JPS6236094A - Bad smell reducing method - Google Patents
Bad smell reducing methodInfo
- Publication number
- JPS6236094A JPS6236094A JP60085693A JP8569385A JPS6236094A JP S6236094 A JPS6236094 A JP S6236094A JP 60085693 A JP60085693 A JP 60085693A JP 8569385 A JP8569385 A JP 8569385A JP S6236094 A JPS6236094 A JP S6236094A
- Authority
- JP
- Japan
- Prior art keywords
- fertilizer
- odor
- waste liquid
- organic
- bad
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 238000000034 method Methods 0.000 title claims description 33
- 239000003337 fertilizer Substances 0.000 claims description 50
- 239000006227 byproduct Substances 0.000 claims description 13
- 150000002894 organic compounds Chemical class 0.000 claims description 11
- 235000013311 vegetables Nutrition 0.000 claims description 10
- 238000005469 granulation Methods 0.000 claims description 7
- 230000003179 granulation Effects 0.000 claims description 7
- 230000036571 hydration Effects 0.000 claims description 5
- 238000006703 hydration reaction Methods 0.000 claims description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 4
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 4
- 239000002994 raw material Substances 0.000 claims description 4
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 claims description 3
- 239000011591 potassium Substances 0.000 claims description 3
- 229910052700 potassium Inorganic materials 0.000 claims description 3
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims description 2
- 229910052757 nitrogen Inorganic materials 0.000 claims description 2
- 235000019645 odor Nutrition 0.000 description 56
- 239000007788 liquid Substances 0.000 description 26
- 239000000126 substance Substances 0.000 description 23
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical group CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 20
- 239000002921 fermentation waste Substances 0.000 description 18
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 15
- 238000004519 manufacturing process Methods 0.000 description 10
- 239000007789 gas Substances 0.000 description 9
- 150000007524 organic acids Chemical class 0.000 description 9
- 239000002699 waste material Substances 0.000 description 7
- 235000005985 organic acids Nutrition 0.000 description 5
- 235000011121 sodium hydroxide Nutrition 0.000 description 5
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 4
- 230000001580 bacterial effect Effects 0.000 description 4
- 235000013379 molasses Nutrition 0.000 description 4
- 239000000047 product Substances 0.000 description 4
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- 230000001476 alcoholic effect Effects 0.000 description 3
- -1 amine compounds Chemical class 0.000 description 3
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 3
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 3
- 235000011130 ammonium sulphate Nutrition 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000000855 fermentation Methods 0.000 description 3
- 230000004151 fermentation Effects 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- QJZYHAIUNVAGQP-UHFFFAOYSA-N 3-nitrobicyclo[2.2.1]hept-5-ene-2,3-dicarboxylic acid Chemical compound C1C2C=CC1C(C(=O)O)C2(C(O)=O)[N+]([O-])=O QJZYHAIUNVAGQP-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 239000004254 Ammonium phosphate Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
- 229910000148 ammonium phosphate Inorganic materials 0.000 description 2
- 235000019289 ammonium phosphates Nutrition 0.000 description 2
- 230000001877 deodorizing effect Effects 0.000 description 2
- 238000001514 detection method Methods 0.000 description 2
- MNNHAPBLZZVQHP-UHFFFAOYSA-N diammonium hydrogen phosphate Chemical compound [NH4+].[NH4+].OP([O-])([O-])=O MNNHAPBLZZVQHP-UHFFFAOYSA-N 0.000 description 2
- 230000002349 favourable effect Effects 0.000 description 2
- 239000004021 humic acid Substances 0.000 description 2
- 150000002681 magnesium compounds Chemical class 0.000 description 2
- 238000000691 measurement method Methods 0.000 description 2
- 230000003472 neutralizing effect Effects 0.000 description 2
- 125000001477 organic nitrogen group Chemical group 0.000 description 2
- 230000020477 pH reduction Effects 0.000 description 2
