JP2008086883A - Treatment method and treated product of white distilled liquor distillation waste liquid - Google Patents

Treatment method and treated product of white distilled liquor distillation waste liquid Download PDF

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JP2008086883A
JP2008086883A JP2006269301A JP2006269301A JP2008086883A JP 2008086883 A JP2008086883 A JP 2008086883A JP 2006269301 A JP2006269301 A JP 2006269301A JP 2006269301 A JP2006269301 A JP 2006269301A JP 2008086883 A JP2008086883 A JP 2008086883A
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waste liquid
shochu
distillation waste
treated product
distilled liquor
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Nobuchika Yoshida
信親 吉田
Toshio Nakamoto
俊雄 中元
Kazuyoshi Tsuchiya
和義 土屋
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Taiheiyo Materials Corp
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    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P60/00Technologies relating to agriculture, livestock or agroalimentary industries
    • Y02P60/80Food processing, e.g. use of renewable energies or variable speed drives in handling, conveying or stacking
    • Y02P60/87Re-use of by-products of food processing for fodder production

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  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a treatment method of allowing a white distilled liquor distillation waste liquid to be easily made useful and a treated product. <P>SOLUTION: The treatment method of the white distilled liquor distillation waste liquid comprises loading the white distilled liquor distillation waste liquid with calcined lime. The treatment method of the white distilled liquor distillation waste liquid and the treated product preferably comprise loading 100 mass parts of the white distilled liquor distillation waste liquid with 30 to 300 mass parts of calcined lime, thereby allowing the white distilled liquor distillation waste liquid to be powdered and also deodorized. Since the main component of the treated product obtained by the treatment method is calcium hydroxide (slaked lime), the treated product can be used for an alternate raw material of a calcium compound, particularly slaked lime, calcined lime or calcium carbonate. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、焼酎蒸留廃液の処理方法、およびその処理物に関し、詳しくは、焼酎蒸留廃液を有用化するための処理方法および有用化した焼酎蒸留廃液の処理物に関する。   TECHNICAL FIELD The present invention relates to a method for treating a shochu distillation waste liquid and a treated product thereof, and more particularly, to a treatment method for making a shochu distillate waste liquid useful and a treated product of a useful shochu distillate waste liquid.

焼酎の製造においては、焼酎蒸留粕や焼酎廃液等と呼ばれる焼酎蒸留廃液が発生し、一般に、この焼酎蒸留廃液量は生産量の2倍に達する。しかも、近年の焼酎ブームによって、その発生量は増加傾向にあり、有効な処理が切望されている。しかし、この焼酎蒸留廃液は、臭気が酷いうえに、含水分が高く(90%〜97%)、BODやSS等の濃度が一般の排水に比べて高く、微細な植物繊維を多量に含むために固液分離が困難な廃液である。   In the production of shochu, shochu distillate waste liquor called shochu distiller, shochu waste liquor, etc. is generated. In general, the amount of shochu distillate waste reaches twice the production volume. Moreover, due to the recent shochu boom, the amount of generation tends to increase, and effective processing is desired. However, this shochu-distilled waste liquid has a severe odor, high moisture content (90% to 97%), high concentration of BOD, SS, etc. compared to general waste water, and contains a large amount of fine plant fibers. It is a waste liquid that is difficult to separate into solid and liquid.

この焼酎蒸留廃液を有用化する方法が従来から試みられており、例えば、焼酎蒸留廃液をそのまま又は堆肥化して肥料化する方法、或いはそのまま飼料化する方法、プラント処理によって濃縮・乾燥した上で飼料化する方法、焼却する方法、嫌気性処理法と活性汚泥法とを組み合わせて排水処理する方法等が知られている(例えば非特許文献1、特許文献1、特許文献2、特許文献3及び特許文献4参照)。   Methods for making this shochu distillate waste liquor useful have been tried in the past, such as, for example, a method of making shochu distillate waste as it is or composting it into a fertilizer, or a method of making it as a feed, a feed after being concentrated and dried by plant treatment There are known methods such as non-patent literature 1, patent literature 1, patent literature 2, patent literature 3 and patents, for example, a method of wastewater treatment by combining an anaerobic treatment method and an activated sludge method. Reference 4).

しかし、焼酎蒸留廃液をそのまま飼料化または肥料化する方法は、悪臭が著しく、夏季に腐敗し易い問題があり、堆肥化して肥料にする場合も同様の問題がある。また飼料化や肥料化したものはその使用量に限界がある。一方、プラント処理による飼料化、焼却処理、嫌気性処理法と活性汚泥法とを組み合わせた排水処理などの方法は、大規模なプラントの建設や維持に費用を要し、中小の焼酎メーカーでは実施し難い。   However, the method of converting shochu distilled liquor into feed or fertilizer as it is has bad odor and is prone to spoilage in summer, and the same problem occurs when composting into fertilizer. Also, the amount of feed and fertilizer used is limited. On the other hand, methods such as feed conversion by plant treatment, incineration treatment, and wastewater treatment that combines the anaerobic treatment method and activated sludge method are expensive to construct and maintain large-scale plants, and are implemented by small and medium-sized shochu manufacturers. It is hard to do.

