obtained by dehydrating sewage sludge. A sulfuric acid tank storing a sulfuric acid solution for pH adjustment, 3 is a kneading machine as a mixing device for mixing the dehydrated sludge cake from the sludge receiving hopper 1 and the sulfuric acid solution from the sulfuric acid tank 2, and 4 is the kneading machine 3 And vegetable oil from the oil tank 7 described below (hereinafter referred to as oil)
And a stirring adjustment tank 5 for stirring and a hydraulic decompression type drying device as a drying device for drying the mixture and oil from the stirring adjustment tank 4 by heating, and 6 a heat treatment by the oil temperature decompression type drying device 5. A centrifuge for separating the sludge and oil that has been separated, 7 stores the oil separated by the centrifuge 6, and the stirring adjustment tank 4 and the oil temperature decompression type drying device 5
Is an oil tank for supplying oil to the pump by a pump 22. Further, 8 is a condenser for cooling the steam from the oil temperature decompression type drying device 5, 9 is a cooling tower for cooling the water circulating in the condenser 8, and 10 is the condenser 8
A pump for draining the condensed water inside, 11 is the condenser 8
A drainage tank for storing water discharged from the pump 10 through the pump 10, a water treatment facility 12 for treating the drainage water from the drainage tank 11, and 13 at atmospheric pressure in the oil temperature decompression type drying device 5 via the condenser 8. It is a vacuum pump that reduces the pressure below.

【0013】上記構成の有機肥料製造装置において、汚
泥受入ホッパー1から脱水汚泥ケーキを混練機3に投入
すると共に、硫酸タンク2から硫酸溶液をポンプ21に
より供給し、混練機3で脱水汚泥ケーキと硫酸溶液を混
合して、その混合物のpH値が約6.5になるように調
整する。上記混練機3からの混合物を撹拌調整タンク4
に導いた後、その混合物と油タンク7からポンプ22に
より送られた油とを撹拌する。
In the organic fertilizer producing apparatus having the above-mentioned structure, the dehydrated sludge cake is put into the kneading machine 3 from the sludge receiving hopper 1, and the sulfuric acid solution is supplied from the sulfuric acid tank 2 by the pump 21 to form the dehydrated sludge cake in the kneading machine 3. Mix the sulfuric acid solution and adjust the pH value of the mixture to about 6.5. The mixture from the kneader 3 is stirred and adjusted in the tank 4
After that, the mixture and the oil sent from the oil tank 7 by the pump 22 are agitated.

【0014】そして、上記撹拌調整タンク4からの汚泥
と油との混合物を油温減圧式乾燥装置5に導いて、その
混合物を大気圧以下の減圧下で約110℃に加熱する。
その結果、上記混合物に含まれていた水は、蒸発して油
と置き換わり、汚泥の乾燥が行われる。
Then, the mixture of sludge and oil from the agitation adjustment tank 4 is introduced into an oil temperature decompression type drying device 5, and the mixture is heated to about 110 ° C. under reduced pressure below atmospheric pressure.
As a result, the water contained in the mixture evaporates and replaces the oil, and the sludge is dried.

【0015】次に、上記油温減圧式乾燥装置5から排出
された油を含む汚泥を遠心分離機6によって脱油する。
上記遠心分離機6から排出された乾燥汚泥は有機肥料と
なる一方、遠心分離機6で分離された油はタンク7に溜
まって再利用される。
Next, the sludge containing the oil discharged from the oil temperature decompression type drying device 5 is deoiled by the centrifugal separator 6.
The dried sludge discharged from the centrifugal separator 6 becomes organic fertilizer, while the oil separated by the centrifugal separator 6 is collected in the tank 7 and reused.

【0016】また、上記油温減圧式乾燥装置5におい
て、油温減圧式乾燥装置5からの蒸気をコンデンサ8で
冷却して凝縮し、コンデンサ8内の凝縮水をポンプ10
により排水タンク11に排水する。そして、上記排水タ
ンク11からの排水を水処理設備12により処理する。
Further, in the oil temperature decompression type drying device 5, the vapor from the oil temperature decompression type drying device 5 is cooled by the condenser 8 and condensed, and the condensed water in the condenser 8 is pumped.
Is drained to the drainage tank 11. Then, the drainage from the drainage tank 11 is treated by the water treatment facility 12.

