JPH047004A - Coagulant and production thereof - Google Patents
Coagulant and production thereofInfo
- Publication number
- JPH047004A JPH047004A JP2106554A JP10655490A JPH047004A JP H047004 A JPH047004 A JP H047004A JP 2106554 A JP2106554 A JP 2106554A JP 10655490 A JP10655490 A JP 10655490A JP H047004 A JPH047004 A JP H047004A
- Authority
- JP
- Japan
- Prior art keywords
- water
- flocculant
- sulfuric acid
- incineration ash
- zinc
- 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
- 238000004519 manufacturing process Methods 0.000 title claims description 7
- 239000000701 coagulant Substances 0.000 title abstract description 4
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 32
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 29
- 239000010813 municipal solid waste Substances 0.000 claims abstract description 23
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims abstract description 22
- 241001465754 Metazoa Species 0.000 claims abstract description 17
- 239000011701 zinc Substances 0.000 claims abstract description 12
- 229910052725 zinc Inorganic materials 0.000 claims abstract description 12
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims abstract description 11
- 238000002156 mixing Methods 0.000 claims abstract description 9
- 239000007788 liquid Substances 0.000 claims abstract 4
- 239000002374 bone meal Substances 0.000 claims description 10
- 229940036811 bone meal Drugs 0.000 claims description 10
- 238000000034 method Methods 0.000 claims description 8
- 238000003756 stirring Methods 0.000 claims description 4
- 239000000376 reactant Substances 0.000 claims description 3
- 239000000706 filtrate Substances 0.000 claims 1
- 238000001914 filtration Methods 0.000 claims 1
- 238000010438 heat treatment Methods 0.000 claims 1
- 210000000988 bone and bone Anatomy 0.000 abstract description 20
- 238000003912 environmental pollution Methods 0.000 abstract description 4
- 239000000203 mixture Substances 0.000 abstract description 2
- 235000002918 Fraxinus excelsior Nutrition 0.000 abstract 4
- 239000002956 ash Substances 0.000 abstract 4
- 239000000843 powder Substances 0.000 description 13
- 229910001385 heavy metal Inorganic materials 0.000 description 9
- 239000002351 wastewater Substances 0.000 description 9
- 239000005416 organic matter Substances 0.000 description 7
- 230000000694 effects Effects 0.000 description 6
- 230000002378 acidificating effect Effects 0.000 description 5
- 230000007935 neutral effect Effects 0.000 description 5
- 239000010802 sludge Substances 0.000 description 4
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 229910052793 cadmium Inorganic materials 0.000 description 3
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 3
- 239000008394 flocculating agent Substances 0.000 description 3
- 239000011148 porous material Substances 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- 231100000331 toxic Toxicity 0.000 description 3
- 230000002588 toxic effect Effects 0.000 description 3
- 241000283690 Bos taurus Species 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 230000002776 aggregation Effects 0.000 description 2
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 description 2
- 235000015278 beef Nutrition 0.000 description 2
- 238000009835 boiling Methods 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- 229910052804 chromium Inorganic materials 0.000 description 2
- 239000011651 chromium Substances 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 239000010794 food waste Substances 0.000 description 2
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 2
- 229910052753 mercury Inorganic materials 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- 239000003921 oil Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000008399 tap water Substances 0.000 description 2
- 235000020679 tap water Nutrition 0.000 description 2
- 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 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 241000283086 Equidae Species 0.000 description 1
- 108010010803 Gelatin Proteins 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 241001494479 Pecora Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 238000004220 aggregation Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910052788 barium Inorganic materials 0.000 description 1
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 1
- 230000015572 biosynthetic process Effects 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
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 229920000159 gelatin Polymers 0.000 description 1
- 239000008273 gelatin Substances 0.000 description 1
- 235000019322 gelatine Nutrition 0.000 description 1
- 235000011852 gelatine desserts Nutrition 0.000 description 1
- 239000003292 glue Substances 0.000 description 1
- 239000004021 humic acid Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000008239 natural water Substances 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 235000012239 silicon dioxide Nutrition 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 210000001519 tissue Anatomy 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 150000003751 zinc Chemical class 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D21/00—Separation of suspended solid particles from liquids by sedimentation
- B01D21/01—Separation of suspended solid particles from liquids by sedimentation using flocculating agents
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は、生ゴミ焼却灰を利用した動物骨含有凝集剤、
及びその製法に関する。Detailed Description of the Invention (Field of Industrial Application) The present invention provides an animal bone-containing flocculant using garbage incineration ash;
and its manufacturing method.