- 230000002265 prevention Effects 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 206010052804 Drug tolerance Diseases 0.000 description 1
- 241000208125 Nicotiana Species 0.000 description 1
- 235000002637 Nicotiana tabacum Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 235000012538 ammonium bicarbonate Nutrition 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- QLULGSLAHXLKSR-UHFFFAOYSA-N azane;phosphane Chemical compound N.P QLULGSLAHXLKSR-UHFFFAOYSA-N 0.000 description 1
- 239000002374 bone meal Substances 0.000 description 1
- 229940036811 bone meal Drugs 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229940043430 calcium compound Drugs 0.000 description 1
- 150000001674 calcium compounds Chemical class 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- YYRMJZQKEFZXMX-UHFFFAOYSA-N calcium;phosphoric acid Chemical compound [Ca+2].OP(O)(O)=O.OP(O)(O)=O YYRMJZQKEFZXMX-UHFFFAOYSA-N 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000009841 combustion method Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 230000000295 complement effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000004332 deodorization Methods 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 230000026781 habituation Effects 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 description 1
- 239000000347 magnesium hydroxide Substances 0.000 description 1
- 229910001862 magnesium hydroxide Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000009965 odorless effect Effects 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 235000011118 potassium hydroxide Nutrition 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 230000001953 sensory effect Effects 0.000 description 1
- 230000008786 sensory perception of smell Effects 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 235000013555 soy sauce Nutrition 0.000 description 1
- 239000002426 superphosphate Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 230000005068 transpiration Effects 0.000 description 1
- 238000010792 warming Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
Landscapes
- Fertilizers (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
〔産業上の利用分野〕
この発明は、有機化成肥料製造時に発生する悪臭を低減
させるための悪臭低減方法に関するもので、さらに詳し
くは各種産業において副生じ、肥料としての利用が可能
な植物質副産物、いわゆる副産植物質肥料を使用した際
に、該副産植物質肥料そのもの、または有機化成肥料の
PH1i整管理することで発生する臭気濃度を低減せし
めることを目的とするものである。[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a method for reducing bad odors generated during the production of organic chemical fertilizers. The purpose is to reduce the odor concentration generated by controlling the PH1i of the by-product vegetable fertilizer itself or organic compound fertilizer when using available vegetable by-products, so-called by-product vegetable fertilizers. It is something to do.
有機化成肥料製造時には、一般に悪臭の発生が伴い、か
\る悪臭発生が公害問題となり、発生企業は長年に亘り
この脱臭対策について種々検討を行ってきた。The production of organic chemical fertilizers is generally accompanied by the generation of foul odors, and the generation of such foul odors has become a pollution problem, and companies that generate such odors have been conducting various studies for many years on measures to eliminate this odor.
一般に有機化成肥料の悪臭源である副産植物質肥料は、
主として食品工業又は発酵工業において副産されるもの
であって、素材は植物質原料から由来するものであり、
これらには醤油粕肥料、煙草屑肥料、アミノ酸副産肥料
、乾燥菌体肥料、発酵副産肥料等が知られているが、代
表的な例として廃糖蜜アルコール発酵廃液を挙げること
ができる。By-product vegetable fertilizers, which are generally the source of bad odors in organic chemical fertilizers, are
It is mainly a by-product in the food industry or fermentation industry, and the material is derived from vegetable raw materials.
Known examples of these include soy sauce lees fertilizer, tobacco waste fertilizer, amino acid by-product fertilizer, dried bacterial cell fertilizer, and fermentation by-product fertilizer, among which a representative example is molasses alcohol fermentation waste liquid.
これは糖蜜液に重炭酸アンモニウム等を加え・発酵濃縮
後、粗油アルコールを分離した後の残渣が廃糖蜜アルコ
ール発酵廃液であり、有機質の窒素、加里を含むいわゆ
る副産植物質肥料である。The residue after adding ammonium bicarbonate, etc. to the molasses liquid, fermenting and concentrating it, and separating the crude oil alcohol is the molasses alcohol fermentation waste liquid, which is a so-called by-product vegetable fertilizer containing organic nitrogen and potassium.