【0017】上記処理前の脱水汚泥ケーキに含まれるア
ンモニアは、下記の式に示すように解離平衡を保ってい
る。
Ammonia contained in the dehydrated sludge cake before the above treatment maintains dissociation equilibrium as shown in the following formula.

【化1】 例えば、上記水溶液中のOH-イオン濃度が高くなる
と、すなわち水溶液のpH値が7を越えると、水溶液中
のアンモニウムイオンNH4 +とアンモニアNH3との平
衡は右側に偏り、アンモニウムイオンNH4 +に対するア
ンモニアNH3の割合が増大する。さらに、水温が上昇
すると、解離定数kが大きくなって、平衡が右側に偏る
ので、アンモニウムイオンNH4 +に対するアンモニアN
3の割合が増大する。また、上記アンモニアNH3が気
相に放出されて失われると、その失われたアンモニアN
3を補うように平衡が右側に偏る。しかも、上記アン
モニアNH3がアンモニウムイオンNH4 +より水への溶
解度が低いことから、平衡が右側に傾くほど、すなわち
アンモニアNH3の割合が大きいほどアンモニアNH
の気相への放出が多くなる。したがって、加熱処理によ
りアンモニアNHの比率が高くなり、アンモニア態窒
素の気相への放出量が増大する。
Embedded image For example, when the OH ion concentration in the aqueous solution becomes high, that is, when the pH value of the aqueous solution exceeds 7, the equilibrium between the ammonium ion NH 4 + and the ammonia NH 3 in the aqueous solution is biased to the right, and the ammonium ion NH 4 + The ratio of ammonia NH 3 to Furthermore, the water temperature rises, the dissociation constant k is increased, since the equilibrium is biased to the right, ammonia N for ammonium ion NH 4 +
The proportion of H 3 increases. Further, when the ammonia NH 3 is released into the gas phase and is lost, the lost ammonia N 3
Equilibrium is biased to the right to compensate for H 3 . Moreover, the ammonia NH 3 solubility in the ammonium ion NH 4 + than water since it is low enough equilibrium tilts right, that is, as ammonia NH 3 is large proportion of ammonia NH 3
Is released into the gas phase. Therefore, the heat treatment increases the proportion of ammonia NH 3 and increases the amount of ammonia nitrogen released into the gas phase.

【0018】図2はpH値に対するアンモニアNH3とア
ンモニウムイオンNH4 +の存在割合を示しており、水溶
液の温度が高いほどアンモニアNH3に対するアンモニ
ウムイオンNH4 +の割合が減少するのに対して、水溶液
のpH値が小さいほどアンモニアNH3に対するアンモニ
ウムイオンNH4 +の割合が増大する。
FIG. 2 shows the abundance ratios of ammonia NH 3 and ammonium ion NH 4 + to the pH value, whereas the ratio of ammonium ion NH 4 + to ammonia NH 3 decreases as the temperature of the aqueous solution increases. As the pH value of the aqueous solution decreases, the ratio of ammonium ion NH 4 + to ammonia NH 3 increases.

【0019】表1は図2においてpH値が8.5と6.
0におけるアンモニアNH3とアンモニウムイオンNH4
+の存在割合を示しており、20℃の汚泥を100℃ま
で加熱する場合、pH値が6.0では、アンモニウムイ
オンNH4 +が100%から96%,アンモニアNH3が0
%から4%と、ほとんど変化しないのに対して、pH値
が8.5では、アンモニウムイオンNH4 +が90%から
8%,アンモニアNH3が10%から92%と大きく変化
する。
Table 1 shows that the pH values in FIG. 2 are 8.5 and 6.
Ammonia NH 3 and ammonium ion NH 4 at 0
When the sludge at 20 ° C. is heated to 100 ° C., ammonium ion NH 4 + is 100% to 96%, ammonia NH 3 is 0% when the pH value is 6.0.
%, The pH value is 8.5, and the ammonium ion NH 4 + changes significantly from 90% to 8% and the ammonia NH 3 changes from 10% to 92%.