(従来の技術〉
人類が開発した近代産業、工業によって新しい文化が生
み出されているが、その反面、それに伴って自然環境に
大きな影響を与え、自然の浄化作用を越えて自然の破壊
や汚染が発生している。(Conventional technology) A new culture has been created by modern industry and industry developed by mankind, but on the other hand, it has had a great impact on the natural environment, causing destruction and pollution of nature that exceeds the purification effect of nature. It has occurred.
人類が常に健康で文化的な生活を確保するためには、産
業の発達と共にその悪影響を取り除いて生活の発展に適
した新しい環境を作り出していく必要がある6その一番
身近な生活公害の生ゴミ焼却灰処理問題が日本のみなら
ず世界各国の悩みとなっている。In order for humankind to always maintain a healthy and cultured life, it is necessary to remove the negative effects of industrial development and create a new environment suitable for the development of life. The problem of garbage incineration ash disposal is a problem not only in Japan but also in countries around the world.
この生ゴミ焼却灰処理問題については各国の各関係機関
等で色々と研究されているが、抜本的な解決策は見出さ
れていないのが現状である。Various related organizations in various countries are conducting various studies on this issue of garbage incineration ash disposal, but at present no fundamental solution has been found.
一方、廃水中の有機物を凝集させる凝集剤としては従来
、硫酸バンド、塩化アルミニウム、第塩化鉄等が知られ
ている。また、有機物を含む廃水は通常、活性汚泥法に
より処理されてきた。しかしながら、従来の凝集剤はい
ずれも酸性側で反応するものであって処理水が酸性とな
らざるを得す、放流による環境汚染の問題が残されてい
た。On the other hand, sulfuric acid, aluminum chloride, ferric chloride, and the like are conventionally known as flocculants that flocculate organic matter in wastewater. Furthermore, wastewater containing organic matter has usually been treated by an activated sludge method. However, all conventional flocculants react on the acidic side, and the treated water inevitably becomes acidic, leaving the problem of environmental pollution due to discharge.
しかも、上記凝集剤では一般の公共水道水や汚染度の低
い水では反応せず、かなり汚れた廃水に対して機能する
ものであった。また、従来の活性汚泥法では、動物性の
腐敗性有機物を含む廃水をこの活性汚泥法で処理した場
合、これによって得られる処理水の水質は放流すること
ができる基準値を満たすものであるが、PHは酸性、B
OD、CODはともに30〜60ppm程度、臭気が完
全には除去されない等、自然水域に無害であるという意
味においては、必ずしも十分な水質とは言えないもので
あった。また、上記処理水では、工場用水や洗浄用水等
として再利用するには不適であった。さらに、活性汚泥
槽を微生物が繁殖活動できる20〜30℃に保つと同時
に、酸素供給のための曝気が常時必要であり、有機物が
適量に存在しなければならない等の条件整備か必要であ
ると共に、処理時間はかなり長時間を要していた。また
、複雑かつ大規模な設備が必要てあり、設備費は多大で
あり、メンテナンス費用及び労力も過大であった。Moreover, the above-mentioned flocculants did not react with general public tap water or water with a low degree of contamination, but functioned with considerably contaminated wastewater. In addition, in the conventional activated sludge method, when wastewater containing putrefactive organic matter of animal origin is treated with this activated sludge method, the quality of the treated water obtained by this method satisfies the standard value that allows it to be discharged. , PH is acidic, B
Both OD and COD were about 30 to 60 ppm, odor was not completely removed, and the water quality could not necessarily be said to be sufficient in terms of being harmless to natural water bodies. Furthermore, the above-mentioned treated water was not suitable for reuse as factory water, washing water, or the like. Furthermore, it is necessary to maintain conditions such as keeping the activated sludge tank at a temperature of 20 to 30°C where microorganisms can reproduce, and at the same time, aeration is required to supply oxygen at all times, and an appropriate amount of organic matter must be present. , the processing time was quite long. Further, complex and large-scale equipment is required, and the equipment cost is large, and the maintenance cost and labor are also excessive.