この肥料は、有機質の窒素、加里を含有しているため、
格好の有機質原料として肥料業界では、有効に利用され
ている。This fertilizer contains organic nitrogen and potassium,
It is effectively used in the fertilizer industry as an excellent organic raw material.
しかして、化成肥料の製造は、窒素、りん酸および加工
の三つの肥料原料を適正組成に設定し、これにアンモニ
ア、硫酸などを添加し、化学的操作を加えて造粒、乾燥
、冷却、篩分けなどおこなって製造するもので、この造
粒工程において、前記の廃糖蜜アルコール発酵廃液を添
加して有機化成肥料を製造している。Therefore, in the production of chemical fertilizers, the three fertilizer raw materials (nitrogen, phosphoric acid, and processing) are set to an appropriate composition, ammonia, sulfuric acid, etc. are added to this, and chemical operations are applied to granulate, dry, cool, and It is produced by sieving, etc., and in this granulation process, the above-mentioned molasses alcohol fermentation waste liquid is added to produce an organic chemical fertilizer.
ところが、この廃糖蜜アルコール発酵廃液は、常温では
有機酸独特の悪臭はさほど感じないものであるが、夏期
など長期にわたって保管にすることにより発酵したり、
肥料としての工程で硫酸と反応させるとともに、乾燥用
ガスで加熱されることによって、悪臭成分である各種有
機酸が気化して大気中に放出され、これが悪臭の原因と
なっている。However, although this molasses alcoholic fermentation waste liquid does not have much of the odor characteristic of organic acids at room temperature, it may ferment if stored for a long period of time, such as during the summer.
When it is reacted with sulfuric acid during the fertilizer process and heated with drying gas, various organic acids, which are bad-smelling components, are vaporized and released into the atmosphere, which causes bad odors.
か−る悪臭の脱臭にはガス洗滌法、吸着法、燃焼法、酸
化法などが公知であり、実施によってそれなりの効果を
あげている。Gas washing methods, adsorption methods, combustion methods, oxidation methods, and the like are well known methods for deodorizing such bad odors, and these methods have achieved certain effects when practiced.
〔発明が解決しようとする問題点〕
悪臭の脱臭法としての、前記の各方法は、いずれも大規
模な装置を必要とし、特にこれらのうちの後二者に属す
るものは、処理費用が嵩み経済面で問題があり、前者も
このもののみで処理を行えば一応の効果は認められるも
の\、未だ完全なものとは言えない。[Problems to be Solved by the Invention] Each of the above-mentioned methods for deodorizing bad odors requires large-scale equipment, and the latter two methods in particular have high processing costs. There is a problem in terms of economics, and although the former can be seen to be somewhat effective if treated with only this product, it cannot be said to be perfect yet.
さらに、悪臭は感覚公害であるため主観的要素が強く、
人間の臭覚には慣れ、疲労、個人の生活環境で多少異な
る。Furthermore, bad odor is a sensory pollution and has a strong subjective element.
Humans' sense of smell differs slightly depending on habituation, fatigue, and individual living environment.
したがって、被害地域の住民の期待は悪臭の多少でなく
、臭うか、臭わないかである。Therefore, the expectations of residents in the affected areas are not whether there is a bad odor, but whether there is a bad odor or not.
それ故、普通悪臭はかなり除去しても人間の感覚ではそ
れ程減少、軽減したように感じられないものである。。Therefore, even if bad odor is removed to a large extent, it does not seem to have been reduced or alleviated to the human senses. .
これについては、ウェーバ−・フェヒナーの法則、スチ
ープンスの理論などが知られている。Regarding this, the Weber-Fechner law and Steepens' theory are known.
しかして、被害としての悪臭を表わす尺度としては嫌悪
性表示が基本であり、この発明の発明者等は脱臭効率の
判断基準として臭気濃度で表示するのが適切であるとい
うことで、三点比較式臭突法による臭気濃度を測定の目
安として悪臭発生原因およびその排除について鋭意検討
の結果、悪臭の原因は通称フミン酸といわれる有機酸に
あることを知った。However, the aversiveness indication is the basic measure for expressing the bad odor as damage, and the inventors of this invention believe that it is appropriate to indicate the odor concentration as a criterion for determining deodorization efficiency, and compared the three points. As a result of intensive investigation into the causes of malodors and their elimination using the odor concentration measured using the odor bombardment method, we learned that the cause of malodors is an organic acid commonly known as humic acid.