このため、現状では、乙類焼酎の生産が日本一の鹿児島県において、平成15年度(醸造年度:7月1日〜翌年6月30日)に発生した約33万tの焼酎蒸留廃液のうち、少なくとも10万tの焼酎蒸留廃液が海洋投入されている。今までは天然に由来する汚染されていない有機物等と見なされ、「廃棄物その他の物の海洋汚染防止に関する条約」(通称「ロンドン条約」)の例外品目として海洋投入が認められてきたが、規制強化により、近々海洋投入が極めて困難となる法的規制が予定されており、このため、従来の方法によらない焼酎蒸留廃液の処理方法が熱望されている。
鹿児島県工業技術センター報告書「焼酎蒸留粕の処理状況に関する研究開発や取り組みの現状について」、平成17年5月発表、1頁−4頁 特開2005−131592号公報 特開2000−157182号公報 特開平11−57794号公報 特開2001−310197号公報
For this reason, out of approximately 330,000 tons of shochu distillation wastewater generated in fiscal 2003 (brewing year: July 1 to June 30 of the following year) in Kagoshima Prefecture, where the production of oyster shochu is the best in Japan. At least 100,000 tons of shochu distillation waste liquid is put into the ocean. Until now, it was considered as an unpolluted organic matter derived from nature, etc., and it was accepted as an exception item in the “Convention on the Prevention of Marine Pollution of Waste and Others” (commonly known as the “London Convention”). Due to the stricter regulations, legal regulations that make it very difficult to enter the ocean in the near future are scheduled. For this reason, a method for treating shochu-distilled waste liquid that is not based on conventional methods is eagerly desired.
Kagoshima Prefectural Industrial Technology Center report “Research and Development and Current Situation of Disposal of Shochu Distillery”, May 2005, pp. 1-4 JP 2005-131582 A JP 2000-157182 A JP-A-11-57794 JP 2001-310197 A

本発明は、焼酎蒸留廃液の処理について、従来の上記問題を解決したものであり、焼酎蒸留廃液を簡単かつ効果的に無機物化する処理方法、およびその処理物を提供することを目的とする。   This invention solves the said conventional problem about the process of shochu-distilled waste liquid, and it aims at providing the processing method which makes shochu-distilled waste liquid mineralized easily and effectively, and its processed material.

本発明は、以下に示す構成によって上記問題を解決した焼酎蒸留廃液の処理方法および焼酎蒸留廃液処理物に関する。
(1)焼酎蒸留廃液に生石灰を添加することを特徴とする焼酎蒸留廃液の処理方法。
(2)焼酎蒸留廃液100質量部に対し、生石灰を30〜300質量部添加する上記(1)に記載する焼酎蒸留廃液の処理方法。
(3)焼酎蒸留廃液に生石灰を添加して、該焼酎蒸留廃液を粉末化する上記(1)または上記(2)に記載する焼酎蒸留廃液の処理方法。
(4)焼酎蒸留廃液に生石灰を添加して、該焼酎蒸留廃液を脱臭する上記(1)〜上記(3)の何れかに記載する焼酎蒸留廃液の処理方法。
(5)上記(1)〜上記(4)の何れかに記載する処理方法によって生じた焼酎蒸留廃液の処理物。
The present invention relates to a method for treating shochu-distilled waste solution and a treated product of shochu-distilled waste solution that have solved the above-described problems with the configuration described below.
(1) A method for treating a shochu distillation waste liquid, comprising adding quick lime to the shochu distillation waste liquid.
(2) The processing method of the shochu-distilled waste liquid as described in said (1) which adds 30-300 mass parts of quicklime with respect to 100 mass parts of shochu-distilled waste liquid.
(3) The method for treating a shochu-distilled waste liquid as described in (1) or (2) above, wherein quick lime is added to the shochu-distilled waste liquid to powder the shochu-distilled waste liquid.
(4) The processing method of the shochu-distilled waste liquid described in any one of (1) to (3) above, wherein quick lime is added to the shochu-distilled waste liquid to deodorize the shochu-distilled waste liquid.
(5) A processed product of shochu distillation waste liquid produced by the treatment method described in any one of (1) to (4) above.

焼酎蒸留廃液は含水率が90%以上の高含水物であるが、これに生石灰を添加すると、その水和反応の発熱によって水分が蒸発し、また生石灰が消石灰に変化するときに多量の水分を吸収するので脱水が進み、生石灰の添加量に応じてスラリー状からペースト状になり、生石灰の添加量が増えると粉末状になる。また同時に脱臭されるので、非常に取り扱いやすくなる。しかも、消石灰を主体とし、重金属等を含まないので、容易に再利用することができる。   Shochu distillation waste liquid is a highly water-containing product with a moisture content of 90% or more, but when quick lime is added to it, water evaporates due to the heat generated by the hydration reaction, and a large amount of water is added when quick lime changes to slaked lime. Since it absorbs, dehydration proceeds, and it changes from a slurry to a paste according to the amount of quicklime added, and becomes powdery when the amount of quicklime added increases. Moreover, since it is deodorized simultaneously, it becomes very easy to handle. Moreover, since it is mainly composed of slaked lime and does not contain heavy metals, it can be easily reused.

本発明の処理方法は、焼酎蒸留廃液に生石灰を添加すればよく、大規模なプラントを必要としないので、中小の焼酎メーカーでも容易に実施することができる。また、本発明の処理方法によって得られる処理物の主成分は水酸化カルシウム(消石灰)であるので、カルシウム化合物、特に消石灰、生石灰、または炭酸カルシウムの代替原材料として用いることができる。   The treatment method of the present invention only needs to add quick lime to the shochu distillation waste liquor and does not require a large-scale plant, so it can be easily implemented even by small and medium shochu manufacturers. Moreover, since the main component of the processed material obtained by the processing method of this invention is calcium hydroxide (slaked lime), it can be used as a substitute raw material of a calcium compound, especially slaked lime, quick lime, or calcium carbonate.