(発明が解決しようとする課題)
本発明は、中性ないしアルカリ性で反応して処理水の放
流による環境汚染の虞れを防止し、一般の公共水道水な
いし同程度の水でも反応する高反応性を有すると共に、
従来のものに比して極めて少ない使用量で十分な機能を
発揮し、しかもフロックの形成が早く分離速度の大きい
凝集剤を提供せんとするものである。また本発明は生ゴ
ミ焼却灰を利用することにより生ゴミ焼却灰処理問題を
解決する一つの有力な方法を提供するものである。(Problems to be Solved by the Invention) The present invention aims to prevent the risk of environmental pollution caused by the discharge of treated water by reacting with neutral or alkaline water, and which reacts with general public tap water or water of the same level. Along with having gender,
The purpose of this invention is to provide a flocculant that exhibits sufficient functionality with an extremely small amount used compared to conventional ones, and that forms flocs quickly and has a high separation rate. Furthermore, the present invention provides an effective method for solving the problem of garbage incineration ash disposal by utilizing garbage incineration ash.
(課題を解決するための手段)
本発明は、生ゴミ焼却灰、動物骨粉及び亜鉛を硫酸また
は塩酸、及び水と混合し溶解してなる凝集剤及びその製
法である。(Means for Solving the Problems) The present invention is a flocculant obtained by mixing and dissolving garbage incineration ash, animal bone meal, and zinc with sulfuric acid or hydrochloric acid, and water, and a method for producing the same.
生ゴミは日常生活により排出されるゴミであり、生ゴミ
焼却灰には通常、有機物、強熱減量成分、フミン酸、残
さ(二酸化ケイ素)、金属類及び有害金属、等が含まれ
る。Food waste is waste generated in daily life, and food waste incineration ash usually contains organic matter, ignition loss components, humic acid, residue (silicon dioxide), metals, toxic metals, etc.
本発明の生ゴミ焼却灰としては有害重金属を実質的に含
まない生ゴミ焼却灰が好ましい。この有害重金属を含ま
ない生ゴミ焼却戻粉はアルカリ性であり、生ゴミ焼却戻
粉から有害重金属〈水銀、カドミウム、鉛〉を除いたも
の、または生ゴミを焼却する際に重金属を除去しつつ焼
成して得られた焼成戻粉、例えば重金属を吸着する吸着
材の存在下に水銀、カドミウム、鉛、クロム等を吸着さ
せつつ焼却して得られた焼却圧粉であり、必要に応じク
ロム等を添加したものである。The garbage incineration ash of the present invention is preferably garbage incineration ash that does not substantially contain harmful heavy metals. This garbage incineration return powder, which does not contain toxic heavy metals, is alkaline and is either the garbage incineration return powder from which toxic heavy metals (mercury, cadmium, lead) have been removed, or the garbage that is incinerated while removing heavy metals. For example, mercury, cadmium, lead, chromium, etc. are adsorbed in the presence of an adsorbent that adsorbs heavy metals, and chromium is then incinerated. It was added.
本発明で有害重金属を実質的に含まない生ゴミ焼却灰は
、通常、生ゴミ焼却灰1kg当たり、アルキル水銀0.
05mg以下、カドミウム1mg以下、鉛10mg以下
、六価クロム5mg以下であり、好ましくはこれら重金
属が検出されない焼却圧粉である。In the present invention, the garbage incineration ash that is substantially free of harmful heavy metals usually has 0.00% alkylmercury per 1 kg of garbage incineration ash.
05 mg or less, cadmium 1 mg or less, lead 10 mg or less, and hexavalent chromium 5 mg or less, and preferably the incineration powder contains no detectable heavy metals.
本発明においてはこの焼却灰は、゛通常、硫酸または塩
酸に溶解した形態で凝集剤の原料として用い、動物骨粉
、亜鉛、水と混合して凝集剤を調製する。In the present invention, this incineration ash is normally used as a raw material for a flocculant in the form of a solution dissolved in sulfuric acid or hydrochloric acid, and is mixed with animal bone meal, zinc, and water to prepare the flocculant.