【表1】 したがって、上記有機肥料製造装置において、弱アルカ
リ性である脱水汚泥ケーキに硫酸溶液を混合して、その
混合物のpH値を約6.5に調整することによって、図
2に示すように、アンモニウムイオンNH4 +に対するア
ンモニアNH3の割合が100℃で約10%以下とな
り、油温減圧式乾燥装置5を用いた加熱処理において、
アンモニアNH3の気相への放出を抑える。
[Table 1] Therefore, in the above-mentioned organic fertilizer manufacturing apparatus, a sulfuric acid solution is mixed with a weakly alkaline dehydrated sludge cake to adjust the pH value of the mixture to about 6.5. The ratio of ammonia NH 3 to 4 + becomes about 10% or less at 100 ° C., and in the heat treatment using the oil temperature decompression dryer 5,
Suppress release of ammonia NH 3 into the gas phase.

【0020】以下、上記有機肥料製造装置において、脱
水汚泥ケーキに硫酸溶液を添加した場合と添加しない場
合の実験結果について説明する。なお、上記脱水汚泥ケ
ーキと硫酸溶液との混合物のpH値を約6.5にした。
Below, the results of experiments in the organic fertilizer producing apparatus with and without addition of the sulfuric acid solution to the dehydrated sludge cake will be described. The pH value of the mixture of the dehydrated sludge cake and the sulfuric acid solution was set to about 6.5.

【0021】表2は硫酸添加時における処理前の脱水汚
泥ケーキ,処理後の肥料および凝縮水中のアンモニア態
窒素量である(11回処理したときの平均値)。なお、表
2における凝縮水中のアンモニア態窒素量は、油温減圧
式乾燥処理開始から20分後,35分後,50分後,65
分後の凝縮水中に移行したアンモニア態窒素量を表わ
す。また、表2の数値の単位はmg/kgである。
Table 2 shows the amount of ammonia nitrogen in the dehydrated sludge cake before the treatment, the fertilizer after the treatment and the condensed water when the sulfuric acid was added (average value after 11 treatments). In addition, the amount of ammonia nitrogen in the condensed water in Table 2 is 20 minutes, 35 minutes, 50 minutes, 65 minutes after the oil temperature decompression type drying treatment is started.
It represents the amount of ammonia nitrogen transferred to the condensed water after a minute. The unit of numerical values in Table 2 is mg / kg.

【表2】 また、表3は硫酸無添加時における処理前の脱水汚泥ケ
ーキ,処理後の肥料および凝縮水中のアンモニア態窒素
量である(12回処理したときの平均値)。なお、表3に
おける凝縮水中のアンモニア態窒素量は、油温減圧式乾
燥処理開始から20分後,35分後,50分後,65分後
の凝縮水中に移行したアンモニア態窒素量を表わす。ま
た、表3の数値の単位はmg/kgである。
[Table 2] Further, Table 3 shows the amount of ammonia nitrogen in the dehydrated sludge cake before the treatment, the fertilizer and the condensed water after the treatment when sulfuric acid was not added (average value after 12 treatments). The amount of ammonia nitrogen in the condensed water in Table 3 represents the amount of ammonia nitrogen transferred to the condensed water after 20 minutes, 35 minutes, 50 minutes, and 65 minutes from the start of the oil-temperature reduced-pressure drying treatment. The unit of numerical values in Table 3 is mg / kg.

【表3】 上記表2と表3に基づいて、硫酸添加時と硫酸無添加時
における脱水汚泥ケーキと処理後の肥料のアンモニア態
窒素量の変化を図3に示している。図3に示すアンモニ
ア態窒素量の変化から分かるように、硫酸無添加時に比
べて、硫酸添加時の肥料中のアンモニア態窒素の減少を
大幅に抑制している。
[Table 3] Based on Tables 2 and 3 above, FIG. 3 shows changes in the amount of ammonia nitrogen in the dehydrated sludge cake and the fertilizer after the treatment when sulfuric acid was added and when sulfuric acid was not added. As can be seen from the change in the amount of ammonia nitrogen shown in FIG. 3, the decrease in ammonia nitrogen in the fertilizer when sulfuric acid is added is significantly suppressed as compared with when sulfuric acid is not added.