以下、本発明を実施例と共に具体的に説明する。
本発明の処理方法は、焼酎蒸留廃液に生石灰を添加することを特徴とする焼酎蒸留廃液の処理方法である。なお、以下の説明において、焼酎蒸留廃液に生石灰を添加したものを処理物と云う。
Hereinafter, the present invention will be specifically described with examples.
The processing method of this invention is a processing method of the shochu-distilled waste liquid characterized by adding quicklime to a shochu-distilled waste liquid. In addition, in the following description, what added quick lime to the shochu distillation waste liquid is called processed material.

本発明に用いる焼酎蒸留廃液の種類は限定されない。芋焼酎蒸留廃液、麦焼酎蒸留廃液、米焼酎蒸留廃液、そば焼酎蒸留廃液、黒糖焼酎蒸留廃液、泡盛焼酎蒸留廃液などの各種原料を用いる蒸留廃液について本発明を適用することができる。   The kind of shochu distillation waste liquid used in the present invention is not limited. The present invention can be applied to distillation waste liquids using various raw materials such as waste shochu distillation waste liquid, wheat shochu distillation waste liquid, rice shochu distillation waste liquid, buckwheat shochu distillation waste liquid, brown sugar shochu distillation waste liquid, and Awamori shochu distillation waste liquid.

本発明に用いる生石灰は、硬焼生石灰、軟焼生石灰などが挙げられ、酸化カルシウムを主成分とするものであれ生石灰として用いることができる。バッチ式で焼酎蒸留廃液に生石灰を添加する場合、生石灰に硬焼生石灰を用いると、水和反応が比較的緩やかに起こり、処理物の急激な温度上昇が起こり難いので、一バッチ当たりの処理量を多くすることができる。一方、生石灰に中焼生石灰または軟焼生石灰を用いると、水和反応が比較的速やかに起こり、処理時間を短くすることができるので好ましい。   Examples of the quicklime used in the present invention include hard calcined quicklime and soft calcined quicklime. When adding quick lime to shochu distillation waste liquid in batch mode, if hard calcined quick lime is used as quick lime, the hydration reaction occurs relatively slowly and the temperature of the processed product is unlikely to rise rapidly. Can be more. On the other hand, it is preferable to use medium calcined lime or soft calcined lime as quick lime because the hydration reaction occurs relatively quickly and the treatment time can be shortened.

処理装置の種類・大きさ・数並びに処理速度(単位時間当たりの処理量)に応じて、生石灰の焼成度、粒度および生石灰の添加量などを適宜選択すれば良い。また、生石灰の焼成度、粒度および生石灰の添加量などに応じて、処理装置の種類・大きさ・数並びに処理速度を適宜選択しても良い。   What is necessary is just to select suitably the baking degree of a quick lime, a particle size, the addition amount of quick lime, etc. according to the kind, magnitude | size, number of processing apparatuses, and the processing speed (processing amount per unit time). In addition, the type, size, number, and processing speed of the processing apparatus may be appropriately selected according to the calcining degree of quicklime, the particle size, the amount of quicklime added, and the like.

生石灰の添加量は、焼酎蒸留廃液100質量部に対し、生石灰30〜300質量部が好ましい。30質量部未満では焼酎蒸留廃液の水分量が多いために、得られるスラリー濃度が薄く、水分を除去するには更に乾燥工程や設備が必要となる。一方、生石灰添加量が300質量部を超えると、生石灰の一部が水和反応せずに残り、保管時に保管状況によっては周りから供給される水分によって発熱し、保管容器が熱によって破損する虞がある。   The amount of quicklime added is preferably 30 to 300 parts by weight with respect to 100 parts by weight of the shochu distillation waste liquid. If it is less than 30 parts by mass, the amount of water in the shochu distillation waste liquid is large, so that the resulting slurry concentration is thin, and a drying process and equipment are further required to remove the water. On the other hand, when the amount of quicklime added exceeds 300 parts by mass, a part of the quicklime remains without hydration reaction, and depending on the storage conditions during storage, heat may be generated due to moisture supplied from the surroundings, and the storage container may be damaged by heat. There is.

生石灰の添加量は、好ましくは、焼酎蒸留廃液100質量部に対し、生石灰50〜200質量部である。生石灰を50質量部以上加えることによって、処理物を粉末化することができるので、処理物の取り扱いが容易となる。また、生石灰の添加量が200質量部以下であれば、未反応の生石灰が少ないか又は無いので、保管時に保管状況によっては周りから供給される水分によって発熱し保管容器が熱によって破損する虞が少ないか又は全くない。より好ましい生石灰の添加量は、焼酎蒸留廃液100質量部に対し、生石灰50〜150質量部である。生石灰の添加量が150質量部以下であれば、処理物が適度な付着水分を有するので処理時,輸送時,使用時等において粉塵が発生し難いと伴に、処理設備をより小さくでき、処理物や原材料の保管スペースをより少なくすることができる。   The amount of quicklime added is preferably 50 to 200 parts by weight with respect to 100 parts by weight of the shochu distillation waste liquid. By adding 50 parts by mass or more of quicklime, the processed product can be pulverized, so that the processed product can be easily handled. Also, if the amount of quicklime added is 200 parts by mass or less, there is little or no unreacted quicklime, and depending on the storage conditions during storage, heat may be generated due to moisture supplied from the surroundings and the storage container may be damaged by heat. Little or no. The addition amount of quick lime is more preferably 50 to 150 parts by weight with respect to 100 parts by weight of the shochu distillation waste liquid. If the amount of quicklime added is 150 parts by mass or less, the treated product will have adequate adhering moisture, so that it is difficult for dust to be generated during processing, transportation, use, etc., and the processing equipment can be made smaller. Storage space for things and raw materials can be reduced.