そして、引続いてこのフミン酸悪臭を経済的および工程
的に安価かつ容易な方法で低減し得る方法をについて研
究試験の結果、この発明を完成するに至った。Subsequently, the present invention was completed as a result of research and testing on a method that can reduce this humic acid malodor in an economical and process-wise inexpensive and easy method.
なお、前記の三点比較式臭突法は、無臭空気を入れた3
側御組のプラスチック袋の一個に問題となった原奥を注
入し、判定員が他の無臭の袋と区別ができなくなる迄原
臭気を薄めていきその薄め倍数(希釈倍数)を求める方
法であり、機器測定法のみに鎖ったこれまでの悪臭測定
法の盲点を補完できるものとして近年注目されているも
のである。Note that the three-point comparison odor detection method described above uses three
This method involves injecting the problematic Haraoku into one of the plastic bags in the side, diluting the original odor until the judge can no longer distinguish it from other odorless bags, and calculating the dilution factor. This method has attracted attention in recent years as a method that can complement the blind spots of conventional odor measurement methods, which are limited to instrumental measurement methods.
この発明は、有機化成肥料の製造時において発生する悪
臭を製造工程中のPHを管理することにより低減させる
方法であって、窒素、りん酸および加工質肥料等に、有
機質原料として副産植物質肥料を加えて有機化成肥料を
製造するにあたり、造粒工程以前において該有機化成肥
料の水和時のPHを4.5以上6.5未満に調整するこ
とを特徴とするものである。This invention is a method for reducing the bad odor generated during the production of organic chemical fertilizers by controlling the pH during the production process. In producing an organic compound fertilizer by adding fertilizer, the pH of the organic compound fertilizer during hydration is adjusted to 4.5 or more and less than 6.5 before the granulation step.
以下、副産植物質肥料要素として不快感のきわめて強い
悪臭を発する廃糖蜜アルコール発酵廃液を使用した有機
化成肥料製造時の悪臭除去について詳述する。The following describes in detail the removal of bad odors during the production of organic chemical fertilizers using molasses alcohol fermentation waste liquid, which emits extremely unpleasant bad odors, as a by-product vegetable fertilizer element.
この発明は、有機化成肥料の製造時における造粒工程以
前における有機化成肥料の水和時のPHを所定の範囲に
コントロールするものであるが、そのコントロールは造
粒工程以前の如何なる工程であってもよい。This invention is to control the pH during hydration of an organic compound fertilizer to a predetermined range before the granulation step during production of the organic compound fertilizer, but the control is not performed at any step before the granulation step. Good too.
ただし、より有効なコントロールは廃糖蜜アルコール発
酵廃液について所要のPHコントロールを行うことであ
る。However, a more effective control is to perform the required pH control on the waste liquid of molasses alcohol fermentation.
この廃糖蜜アルコール発酵廃液の臭気濃度は、加温ない
し加熱することにより通常1 、000〜3,000で
あり、保管条件によっては、3,000以上のケースも
あり、かつ可成りの悪臭である。The odor concentration of this molasses alcohol fermentation waste liquid is usually 1,000 to 3,000 when heated, and depending on the storage conditions, it can exceed 3,000 in some cases, and it has a considerable odor. .
また、P旧よほぼ4.8〜5.4の範囲で変動している
。In addition, compared to the old P, it fluctuates in the range of approximately 4.8 to 5.4.
か\る廃糖蜜アルコール発酵廃液のPHを5.5以上6
.5未満に調整する方法は、簡単且つ経済的であり、そ
れは後述するごとくアルカリ成分を添加することである
。この場合、アルカリ成分は化成肥料主成分中へ予め混
合しておくことも可能である。The pH of the molasses alcohol fermentation waste liquid is 5.5 or higher 6
.. A simple and economical method for adjusting the molecular weight to less than 5 is to add an alkaline component as described below. In this case, the alkaline component can be mixed in advance into the main component of the chemical fertilizer.