【0022】また、表4は上記表2と表3より求めた肥
料中へのアンモニア態窒素の留保率であり、表5は上記
表2と表3より求めた凝縮水へのアンモニア態窒素の放
出率である。
Table 4 shows the retention rate of ammonia nitrogen in the fertilizer obtained from Tables 2 and 3 above, and Table 5 shows the retention rate of ammonia nitrogen in condensed water obtained from Tables 2 and 3 above. The release rate.

【表4】 [Table 4]

【表5】 上記表5に基づいて、油温減圧式乾燥処理開始からの経
過時間に対するアンモニア態窒素量の変化を図4に示し
ている。図4に示すアンモニア態窒素量の変化から、硫
酸添加時は、経過時間に係わらず、アンモニア態窒素の
放出が少ないことが分かる。
[Table 5] Based on Table 5 above, FIG. 4 shows the change in the amount of ammonia nitrogen with respect to the elapsed time from the start of the oil temperature reduced pressure drying process. From the change in the amount of ammonia nitrogen shown in FIG. 4, it can be seen that when sulfuric acid is added, the amount of ammonia nitrogen released is small regardless of the elapsed time.

【0023】このように、上記脱水汚泥ケーキに硫酸溶
液を混合して、その混合物のpH値を約6.5にするこ
とによって、解離定数が大きくなり、アンモニウムイオ
ンNH4 +に対するアンモニアNH3の割合が減少する。
したがって、上記脱水汚泥ケーキと硫酸溶液および油の
混合物を油温減圧式乾燥装置5により加熱処理しても、
アンモニアNH3の気相への放出量が減少するので、加
熱処理後に脱油された乾燥肥料に、肥料中の窒素成分と
して分別される有機体窒素とアンモニア態窒素のうち、
植物が利用しやすい形態のアンモニア態窒素を留保する
ことができる。また、上記油温減圧式乾燥装置5による
加熱処理において、混合物から気相に放出されるアンモ
ニアが少なくなり、蒸発後の凝縮水中のアンモニア態窒
素量が減少するので、アンモニア態窒素を除去する水処
理設備12の負荷を軽減することができる。
As described above, by mixing the dehydrated sludge cake with a sulfuric acid solution and setting the pH value of the mixture to about 6.5, the dissociation constant becomes large, and the ammonia NH 3 + to the ammonium ion NH 4 + is increased. The rate decreases.
Therefore, even if the mixture of the dehydrated sludge cake, the sulfuric acid solution, and the oil is heat-treated by the oil-temperature reduced-pressure drying device 5,
Since the amount of ammonia NH 3 released into the gas phase is reduced, the dry fertilizer deoiled after the heat treatment should be separated into the organic nitrogen and ammonia nitrogen that are separated as nitrogen components in the fertilizer.
Ammonia nitrogen in a form that can be easily used by plants can be reserved. Further, in the heat treatment by the oil temperature decompression type drying device 5, the amount of ammonia released from the mixture into the gas phase is reduced, and the amount of ammonia nitrogen in the condensed water after evaporation is reduced. The load on the processing facility 12 can be reduced.

【0024】また、上記油温減圧式乾燥装置5は、上記
混合物を油中で加熱するので、混合物中の水が油と置き
換わって、汚泥中の水分を効率よく蒸発させることがで
きる。
Further, since the oil temperature decompression type drying device 5 heats the mixture in the oil, the water in the mixture replaces the oil and the water in the sludge can be efficiently evaporated.

【0025】また、上記油温減圧式乾燥装置5により上
記混合物を大気圧以下の減圧下で加熱するので、比較的
低い温度で汚泥中の水分の蒸発を促進することができ
る。また、汚泥中の有機物を燃やさないので、栄養分豊
富な良質の有機肥料を製造することができる。
Further, since the mixture is heated under the reduced pressure of atmospheric pressure or less by the oil temperature decompression type drying device 5, evaporation of water in the sludge can be promoted at a relatively low temperature. In addition, since organic matter in sludge is not burned, it is possible to produce high-quality organic fertilizer rich in nutrients.