本発明の処理方法を実施する装置は、焼酎蒸留廃液に生石灰を添加できるものであれば良く、形式、大きさなどは限定されない。例えば、連続的に焼酎蒸留廃液に生石灰を所定量添加できる装置を用いても良いし、バッチ式で焼酎蒸留廃液に生石灰を所定量添加できる装置を用いても良い。連続的に焼酎蒸留廃液に生石灰を所定量添加できる装置としては、例えば、連続式コンクリートミキサ、生石灰用ベルトコンベアに所定量の焼酎蒸留廃液を噴霧添加するための噴霧装置を備えた装置、生石灰用輸送管に所定量の焼酎蒸留廃液を噴霧添加するための噴霧装置を備えた装置などが挙げられる。また、バッチ式で焼酎蒸留廃液に生石灰を所定量添加できる装置としては、パン型コンクリートミキサ、パグミル型コンクリートミキサ、重力式コンクリートミキサ、ヘンシェル式ミキサ、リボンミキサ、噴射式ミキサ、トラックアジテータなどが挙げられる。   The apparatus which implements the processing method of this invention should just be able to add quick lime to a shochu distillation waste liquid, and a type, a magnitude | size, etc. are not limited. For example, an apparatus capable of continuously adding a predetermined amount of quick lime to the shochu distillation waste liquid may be used, or an apparatus capable of adding a predetermined amount of quick lime to the shochu distillation waste liquid in a batch type may be used. As a device that can continuously add a predetermined amount of quick lime to the shochu distillation waste liquid, for example, a continuous concrete mixer, a device equipped with a spray device for spraying and adding a predetermined amount of shochu distillation waste liquid to a quick lime belt conveyor, for quick lime Examples include an apparatus equipped with a spraying device for spraying and adding a predetermined amount of shochu distillation waste liquid to the transport pipe. The batch type equipment that can add a certain amount of quicklime to the shochu distillation waste liquid includes bread type concrete mixer, pug mill type concrete mixer, gravity concrete mixer, Henschel type mixer, ribbon mixer, jet mixer, truck agitator, etc. It is done.

なお、上記実施装置においては、生石灰と焼酎蒸留廃液とが均一に混合されるように、コンクリートミキサなどの混合手段を有する装置が好ましい。また、本発明の実施装置は、ミキサ、計量器、焼酎蒸留廃液供給用ポンプ、生石灰用ホッパ、および制御盤などをトラック等の車体に載せた移動式の装置としても良い。   In addition, in the said implementation apparatus, the apparatus which has mixing means, such as a concrete mixer, is preferable so that quick lime and shochu distillation waste liquid may be mixed uniformly. Moreover, the implementation apparatus of this invention is good also as a mobile apparatus which mounted the mixer, the meter, the pump for shochu distillation waste liquid supply, the lime hopper, the control panel, etc. on the vehicle bodies, such as a truck.

本発明の処理方法によれば、焼酎蒸留廃液に生石灰を添加することによって、焼酎蒸留廃液に95質量%程度含まれる水分と生石灰が発熱しながら水和反応し、水酸化カルシウム(消石灰)を生じる。このときの発熱によって焼酎蒸留廃液中の水分が蒸発し、また消石灰に水分が取り込まれるので更らに水分が減少する。処理物の状態は生石灰の添加量に応じてスラリー状からペースト状になり、生石灰の添加量が増えると粉末状になる。   According to the treatment method of the present invention, by adding quick lime to the shochu distillation waste liquor, the moisture and quick lime contained in the shochu distillation waste liquor is about 95% by mass while generating heat to produce calcium hydroxide (slaked lime). . Due to the heat generated at this time, the water in the shochu distillation waste liquid evaporates and the water is further taken in by the slaked lime. The state of the processed material changes from a slurry to a paste according to the amount of quicklime added, and becomes powdery when the amount of quicklime added increases.

本発明の処理物は、焼酎蒸留廃液に生石灰を添加したものであり、消石灰を主体とした強アルカリ性の物質であるので、腐敗し難く、長期保存し易い。また、この処理物は脱臭されており、原料である焼酎蒸留廃液の臭気が大幅に除去されているので取り扱い易い。特に、該処理物を粉末状にすることによって取扱性がさらに向上し、また臭気も消石灰と同程度になるので消石灰と同様に取り扱うことができ、より好ましい。   The treated product of the present invention is obtained by adding quick lime to shochu distillation waste liquid and is a strong alkaline substance mainly composed of slaked lime. In addition, this treated product is deodorized and is easy to handle because the odor of the shochu-distilled waste liquid which is a raw material is largely removed. In particular, the handling property is further improved by making the treated product into a powder form, and the odor is almost the same as that of slaked lime.