そめ割きは通常、動物骨粉100重量部に対して、焼却
灰は100〜550重量部、好ましくは150〜400
重量部であり、焼却粉の量が100重量部より少ないと
凝集速度を増大させる焼却灰の効果が少なくなり、55
0重量部を越えると動物骨粉による凝集効果が低下する
。Somewari usually contains 100 parts by weight of animal bone powder and 100 to 550 parts by weight of incinerated ash, preferably 150 to 400 parts by weight.
If the amount of incinerated powder is less than 100 parts by weight, the effect of incinerated ash to increase the agglomeration rate will be reduced, and 55
If the amount exceeds 0 parts by weight, the aggregation effect of animal bone powder will decrease.
凝集剤中における動物骨粉と焼却灰の合計量は液中に硫
酸または塩酸の量によって変わるがいずれにしても室温
においてこれらか液中に溶解し得る量以下である。The total amount of animal bone meal and incineration ash in the coagulant will vary depending on the amount of sulfuric acid or hydrochloric acid in the solution, but in any case it will be less than the amount that can be dissolved in the solution at room temperature.
また動物青粉は、従来畜産場等で殆ど廃棄されていた骨
、特に牛、馬、羊等の硬骨が主体の動物の骨が採用され
る。In addition, the animal green powder is made from bones, which have conventionally been mostly discarded at livestock farms, especially bones of animals such as cows, horses, sheep, etc., which are mainly hard bones.
これらの動物の生骨は焼成しやすい大きさに切断し、そ
の上で圧力釜に投入し、200〜400℃前後で、約9
0分前後煮沸する。次いでこの骨を焼成炉に入れ、90
0〜1100℃前後で、60〜180分前後焼成し、そ
のまま炉内で60分前後自然冷却させて室温乃至しこれ
に近い状態に戻す。The raw bones of these animals are cut into sizes that are easy to burn, then put into a pressure cooker and heated at around 200 to 400 degrees Celsius for about 90 minutes.
Boil for about 0 minutes. The bones were then placed in a kiln for 90
It is fired at a temperature of about 0 to 1100° C. for about 60 to 180 minutes, and then allowed to naturally cool in the furnace for about 60 minutes to return to room temperature or a state close to this temperature.
骨に青成分以外のゼラチン、脂肪、蛋白質、にかわ等の
有機物が残存すると酸化腐敗の原因となるので、これを
確実に除去しておくことが重要である。上記煮沸工程に
よって、外側のみならず気孔内に付着している有機物を
骨から大力分離除去することができる。If organic substances other than the blue component, such as gelatin, fat, protein, and glue, remain in the bones, they will cause oxidative decay, so it is important to ensure that they are removed. By the above boiling process, organic matter adhering not only to the outside but also to the inside of the pores can be strongly separated and removed from the bone.
その上で上記焼成工程を通すことによって、残存する有
機物を完全に除去することができ、同時に骨中の湿度(
水分)を数%以下、好ましくはほぼ0%にまで低下させ
ることができる。上記焼成条件によれば、骨は白骨化し
て無数の気孔を有した原形組織状態を維持する。By then passing through the above baking process, remaining organic matter can be completely removed, and at the same time the humidity in the bone can be reduced.
The water content can be reduced to several percent or less, preferably to almost 0%. According to the above-mentioned firing conditions, the bone turns into a skeleton and maintains its original tissue state having countless pores.
上記焼成、冷却後、この骨を破砕し、パウダー機にかけ
て20〜200メツシユ前後、特に好ましくは50〜1
00メツシユの粉状の骨粉とする。After the above-mentioned baking and cooling, the bone is crushed and powdered into powder powder to produce approximately 20 to 200 meshes, particularly preferably 50 to 1 mesh.
00 mesh powdered bone meal.
上記骨粉は、牛骨の場き、原料の生骨に比して重量比的
40%の収量で得られる。粒子は、カルシウム(約33
重量%)を主成分とし、リン(約167%)、バリウム
(約、03%)、ナトリウム(約0.76%)、イオウ
(約0.64%)、他にマグネシウム、カリウム、塩素
、アミン、鉄等からなっており、粒子の内外に渡って無
数の微小気孔が連通存在している。この骨粉はカルシウ
ムを含有するためにアルカリ性である。The above-mentioned bone meal is obtained from bovine bones at a yield of 40% by weight compared to raw raw bones. The particles contain calcium (approximately 33
The main components are phosphorus (approx. 167%), barium (approx. 0.3%), sodium (approx. 0.76%), sulfur (approx. 0.64%), and magnesium, potassium, chlorine, and amines. , iron, etc., and countless microscopic pores exist in communication between the inside and outside of the particles. This bone meal is alkaline because it contains calcium.