【0026】上記実施の形態では、乾燥装置としての油
温減圧式乾燥装置5において、被処理物としての汚泥を
油中で加熱により乾燥したが、乾燥装置による加熱乾燥
方式はこれに限らず、対流伝熱(温風)乾燥、伝導伝熱乾
燥、輻射伝導乾燥等でもよい。
In the above embodiment, in the oil temperature decompression type drying device 5 as the drying device, the sludge as the object to be treated is heated and dried in oil, but the heating and drying method by the drying device is not limited to this. Convection heat transfer (warm air) drying, conduction heat transfer drying, radiation conduction drying, etc. may be used.

【0027】また、上記実施の形態では、脱水汚泥ケー
キと硫酸溶液を混合して、その混合物のpH値を約6.
5に調整したが、その混合物のpH値は、アンモニウム
イオンNH4 +に対するアンモニアNH3の割合が100
℃において約20%以下になる7以下の適宜な値にして
よい。
Further, in the above embodiment, the dehydrated sludge cake and the sulfuric acid solution are mixed, and the pH value of the mixture is about 6.
The pH value of the mixture was adjusted to 5 so that the ratio of ammonia NH 3 to ammonium ion NH 4 + was 100.
It may be an appropriate value of 7 or less, which is about 20% or less at ° C.

【0028】また、上記実施の形態では、被処理物とし
ての汚泥に酸性溶液として硫酸溶液を混合したが、酸性
溶液はこれに限らず、無機酸,有機酸(例えばクエン酸)
を問わない。
Further, in the above-mentioned embodiment, the sulfuric acid solution as the acidic solution was mixed with the sludge as the material to be treated, but the acidic solution is not limited to this, and inorganic acid, organic acid (eg citric acid)
It doesn't matter.

【0029】また、上記実施の形態では、被処理物とし
て下水汚泥を処理したが、被処理物はこれに限らず、生
ゴミ,糞尿および産業廃棄物等でもよいのは勿論であ
る。
In the above embodiment, the sewage sludge is treated as the object to be treated, but the object to be treated is not limited to this, and may be garbage, manure, industrial waste or the like.

【0030】[0030]

【発明の効果】以上より明らかなように、請求項1の発
明の有機肥料製造方法は、被処理物と酸性溶液を混合し
て、上記被処理物と酸性溶液との混合物のpH値が7以
下になるようにするので、混合物中の解離平衡状態のア
ンモニアとアンモニウムイオンの解離定数が大きくな
り、アンモニウムイオンが増大する一方、アンモニアが
減少する。そして、上記混合物を加熱するとき、気相に
放出されるアンモニアが少なくなるので、混合物中のア
ンモニアの減少を防ぐ。したがって、上記混合物を加熱
により乾燥させても、アンモニアが気相にほとんど放出
されないので、アンモニア態窒素の減少を防いで、乾燥
後の処理物に有効窒素が留保される。また、乾燥処理に
おいて、混合物から蒸発した後の凝縮水に含まれるアン
モニア態窒素の量が少なくなるので、アンモニア態窒素
を除去する水処理設備の負荷を軽減することができる。
As is apparent from the above, in the method for producing organic fertilizer according to the first aspect of the invention, the pH value of the mixture of the material to be treated and the acidic solution is 7 by mixing the material to be treated and the acidic solution. Since it is set as follows, the dissociation constant of ammonia and ammonium ions in the dissociation equilibrium state in the mixture becomes large, and the ammonium ions increase while the ammonia amount decreases. Then, when the above mixture is heated, the amount of ammonia released into the gas phase is reduced, so that the reduction of ammonia in the mixture is prevented. Therefore, even if the above mixture is dried by heating, almost no ammonia is released into the gas phase, so that reduction of ammonia nitrogen is prevented and effective nitrogen is retained in the dried product. Further, in the drying treatment, the amount of ammonia nitrogen contained in the condensed water after being evaporated from the mixture is reduced, so that the load on the water treatment equipment for removing ammonia nitrogen can be reduced.