さらに、本発明の処理物は、主成分が水酸化カルシウムであるので、カルシウム化合物、特に消石灰、生石灰または炭酸カルシウム(石灰石)の代替原材料として用いることができる。因みに、水酸化カルシウムが酸化カルシウムになる温度は約450℃であり、炭酸カルシウムが酸化カルシウムになる温度約900℃に比べてかなり低いので、本発明の処理物を炭酸カルシウムの代替原材料として用いると、燃料費が少なく、かつ発生するCO2量も少なくできるので好ましい。 Furthermore, since the main component of the treated product of the present invention is calcium hydroxide, it can be used as an alternative raw material for calcium compounds, particularly slaked lime, quicklime or calcium carbonate (limestone). Incidentally, the temperature at which calcium hydroxide becomes calcium oxide is about 450 ° C., and is considerably lower than the temperature at which calcium carbonate becomes calcium oxide, which is about 900 ° C. Therefore, when the treated product of the present invention is used as an alternative raw material for calcium carbonate, It is preferable because the fuel cost is low and the amount of generated CO 2 can be reduced.

従来の焼酎蒸留廃液の処理方法は、主にこれを飼料や肥料などの有機資源材料として利用する方法であり、あるいは焼却処分する方法である。飼料や肥料として利用するには、栄養成分や肥料成分を保持するための処理方法に限られ、悪臭を充分に除去できないなどの問題があるが、本発明の処理方法は焼酎蒸留廃液を無機材料化する方法であり、従って、本発明によって得られる処理物は、消石灰を主体とするので、例えば、セメント、膨張材や急結剤等のセメント・コンクリート用混和材料、静的破砕剤、固化材、肥料、飼料、脱硫剤等の原材料として用いることができる。   Conventional methods for treating shochu-distilled waste liquid are mainly methods of using this as organic resource materials such as feed and fertilizer, or methods of incineration. In order to use it as feed or fertilizer, it is limited to treatment methods for retaining nutrient components and fertilizer components, and there is a problem that malodor cannot be sufficiently removed. Therefore, the processed product obtained by the present invention is mainly made of slaked lime. For example, cement, concrete admixtures such as cement, expansion material and quick setting agent, static crushing agent, solidifying material It can be used as a raw material for fertilizers, feeds, desulfurization agents and the like.

〔実施例1〕
直径約15cmの蒸発皿に焼酎蒸留廃液を50ml入れ、攪拌しながら生石灰を所定量添加し、更に3分間スパチュラで混合した。焼酎蒸留廃液は芋焼酎製造時に発生したもの(水分97質量%、褐色濁液、独特な臭気あり)を用い、生石灰は、軟焼生石灰(粒度:ブレーン比表面積4000cm2/g)を用いた。焼酎蒸留廃液に対する生石灰の添加量を変えて試験を行った。生石灰の添加量に応じた処理物の最高温度、処理時の粉塵の発生状況、処理物の性状を表1に示す。
[Example 1]
50 ml of shochu distillation waste liquid was put into an evaporating dish having a diameter of about 15 cm, a predetermined amount of quick lime was added with stirring, and further mixed with a spatula for 3 minutes. The shochu distillation waste liquid used was the one generated during the production of shochu shochu (water content 97% by weight, brown turbid liquid, with a unique odor), and quick lime was soft calcined lime (particle size: Blaine specific surface area 4000 cm 2 / g). The test was conducted by changing the amount of quicklime added to the shochu distillation waste liquid. Table 1 shows the maximum temperature of the treated product according to the amount of quicklime added, the state of dust generation during the treatment, and the properties of the treated product.

Figure 2008086883
Figure 2008086883

何れの試験水準も、生石灰投入開始から数秒で水蒸気が発生した。投入開始から1〜2分間は激しく水蒸気が発生し、以後は数分にわたり水蒸気が発生し続けたことを目視により確認した。   In all the test levels, water vapor was generated within a few seconds from the start of quick lime charging. It was visually confirmed that water vapor was vigorously generated for 1 to 2 minutes from the start of the charging, and that water vapor was continuously generated for several minutes thereafter.

さらに、各試験水準の処理物について、付着水分量と構成鉱物を調べた。この分析結果を表2に示す。付着水分は、混練終了直後の処理物を105℃の恒温槽内に24時間入れ、その前後の質量変化を混練終了直後の処理物の質量で除し、パーセント表示で表したものである。また、構成鉱物は、付着水分を105℃の恒温槽内で除去したものを粉末X線回折装置によって分析した。強熱減量(ig.loss)は、1000℃における値である。また、他の化学成分は、強熱減量を測定した後の処理物を蛍光X線分析により求めた値である。   Furthermore, the amount of adhering water and the constituent minerals were examined for the processed products at each test level. The analysis results are shown in Table 2. The adhering moisture is expressed as a percentage by putting the treated product immediately after completion of kneading in a thermostat at 105 ° C. for 24 hours, dividing the mass change before and after that by the mass of the treated product immediately after finishing kneading. In addition, the constituent minerals were analyzed by a powder X-ray diffractometer after removing adhering moisture in a constant temperature bath at 105 ° C. The ignition loss (ig.loss) is a value at 1000 ° C. The other chemical components are values obtained by fluorescent X-ray analysis of the processed product after measuring the loss on ignition.