廃糖蜜アルコール発酵廃液に添加するアルカリ性物質と
しては、−酸基アルカリの可溶の苛性ソーダ、または苛
性カリの添加が好ましい。As the alkaline substance to be added to the molasses alcohol fermentation waste liquid, it is preferable to add -acid group-alkali soluble caustic soda or caustic potash.
また、その他のアルカリ性物質、例えば水酸化マグネシ
ウム、水酸化カルシウム、酸化カルシウム等を固形物と
して添加することも可能である。It is also possible to add other alkaline substances, such as magnesium hydroxide, calcium hydroxide, calcium oxide, etc., as a solid substance.
しかしながら、前記アルカリ性物質中、カルシウム化合
物、マグネシウム化合物の添加は、有機酸と反応して沈
澱物を作るものもあり、この処理が面倒な場合もある。However, the addition of calcium compounds and magnesium compounds among the alkaline substances may react with organic acids to form precipitates, and this treatment may be troublesome.
か−る時は、化成肥料製造の造粒工程前において、カル
シウム、マグネシウム化合物等を添加しておけば解決す
ることができる。This problem can be solved by adding calcium, magnesium compounds, etc. before the granulation process of chemical fertilizer production.
この発明の方法は、前記したPHの調整を単独で行って
よいことは勿論であるが、先に述べたガス洗浄法や吸着
法との組合せにおいて実施してもよい。Of course, the method of the present invention may be used to adjust the pH described above alone, but it may also be carried out in combination with the gas cleaning method or adsorption method described above.
前記のとおり、廃糖蜜アルコール発酵廃液の臭気濃度は
加温ないし加熱することにより、通常1゜000〜3,
000であり、保管条件によっては、3,000以上と
もなり、且つ可成りの悪臭である。As mentioned above, the odor concentration of molasses alcoholic fermentation waste liquid can be reduced by warming or heating, usually from 1°000 to 3,000°C.
000, and depending on storage conditions, it can reach 3,000 or more, and has a considerable odor.
また、pHは4.8〜5.4位に変動しており、発明者
等はこのPRの変位は主としてアミン化合物と有機酸の
夫々の量に起因するものと考え、これを中和によりPH
値を変化させたとき悪臭がどのように変化するかを検討
した。In addition, the pH fluctuates from 4.8 to 5.4, and the inventors believe that this change in PR is mainly due to the respective amounts of amine compounds and organic acids, and by neutralizing this, the pH changes.
We investigated how the odor changes when the value is changed.
すなわち、廃糖蜜アルコール発酵廃液のPHに対応した
苛性ソーダの量を種々変えて添加し、発生させた悪臭ガ
スを三点比較式臭突法による臭気濃度の測定を行って、
最も臭気濃度が低いときの最適PH値を詳細に検討した
。That is, various amounts of caustic soda corresponding to the pH of the molasses alcohol fermentation waste liquid were added, and the odor concentration of the generated foul-smelling gas was measured using a three-point comparative odor detection method.
The optimum pH value when the odor concentration is the lowest was investigated in detail.
その結果、廃糖蜜アルコール発酵廃液を直接中和する場
合は、PH6,5を最大として高目がよく、この値を超
えるとアミン化合物の発生により悪臭の発生が増すよう
になり、排気ガスの臭気濃度はこの最適点では従来に比
べ50%以上低減できることが可能となった。As a result, when directly neutralizing molasses alcoholic fermentation waste liquid, it is best to set the pH to a maximum of 6.5; if this value is exceeded, the generation of amine compounds will increase the generation of bad odors, and the odor of exhaust gas will increase. At this optimum point, the concentration can be reduced by more than 50% compared to the conventional method.