【0031】また、請求項2の発明の有機肥料製造装置
は、混合装置により被処理物供給装置からの被処理物と
酸性溶液供給装置からの酸性溶液を混合して混合物を生
成すると共に、その混合物のpH値を7以下にした後、
上記混合装置からの混合物をクッカーにより加熱し、被
処理物中に含まれる水を蒸発させて、有機肥料を製造す
る。このとき、上記混合物のpH値を7以下にしている
ので、解離定数が大きくなって、アンモニウムイオンが
増大する一方、アンモニアが減少し、乾燥処理において
気相に放出されるアンモニア量が少なくなる。したがっ
て、上記加熱処理時の混合物中のアンモニア態窒素の減
少を防ぎ、乾燥後の肥料に有効窒素を留保することがで
きる。また、上記乾燥処理において混合物から蒸発した
後の凝縮水に移行したアンモニア態窒素が少ないので、
アンモニア態窒素を除去する水処理設備の負荷を軽減す
ることができる。
Further, in the organic fertilizer manufacturing apparatus of the invention of claim 2, the mixing apparatus mixes the object to be treated from the object supplying apparatus and the acidic solution from the acidic solution supplying apparatus to generate a mixture, and After adjusting the pH value of the mixture to 7 or less,
The mixture from the above mixing device is heated by a cooker to evaporate the water contained in the material to be treated to produce an organic fertilizer. At this time, since the pH value of the mixture is set to 7 or less, the dissociation constant increases and ammonium ions increase, while ammonia decreases and the amount of ammonia released into the gas phase during the drying process decreases. Therefore, it is possible to prevent the decrease of ammonia nitrogen in the mixture during the heat treatment and to retain the available nitrogen in the dried fertilizer. Further, since the amount of ammonia nitrogen transferred to the condensed water after being evaporated from the mixture in the drying treatment is small,
It is possible to reduce the load on the water treatment facility for removing ammoniacal nitrogen.

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

【図1】 図1はこの発明の実施の形態の有機肥料製造
装置の概略構成図である。
FIG. 1 is a schematic configuration diagram of an organic fertilizer manufacturing apparatus according to an embodiment of the present invention.

【図2】 図2はpH値に対するアンモニアとアンモニ
ウムイオンの存在割合を示す図である。
FIG. 2 is a diagram showing the abundance ratios of ammonia and ammonium ions with respect to pH values.

【図3】 図3は上記実施の形態の有機肥料製造装置に
よる実験結果に基づいて、硫酸添加時および硫酸無添加
時のアンモニア態窒素量を示す図である。
FIG. 3 is a diagram showing the amount of ammonia nitrogen when sulfuric acid is added and when sulfuric acid is not added, based on the results of experiments by the organic fertilizer manufacturing apparatus of the above embodiment.

【図4】 図4は上記有機肥料製造装置による実験結果
に基づいて、油温減圧式乾燥処理開始からの経過時間毎
の凝縮水中のアンモニア態窒素量を示す図である。
FIG. 4 is a diagram showing the amount of ammonia nitrogen in the condensed water for each elapsed time from the start of the oil temperature decompression type drying process, based on the experimental results by the organic fertilizer manufacturing apparatus.

【符号の説明】[Explanation of symbols]