表2に示すように、試験水準No.1〜No.6の何れの処理物も、水酸化カルシウムのピークのみ確認できた。化学成分の測定結果を併せて考慮すると、試験水準No.1〜No.6の処理物の主成分は水酸化カルシウムであることが確認された。試験水準No.7〜No.9の処理物について同様に構成鉱物を分析すると、水酸化カルシウムのピークの他に、酸化カルシウムのピークも確認でき、未反応の生石灰が処理物中に残っていることが確認された。   As shown in Table 2, only the calcium hydroxide peak could be confirmed in any of the processed products of test levels No. 1 to No. 6. Considering the measurement results of the chemical components together, it was confirmed that the main component of the processed products of test levels No. 1 to No. 6 was calcium hydroxide. When the constituent minerals are similarly analyzed for the processed products of test levels No. 7 to No. 9, in addition to the calcium hydroxide peak, a calcium oxide peak can also be confirmed, and unreacted quicklime remains in the processed product. It was confirmed.

表2の結果から、生石灰の添加量は焼酎蒸留廃液100質量部に対して30〜300質量部が適当であり、50〜200質量部が好ましいことが分かる。生石灰を30〜150質量部添加した処理物は生石灰の全量が消石灰に変化し、30質量部添加したものは24時間後に粉末状になり、50質量部添加したものは混練直後に粉末状の処理物が得られ、処理時の粉塵の発生も少ない。一方、生石灰を200質量部以上添加すると、未反応の生石灰が残り、処理時の粉塵が激しく、300質量部を超えると、処理物の最高温度がかなり高くなる。   From the results of Table 2, it can be seen that the amount of quicklime added is suitably 30 to 300 parts by mass and preferably 50 to 200 parts by mass with respect to 100 parts by mass of the shochu distillation waste liquid. The processed product added with 30 to 150 parts by weight of quick lime changes the total amount of quick lime to slaked lime, the one added with 30 parts by weight becomes powdery after 24 hours, and the one with 50 parts by weight added is treated with powder immediately after kneading. Products are obtained, and the generation of dust during processing is small. On the other hand, when 200 parts by mass or more of quicklime is added, unreacted quicklime remains, and the dust during the treatment is intense. When the amount exceeds 300 parts by mass, the maximum temperature of the processed product becomes considerably high.

Figure 2008086883
Figure 2008086883

実施例1の処理物の脱臭効果を調べた。試験方法は、試験水準No.1、No.4、No.5、No.7の処理物について、10人のモニター(A〜J)による官能(臭気)試験を行なった。評価基準は焼酎蒸留廃液の臭気を10とし、消石灰(特級品)の臭気を0とする10段階評価で判定した。試験結果を表3に示す。表3に示すとおり、本発明の処理物は何れも悪臭が大幅に低減されており、試験水準No.7は消石灰に近い臭気まで脱臭されている。   The deodorizing effect of the processed product of Example 1 was examined. The test method performed the sensory (odor) test by 10 monitors (AJ) about the processed material of test level No.1, No.4, No.5, No.7. The evaluation criteria were determined by a 10-step evaluation in which the odor of shochu distillation waste liquid was 10 and the odor of slaked lime (special grade product) was 0. The test results are shown in Table 3. As shown in Table 3, all of the processed products of the present invention have greatly reduced malodor, and test level No. 7 has been deodorized to an odor close to slaked lime.

Figure 2008086883
Figure 2008086883

[実施例2]
100リットルのパン型モルタル用ミキサに焼酎蒸留廃液を入れ、攪拌しながら生石灰を所定量添加し、更に15分間混合した。処理物の温度が50℃程度に下がったところで、当該処理物をフレキシブルコンテナに移し保管した。焼酎蒸留廃液は芋焼酎製造時に発生したもの(水分97質量%,褐色濁液,独特な臭気あり)を用い、生石灰は軟焼生石灰(粒度:目開き3mmの篩通過品)を用いた。焼酎蒸留廃液に対する生石灰の添加量を変えて試験を行った。生石灰の添加量に応じた処理時の粉塵の発生状況、処理物の性状を表4に示す。
[Example 2]
The shochu-distilled waste liquid was put into a 100-liter pan-type mortar mixer, and a predetermined amount of quick lime was added while stirring, and further mixed for 15 minutes. When the temperature of the processed product dropped to about 50 ° C., the processed product was transferred to a flexible container and stored. The shochu distillation waste liquid used was the one generated during the production of shochu shochu (water content 97 mass%, brown turbid liquid, with a unique odor), and the soft lime was soft calcined lime (particle size: sieved product with 3 mm openings). The test was conducted by changing the amount of quicklime added to the shochu distillation waste liquid. Table 4 shows the state of dust generation during treatment according to the amount of quicklime added and the properties of the treated product.

No.10〜No.13の何れの試験水準も、生石灰投入開始から数秒で水蒸気が発生した。投入開始から1〜2分間は激しく水蒸気が発生し、以後は10数分にわたり水蒸気が発生し続けた。処理時における処理物の最高温度は、何れの水準も103℃程度であった。   In any test level of No. 10 to No. 13, water vapor was generated within a few seconds from the start of quicklime input. Water vapor was vigorously generated for 1 to 2 minutes from the start of charging, and water vapor was continuously generated over 10 minutes thereafter. The maximum temperature of the processed material at the time of processing was about 103 ° C. in all levels.

さらに、各試験水準の処理物について、付着水分量と構成鉱物を調べた。この分析結果を表4に示す。付着水分は、混練終了直後の処理物を105℃の恒温槽内に24時間入れ、その前後の質量変化を混練終了直後の処理物の質量で除し、パーセント表示で表したものである。また、構成鉱物は、付着水分を105℃の恒温槽内で除去したものを粉末X線回折装置によって分析した。   Furthermore, the amount of adhering water and the constituent minerals were examined for the processed products at each test level. The analysis results are shown in Table 4. The adhering moisture is expressed as a percentage by putting the treated product immediately after completion of kneading in a thermostat at 105 ° C. for 24 hours, dividing the mass change before and after that by the mass of the treated product immediately after finishing kneading. In addition, the constituent minerals were analyzed by a powder X-ray diffractometer after removing adhering moisture in a constant temperature bath at 105 ° C.