そして、廃糖蜜アルコール発酵廃液のpHを5.5以上
6.5未満の範囲とすることにより、悪臭の発生が低減
したが、これは有機酸の蒸散が著しく低下するために悪
臭が低下するものと推測される。By adjusting the pH of the molasses alcohol fermentation waste liquid to a range of 5.5 or more and less than 6.5, the occurrence of bad odors was reduced, but this is because the transpiration of organic acids is significantly reduced. It is assumed that.
一方、そのPHが6.5以上となると有機酸と塩を作っ
ているアミン化合物が蒸散し、これが悪臭発生の原因と
なっているものと考えられる。On the other hand, when the pH is 6.5 or more, the amine compound forming the salt with the organic acid evaporates, which is thought to be the cause of the bad odor.
また、PH5,5未満の場合も悪臭の低減効果は薄く、
この発明の目的に沿うものではない。Also, if the pH is less than 5.5, the odor reduction effect is weak.
This does not meet the purpose of this invention.
なお、化成肥料等の固形物のPHの測定は、試料5gを
500m j!のメスフラスコに正確にとり、本釣40
0Illを加え、1分間30〜40回回転の振り混ぜ機
で80分間振り混ぜたのち、標線まで水を加えて直ちに
乾燥濾紙で濾過した液のPHを測定したものである。In addition, when measuring the PH of solid substances such as chemical fertilizers, 5 g of sample is heated at 500 m j! Accurately put it in a volumetric flask and make 40
After adding 0Ill and shaking for 80 minutes using a shaker that rotates 30 to 40 times per minute, water was added up to the marked line and immediately filtered through dry filter paper, and the pH of the liquid was measured.
以下、実施例を掲げてこの発明をより具体的に説明する
。なお、実施例中の「部」とあるのは「重量部」である
。Hereinafter, this invention will be described in more detail with reference to Examples. Note that "parts" in the examples are "parts by weight."
実施■」
硫安(硫酸アンモニウム)340部、りん安(燐酸アン
モニウム)40部、過りん酸石灰370部、塩化加工1
34部、乾燥菌体肥料68部、副産植物質肥料(廃糖蜜
アルコール発酵廃液)100部を用いて有機化成肥料を
製造した。Implementation ■ 340 parts of ammonium sulfate (ammonium sulfate), 40 parts of ammonium phosphate (ammonium phosphate), 370 parts of lime superphosphate, chloride treatment 1
An organic chemical fertilizer was produced using 34 parts of the dried bacterial fertilizer, 68 parts of the dried bacterial fertilizer, and 100 parts of the by-product vegetable fertilizer (molasses alcohol fermentation waste liquid).
これに使用した廃糖蜜アルコール発酵廃液のPHは5.
3、臭気濃度は2.550であった。The pH of the molasses alcohol fermentation waste liquid used for this was 5.
3. The odor concentration was 2.550.
この廃糖蜜アルコール廃液に12.5%苛性ソーダ8部
を添加し、PH6,5に調整し前記のとおり操業した。8 parts of 12.5% caustic soda was added to this molasses alcohol waste liquid, the pH was adjusted to 6.5, and the operation was carried out as described above.
この結果、処理前の廃糖蜜アルコール廃液の臭気濃度2
,550および排気ガスの臭気濃度170が処理後、廃
糖蜜アルコール廃液の臭気濃度1.1800、排気ガス
の臭気濃度が80となって、工場周辺の臭気もなくなり
有機酸による不快感は消失した。As a result, the odor concentration of the molasses alcohol waste liquid before treatment was
, 550 and the odor concentration of the exhaust gas became 170. After the treatment, the odor concentration of the waste molasses alcohol waste liquid became 1.1800 and the odor concentration of the exhaust gas became 80. The odor around the factory also disappeared and the unpleasant feeling caused by the organic acid disappeared.
また、かくて得た製品有機化成肥料はそのPHが4.2
から5.4に上昇しているので、肥料による土壌の酸性
化を嫌う需要者にとって好ましい結果を与えることがで
きるものである。In addition, the product organic chemical fertilizer thus obtained has a pH of 4.2.
This has increased from 5.4 to 5.4, which can provide favorable results for users who dislike soil acidification due to fertilizers.