1…汚泥受入ホッパー、2…硫酸タンク、3…混練機、
4…撹拌調整タンク、5…油温減圧式乾燥装置、6…遠
心分離機、7…油タンク、8…コンデンサ、9…クーリ
ングタワー、10,21,22…ポンプ、11…排水タン
ク、12…水処理設備。
1 ... Sludge receiving hopper, 2 ... Sulfuric acid tank, 3 ... Kneader,
4 ... Stirring adjustment tank, 5 ... Oil temperature decompression type drying device, 6 ... Centrifuge, 7 ... Oil tank, 8 ... Condenser, 9 ... Cooling tower, 10, 21, 22 ... Pump, 11 ... Drainage tank, 12 ... Water Processing equipment.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 被処理物と酸性溶液を混合して、上記被
処理物と上記酸性溶液との混合物のpH値が7以下にな
るようにするステップと、 上記混合物を加熱により乾燥するステップとを備えたこ
とを特徴とする有機肥料製造方法。
1. A step of mixing a material to be treated with an acidic solution so that a pH value of the mixture of the material to be treated and the acidic solution is 7 or less; and a step of drying the mixture by heating. A method for producing an organic fertilizer, comprising:
【請求項2】 被処理物を供給する被処理物供給装置
と、 酸性溶液を供給する酸性溶液供給装置と、 上記被処理物供給装置からの上記被処理物と上記酸性溶
液供給装置からの上記酸性溶液とを混合して混合物を生
成すると共に、その混合物のpH値が7以下になるよう
にする混合装置と、 上記混合装置からの上記混合物を加熱により乾燥する乾
燥装置とを備えたことを特徴とする有機肥料製造装置。
2. An object-supplying device for supplying an object to be processed, an acidic-solution supplying device for supplying an acidic solution, the object to be processed from the object-supplying device and the object to be supplied from the acidic-solution supplying device. A mixing device for mixing the acidic solution and the mixture to form a mixture, the pH value of the mixture being 7 or less, and a drying device for drying the mixture from the mixing device by heating are provided. Characteristic organic fertilizer manufacturing equipment.
JP26836095A 1995-10-17 1995-10-17 Production of organic fertilizer and apparatus therefor Pending JPH09110570A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP26836095A JPH09110570A (en) 1995-10-17 1995-10-17 Production of organic fertilizer and apparatus therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP26836095A JPH09110570A (en) 1995-10-17 1995-10-17 Production of organic fertilizer and apparatus therefor

Publications (1)

Publication Number Publication Date
JPH09110570A true JPH09110570A (en) 1997-04-28

Family

ID=17457445

Family Applications (1)

Application Number Title Priority Date Filing Date
JP26836095A Pending JPH09110570A (en) 1995-10-17 1995-10-17 Production of organic fertilizer and apparatus therefor

Country Status (1)

Country Link
JP (1) JPH09110570A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6733558B2 (en) 2000-11-07 2004-05-11 Honeywell International Inc. Beneficiated sludge
US6852142B2 (en) 2000-06-01 2005-02-08 Green Technologies, Inc. Organic-based fertilizer
JP2008178826A (en) * 2007-01-25 2008-08-07 Toshiba Corp Water treatment apparatus
JP2009268999A (en) * 2008-05-09 2009-11-19 Toshiba Corp Method and apparatus for treating water
JP2016203103A (en) * 2015-04-23 2016-12-08 三井造船環境エンジニアリング株式会社 Processing method of organic waste
US9695092B2 (en) 2006-02-23 2017-07-04 Anuvia Plant Nutrients Corporation Process for treating sludge and manufacturing bioorganically-augmented high nitrogen-containing inorganic fertilizer
US10870609B2 (en) 2018-08-16 2020-12-22 Anuvia Plant Nutrients Corporation Reactive inorganic coatings for agricultural fertilizers

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6852142B2 (en) 2000-06-01 2005-02-08 Green Technologies, Inc. Organic-based fertilizer
US6733558B2 (en) 2000-11-07 2004-05-11 Honeywell International Inc. Beneficiated sludge
US9695092B2 (en) 2006-02-23 2017-07-04 Anuvia Plant Nutrients Corporation Process for treating sludge and manufacturing bioorganically-augmented high nitrogen-containing inorganic fertilizer
JP2008178826A (en) * 2007-01-25 2008-08-07 Toshiba Corp Water treatment apparatus
JP2009268999A (en) * 2008-05-09 2009-11-19 Toshiba Corp Method and apparatus for treating water
JP2016203103A (en) * 2015-04-23 2016-12-08 三井造船環境エンジニアリング株式会社 Processing method of organic waste
US10870609B2 (en) 2018-08-16 2020-12-22 Anuvia Plant Nutrients Corporation Reactive inorganic coatings for agricultural fertilizers
US11542213B2 (en) 2018-08-16 2023-01-03 Anuvia Plant Nutrients IP Holdings, LLC Reactive inorganic coatings for agricultural fertilizers

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