表4に示すように、試験水準No.10〜No.13の何れの処理物も、水酸化カルシウムのピークのみ確認できた。各試験水準の処理物の1000℃に加熱後における化学成分の測定の結果、強熱減量ベースのCaO含有率が何れも96.6質量%〜96.8質量%であったことを併せて考慮すると、この処理物の主成分は水酸化カルシウムであることが確認された。また、処理前の焼酎蒸留廃液に比べて、処理物の臭気はかなり抑えられて取り扱い易くなっており、2週間フレキシブルコンテナで保管した後の処理物の臭気は、市販の消石灰の臭気と略同程度であった。   As shown in Table 4, only the calcium hydroxide peak could be confirmed in any of the processed products of test levels No. 10 to No. 13. Considering that the results of measurement of chemical components of each processed product at the test level after heating to 1000 ° C. were 96.6% by mass to 96.8% by mass on the basis of loss on ignition. Then, it was confirmed that the main component of this treated product was calcium hydroxide. In addition, the odor of the treated product is considerably suppressed compared with the waste liquor before treatment, and the odor of the treated product after being stored in a flexible container for 2 weeks is almost the same as the odor of commercially available slaked lime. It was about.

Figure 2008086883
Figure 2008086883

[実施例3]
試験水準No.13の処理物を用い、表5の配合で混合粉砕した粉砕物を1450℃の電気炉で60分加熱後急冷し、その焼結物に二水石膏を添加し、ボールミルでブレーン比表面積3300cm2/gに粉砕することによって普通ポルトランドセメントを作製した。処理物以外には、珪石,バン土頁岩,酸化鉄,二水石膏を用いた。
[Example 3]
Using the processed product of test level No. 13, the pulverized product mixed and pulverized with the composition shown in Table 5 was heated in an electric furnace at 1450 ° C. for 60 minutes and then rapidly cooled. Dihydrate gypsum was added to the sintered product, and brain-browned. Ordinary Portland cement was prepared by grinding to a specific surface area of 3300 cm 2 / g. In addition to the treated material, silica stone, bangshale shale, iron oxide, and dihydrate gypsum were used.

作製したセメント100質量部に対し、珪砂300質量部および水12.5質量部をホバート社製ミキサ(型式:N−50)に入れて4分間混合し、規格(JIS R 5201 「セメントの物理試験方法」)に準じてモルタルを作製した。このモルタルの材齢3日,7日,28日の圧縮強さを測定した。その結果、圧縮強さは、それぞれ27.8N/mm2,43.5N/mm2,59.4N/mm2であり、通常のセメントを用いた場合と同程度であった。 To 100 parts by mass of the produced cement, 300 parts by mass of silica sand and 12.5 parts by mass of water are placed in a Hobart mixer (model: N-50) and mixed for 4 minutes. Standard (JIS R 5201 “Physical test of cement” A mortar was prepared according to the method ")". The compressive strength of this mortar was measured at the age of 3 days, 7 days and 28 days. As a result, compressive strength, respectively 27.8N / mm 2, 43.5N / mm 2, a 59.4N / mm 2, were comparable to the case of using a conventional cement.

Figure 2008086883
Figure 2008086883

[実施例4]
試験水準No.13の処理物を用い、表6の配合で混合粉砕した粉砕物を1450℃の電気炉で60分加熱後急冷し、ボールミルでブレーン比表面積2300cm2/gに粉砕することによってセメント混和材料を作製した。処理物以外には珪石,バン土頁岩,酸化鉄,無水石膏を用いた。
[Example 4]
Cement by using the processed product of test level No. 13, mixed and pulverized with the composition shown in Table 6, heated in an electric furnace at 1450 ° C. for 60 minutes, rapidly cooled, and pulverized to a Blaine specific surface area of 2300 cm 2 / g with a ball mill. An admixture was prepared. In addition to the treated material, silica stone, van earth shale, iron oxide, and anhydrous gypsum were used.

作製したセメント混和材料7質量部、普通ポルトランドセメント93質量部、およびISO標準砂300質量部をビニール袋により乾式で混合し、セメント組成物を作製した。このセメント組成物100質量部に対し水12.5質量部を添加し、混練し、モルタルを作製した。作製したモルタルを規格(JIS A 6202「コンクリート用膨張材」附属書2)に従って、材齢7日の膨張率を測定した。その結果、作製したモルタルの膨張率が0.108%であったので、作製したセメント混和材料は、コンクリート用膨張材として好適であることが確認された。   A cement composition was prepared by mixing 7 parts by mass of the prepared cement admixture, 93 parts by mass of ordinary Portland cement, and 300 parts by mass of ISO standard sand using a plastic bag. 12.5 parts by mass of water was added to 100 parts by mass of the cement composition and kneaded to prepare a mortar. The expansion rate of the produced mortar was measured according to the standard (JIS A 6202 “Expanding material for concrete” Annex 2) at the age of 7 days. As a result, since the expansion rate of the produced mortar was 0.108%, it was confirmed that the produced cement admixture was suitable as an expansion material for concrete.