動物骨粉そのまま、または硫酸もしくは塩酸の溶液とし
て、他の原料と混合して凝集剤の11i製に用いる。Animal bone meal is used as it is or as a solution of sulfuric acid or hydrochloric acid, mixed with other raw materials to make flocculant 11i.
本発明においては凝集剤の成分の一つとして亜鉛を含有
するが、この亜鉛もそのまま、または硫酸もしくは塩酸
の溶液として用いるが、通常、後者の溶液の状態で使用
する。水は焼却灰等の粉体を溶解したり、濃度を調節す
るために用いる。In the present invention, zinc is contained as one of the components of the flocculant, and this zinc is also used as it is or as a solution in sulfuric acid or hydrochloric acid, but the latter solution is usually used. Water is used to dissolve powder such as incineration ash and adjust its concentration.
本発明の凝集剤は中性ないしアルカリ性で効果的に反応
する。そのためにPHが酸性領域の廃水等に対しては、
これを中性ないしアルカリ性にするために、上記凝集剤
と同時に水酸化ナトリウム、水酸化カルシウム等のアル
カリ性反応剤を廃水に混合して使用するのがよい。また
PHか9.5以上の場合は希硫酸等の酸性反応剤を用い
るのが好ましい。The flocculant of the present invention reacts effectively in neutral to alkaline conditions. Therefore, for wastewater with an acidic pH,
In order to make the wastewater neutral or alkaline, it is preferable to use an alkaline reactant such as sodium hydroxide or calcium hydroxide mixed with the wastewater at the same time as the flocculant. Further, if the pH is 9.5 or higher, it is preferable to use an acidic reactant such as dilute sulfuric acid.
本発明の凝集剤は前記の原料成分を混合し溶解すること
によって得られるが、通常、有害重金属を実質的に含ま
ない生ゴミ焼却灰をTa酸または塩酸に溶解した焼却灰
溶液を得て、この溶液と動物骨粉、亜鉛及び水を混きし
均一化することによってy8!遣する。混合後は、加熱
、撹拌し、次いで瀘過して不溶解分を分離し、溶液を凝
集剤として回収するのが好ましい。The flocculant of the present invention can be obtained by mixing and dissolving the above-mentioned raw material components, but usually, an incineration ash solution is obtained by dissolving garbage incineration ash, which is substantially free of harmful heavy metals, in Ta acid or hydrochloric acid. By mixing and homogenizing this solution with animal bone meal, zinc and water, y8! send After mixing, it is preferable to heat and stir, then filter to separate undissolved components, and recover the solution as a flocculant.
凝集剤の製造の一態様を示すと次のとおりである。有害
重金属を実質的に含まない生ゴミ焼却灰700gを濃硫
酸に溶解し、牛骨粉300g、亜鉛20g (硫酸に溶
解したもの)に水501を加える。水を加えると発熱す
る。180℃で30〜60分、撹拌しながら全体が約I
Kgになるまで煮詰めた後、瀘過し、凝集剤を得る。One aspect of the production of the flocculant is as follows. Dissolve 700 g of garbage incineration ash, which does not substantially contain harmful heavy metals, in concentrated sulfuric acid, and add 50 g of water to 300 g of beef bone powder, 20 g of zinc (dissolved in sulfuric acid). Generates heat when water is added. At 180℃ for 30-60 minutes, while stirring, the whole
After boiling down to kg, it is filtered to obtain a flocculant.
(発明の効果)
本発明の凝集剤は生ゴミ焼却灰を利用するものであり、
生ゴミ焼却灰処理問題を解決する一つの有力な手段とな
り得る。(Effect of the invention) The flocculant of the present invention utilizes garbage incineration ash,
This could be an effective means of solving the problem of garbage incineration ash disposal.