なお、化成肥料等の固形物のPl+の測定は、試料5g
を50On+ 42のメスフラスコに正確にとり、本釣
40Oraltを加え、1分間30〜40回回転の振り
混ぜ機で30分間振り混ぜたのぢ、標線まで水を加えて
直ちに乾燥濾紙で濾過した液のPHを測定した。In addition, when measuring Pl+ in solid substances such as chemical fertilizers, 5g of sample is used.
Accurately put the solution into a 50On+42 volumetric flask, add Honsuri 40Oralt, shake it for 30 minutes with a shaker that rotates 30 to 40 times per minute, add water up to the marked line, and immediately filter the liquid with dry filter paper. The pH of the sample was measured.
去用■」
硫安430部、りん安150部、塩化加工185部、乾
燥菌体肥料150部、蒸製骨粉10部、副産植物質肥料
(廃糖蜜アルコール発酵廃液)140部で有機化成肥料
を製造した。Organic chemical fertilizer is manufactured using 430 parts of ammonium sulfate, 150 parts of ammonium phosphorus, 185 parts of chloride processing, 150 parts of dried bacterial fertilizer, 10 parts of steamed bone meal, and 140 parts of by-product vegetable fertilizer (molasses alcohol fermentation waste liquid). did.
この時の廃糖蜜アルコール発酵廃液のPHは5.2であ
り、廃液の臭気濃度は3,740 、排気ガス臭気濃度
は120であった。At this time, the pH of the molasses alcohol fermentation waste liquid was 5.2, the odor concentration of the waste liquid was 3,740, and the odor concentration of the exhaust gas was 120.
これに11%苛性ソーダ10部添加とPH6,0に調整
した。この結果、苛性ソーダ添加後の廃糖蜜アルコール
発酵廃液臭気濃度はL740 、排ガス臭気濃度50と
半減し、製品PHも5.4から6.5に上昇し、これは
肥料の施用面でも好ましいものである。To this was added 10 parts of 11% caustic soda and the pH was adjusted to 6.0. As a result, the odor concentration of the molasses alcohol fermentation waste liquid after addition of caustic soda was halved to L740 and exhaust gas odor concentration was 50, and the product pH increased from 5.4 to 6.5, which is favorable in terms of fertilizer application. .
また、この工場の周辺における「におい」のモニター数
十人の報告により、主要臭気源側に記録を集計している
が、昭和58年10月より昭和58年9月に至る約−年
間において肥料臭であると報告があった件数は12件あ
り、そのうち、この発明の悪臭低減方法の実施前は10
件であったものが、実施後は2件と激減した。In addition, we have compiled records of major odor sources based on reports from dozens of odor monitors in the vicinity of this factory. There were 12 cases where odor was reported, of which 10 were reported before the implementation of the odor reduction method of this invention.
After implementation, the number of cases decreased sharply to two.
以上述べたようにこの発明によれば、有機化成肥料製造
における造粒工程以前において有機化成肥料の水和時の
円1を所定の範囲内にコントロールすること、とくに有
機酸等を含有している廃糖蜜アルコール発酵廃液の如き
副産有機質肥料物質にアルカリ性物質を添加し、PHを
所定の範囲に調整管理することによって、簡易且つ経済
的に悪臭を低減することが可能となり、公害防止関連技
術として有効かつ価値ある発明である。As described above, according to the present invention, it is possible to control the circle 1 at the time of hydration of the organic compound fertilizer within a predetermined range before the granulation process in the production of the organic compound fertilizer, and in particular, to control the circle 1 during hydration of the organic compound fertilizer, which contains an organic acid, etc. By adding an alkaline substance to by-product organic fertilizer substances such as molasses alcohol fermentation waste liquid and controlling the pH within a predetermined range, it is possible to easily and economically reduce bad odors, and this technology has been developed as a technology related to pollution prevention. It is an effective and valuable invention.