Figure 2008086883
Figure 2008086883

[実施例5]
試験水準No.13の処理物を用い、表7の配合で混合粉砕した粉砕物を焼点温度1450℃のロータリーキルンで焼成し冷却した後、焼結塊をボールミルでブレーン比表面積2300cm2/gに粉砕することによってセメント混和材料を作製した。処理物以外には生石灰,珪石,バン土頁岩,酸化鉄,無水石膏を用いた。
[Example 5]
Using a processed product of test level No. 13, the pulverized product mixed and pulverized with the composition shown in Table 7 was baked in a rotary kiln having a baking temperature of 1450 ° C. and cooled, and then the sintered ingot was subjected to a Blaine specific surface area of 2300 cm 2 / g with a ball mill. A cement admixture was made by grinding. In addition to the treated material, quicklime, quartzite, van earth shale, iron oxide, and anhydrous gypsum were used.

作製したセメント混和材料7質量部、普通ポルトランドセメント93質量部、およびISO標準砂300質量部をビニール袋により乾式で混合し、セメント組成物を作製した。このセメント組成物100質量部に対し水12.5質量部を添加し、混練し、モルタルを作製した。作製したモルタルを規格(JIS A 6202「コンクリート用膨張材」附属書2)に従って、材齢7日の膨張率を測定した。その結果、作製したモルタルの膨張率が0.125%であったので、作製したセメント混和材料は、コンクリート用膨張材として好適であることが確認された。   A cement composition was prepared by mixing 7 parts by mass of the prepared cement admixture, 93 parts by mass of ordinary Portland cement, and 300 parts by mass of ISO standard sand using a plastic bag. 12.5 parts by mass of water was added to 100 parts by mass of the cement composition and kneaded to prepare a mortar. The expansion rate of the produced mortar was measured according to the standard (JIS A 6202 “Expanding material for concrete” Annex 2) at the age of 7 days. As a result, since the expansion rate of the produced mortar was 0.125%, it was confirmed that the produced cement admixture was suitable as an expansion material for concrete.

Figure 2008086883
Figure 2008086883

本発明の処理方法によれば、焼酎蒸留廃液を無機材料化することによって、廃棄物として処分されてきた焼酎蒸留廃液を従来より容易に処理することができる。また、本発明の処理方法によって製造された処理物は、消石灰を主体とするので、セメント,膨張材や急結剤等のセメント・コンクリート用混和材料、静的破砕剤、固化材、肥料、飼料、脱硫剤等の原材料として好適に用いることができ、広範な分野に用いることができるので、従来よりも多量の焼酎蒸留廃液を有用化することができる。   According to the treatment method of the present invention, by converting the shochu distillation waste liquid into an inorganic material, the shochu distillation waste liquid that has been disposed of as waste can be more easily treated than before. Moreover, since the processed product manufactured by the processing method of the present invention is mainly composed of slaked lime, cement, concrete admixture such as cement, expansion material and quick setting agent, static crushing agent, solidifying material, fertilizer, feed Since it can be suitably used as a raw material such as a desulfurizing agent and can be used in a wide range of fields, a larger amount of shochu distillation waste liquid than before can be made useful.

Claims (5)

焼酎蒸留廃液に生石灰を添加することを特徴とする焼酎蒸留廃液の処理方法。
A method for treating shochu distillation waste liquid, comprising adding quick lime to the shochu distillation waste liquid.
焼酎蒸留廃液100質量部に対し、生石灰を30〜300質量部添加する請求項1に記載する焼酎蒸留廃液の処理方法。
The processing method of the shochu-distilled waste liquid of Claim 1 which adds 30-300 mass parts of quick lime with respect to 100 mass parts of shochu-distilled waste liquid.
焼酎蒸留廃液に生石灰を添加して、該焼酎蒸留廃液を粉末化する請求項1または請求項2に記載する焼酎蒸留廃液の処理方法。
The processing method of the shochu-distilled waste liquid of Claim 1 or Claim 2 which adds quick lime to a shochu-distilled waste liquid, and pulverizes this shochu-distilled waste liquid.
焼酎蒸留廃液に生石灰を添加して、該焼酎蒸留廃液を脱臭する請求項1〜請求項3の何れかに記載する焼酎蒸留廃液の処理方法。
The processing method of the shochu-distilled waste liquid in any one of Claims 1-3 which adds a quick lime to a shochu-distilled waste liquid, and deodorizes this shochu-distilled waste liquid.
請求項1〜請求項4の何れかに記載する処理方法によって生じた焼酎蒸留廃液の処理物。 Processed product of the shochu distillation waste liquid produced by the processing method according to claim 1.
JP2006269301A 2006-09-29 2006-09-29 Treatment method and treated product of white distilled liquor distillation waste liquid Pending JP2008086883A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012046403A (en) * 2010-08-24 2012-03-08 Takuichiro Kendo Method of manufacturing slaked lime containing organic substance

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52127473A (en) * 1976-04-19 1977-10-26 Kaihoo Kk Method of treating organic wastes
JPS63162592A (en) * 1986-12-26 1988-07-06 有限会社 南薩農林 Solid valuables from spirits distilled waste lye as raw material and manufacture

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52127473A (en) * 1976-04-19 1977-10-26 Kaihoo Kk Method of treating organic wastes
JPS63162592A (en) * 1986-12-26 1988-07-06 有限会社 南薩農林 Solid valuables from spirits distilled waste lye as raw material and manufacture

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012046403A (en) * 2010-08-24 2012-03-08 Takuichiro Kendo Method of manufacturing slaked lime containing organic substance

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