また、この発明によれば得られた製品としての有機化成
肥料は、そのpHが上昇して酸性の度合を低くする方向
に移行するが、これは肥料の施用面で土壌の酸性化を防
ぐことができて好ましいものであり、この点においても
この発明の方法は利用価値大なるものである。Further, according to the present invention, the pH of the organic compound fertilizer obtained as a product increases and the degree of acidity decreases, but this is because the acidification of the soil is prevented when applying the fertilizer. The method of the present invention has great utility value in this respect as well.
特 許 出 願 人 トーア化成 株式会社手続ネ甫
正書(方式)
%式%
1、事件の表示
昭和60年特 許 願第85693号
2、発明の名称
悪臭低減方法
3、補正をする者
事件との関係 特許出願人
昭和61年 8月26日(発送日)
6、補正の対象
明細書の「発明の名称」の欄
7、補正の内容
(1)明細書第1頁の発明の名称として「悪臭低減方法
(公害防止関連技術)」とあるを「悪臭低減方法」と補
正する。Patent applicant Toa Kasei Co., Ltd. Procedure Neho Seisho (Method) % formula % 1. Indication of the case 1985 Patent Application No. 85693 2. Name of the invention Offensive odor reduction method 3. Person making the amendment Case and Relationship between Patent applicant August 26, 1988 (shipping date) 6. Column 7 of "Title of the invention" of the specification subject to amendment, Contents of the amendment (1) As the title of the invention on page 1 of the specification, " The phrase ``Offensive odor reduction method (pollution prevention related technology)'' will be corrected to ``Offensive odor reduction method.''
Claims (1)
副産植物質肥料を加えて有機化成肥料を製造するにあた
り、造粒工程以前において該有機化成肥料の水和時のP
Hを4.5以上6.5未満に調整することを特徴とする
悪臭低減方法。When producing organic compound fertilizer by adding by-product vegetable fertilizer as an organic raw material to nitrogen, phosphoric acid, potassium fertilizer, etc., P during hydration of the organic compound fertilizer is determined before the granulation process.
A method for reducing bad odor, comprising adjusting H to 4.5 or more and less than 6.5.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60085693A JPS6236094A (en) | 1985-04-22 | 1985-04-22 | Bad smell reducing method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60085693A JPS6236094A (en) | 1985-04-22 | 1985-04-22 | Bad smell reducing method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6236094A true JPS6236094A (en) | 1987-02-17 |
| JPH0248520B2 JPH0248520B2 (en) | 1990-10-25 |
Family
ID=13865912
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60085693A Granted JPS6236094A (en) | 1985-04-22 | 1985-04-22 | Bad smell reducing method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6236094A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101781138A (en) * | 2010-03-19 | 2010-07-21 | 云南省轻工业科学研究院 | Method for preparing nitrogen-potassium binary compound fertilizer by using molasses-alcoholic waste fermented liquid |
| CN101830734A (en) * | 2010-03-19 | 2010-09-15 | 云南省轻工业科学研究院 | Method for preparing potash fertilizer by using molasses alcohol waste mash |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0924931A (en) * | 1995-07-11 | 1997-01-28 | Ogura Bijutsu Insatsu Kk | Packaging box for bottles |
-
1985
- 1985-04-22 JP JP60085693A patent/JPS6236094A/en active Granted
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101781138A (en) * | 2010-03-19 | 2010-07-21 | 云南省轻工业科学研究院 | Method for preparing nitrogen-potassium binary compound fertilizer by using molasses-alcoholic waste fermented liquid |
| CN101830734A (en) * | 2010-03-19 | 2010-09-15 | 云南省轻工业科学研究院 | Method for preparing potash fertilizer by using molasses alcohol waste mash |
| CN101830734B (en) | 2010-03-19 | 2012-07-04 | 云南省轻工业科学研究院 | Method for preparing potash fertilizer by using molasses alcohol waste mash |
| CN101781138B (en) | 2010-03-19 | 2012-07-04 | 云南省轻工业科学研究院 | Method for preparing nitrogen-potassium binary compound fertilizer by using molasses-alcoholic waste fermented liquid |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0248520B2 (en) | 1990-10-25 |
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