本発明の凝集剤は画期的なものであり、中性ないしアル
カリ性て反応するため処理水の放流による環境汚染のお
それが防止でき、高反応性を有するので一般の公共水道
水ないし同程度の水にも適用でき 従来のものに比して
極めて少ない使用量で十分な機能を発揮し、しかもフロ
7クの形成が早く分離速度が大きい、という閉著な効果
を達成し得る。The flocculant of the present invention is a groundbreaking product, and because it reacts with neutral or alkaline properties, it is possible to prevent the risk of environmental pollution caused by the discharge of treated water. It can also be applied to water, exhibits sufficient functionality with an extremely small amount used compared to conventional products, and achieves remarkable effects such as rapid formation of flocs and high separation speed.
(実施例)
■凝集剤の製造
生ゴミ焼却灰700gを濃硫酸に溶解し、牛骨粉300
g、亜鉛20y(硫酸に溶解したもの)に水5ONを加
えた。水を加えると発熱した。180℃で約45分、撹
拌しながら全体が約1kgになるまで煮詰めた後、濾過
し、凝集剤を得た。(Example) ■Production of flocculant Dissolve 700g of garbage incineration ash in concentrated sulfuric acid, and dissolve 300g of beef bone powder.
50N of water was added to 20y of zinc (dissolved in sulfuric acid). When water was added, it generated heat. The mixture was boiled at 180° C. for about 45 minutes with stirring until the total weight was about 1 kg, and then filtered to obtain a flocculant.
■凝集剤の試験
ガソリンスタンドの排水(洗車後の排水が主体のもの)
を取水し、試験管に8分目位入れ、アルカリ粉末を加え
てPHをほぼ中性にした後、上記凝集剤を1〜2滴加え
、振り混ぜたところ、凝集剤添加の10秒後にはフロッ
クが生成し、それとほぼ同時に試験管の上部に油とフロ
ック、下部に水層が分離した。■Flocculant testing Gas station wastewater (mainly wastewater from car washes)
After taking the water and putting it into a test tube for about 8 minutes, adding alkali powder to make the pH almost neutral, I added 1 to 2 drops of the above flocculant and shook it. 10 seconds after adding the flocculant, Flocs were formed, and almost at the same time, oil and flocs separated from the top of the test tube, and a water layer separated from the bottom.
比較のため、上記の凝集剤の代わりに硫酸バンドを加え
て振り混ぜたところ、フロックの形成に30秒を要し、
次いで分離に30分を要し、上部に油、中間分に水層、
下部にフロックが分離した。For comparison, when we added sulfuric acid band instead of the above flocculant and mixed it by shaking, it took 30 seconds to form flocs.
Next, it takes 30 minutes to separate, with oil on the top and water layer in the middle.
The flocs were separated at the bottom.
Claims (4)
、及び水と混合し溶解してなる凝集剤。(1) A flocculant made by mixing and dissolving garbage incineration ash, animal bone meal, and zinc with sulfuric acid or hydrochloric acid, and water.
リ性反応剤を添加した上で使用することを特徴とする請
求項(1)記載の凝集剤の使用方法。(2) A method for using the flocculant according to claim (1), characterized in that the flocculant according to claim (1) is used as a treatment liquid and an alkaline reactant is added thereto.
液を得、この溶液と動物骨粉、亜鉛及び水を混合し均一
化することを特徴とする凝集剤の製法。(3) A method for producing a flocculant, which comprises obtaining an incineration ash solution by dissolving garbage incineration ash in sulfuric acid or hydrochloric acid, and mixing and homogenizing this solution with animal bone meal, zinc, and water.
集剤として回収する請求項(3)記載の凝集剤の製法。(4) The method for producing a flocculant according to claim (3), wherein after mixing, heating and stirring are performed, followed by filtration and the filtrate is recovered as a flocculant.
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2106554A JP2532293B2 (en) | 1990-04-24 | 1990-04-24 | Flocculant and manufacturing method thereof |
KR1019900008074A KR910018057A (en) | 1990-04-24 | 1990-05-31 | Flocculant, preparation method thereof and method of use |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2106554A JP2532293B2 (en) | 1990-04-24 | 1990-04-24 | Flocculant and manufacturing method thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH047004A true JPH047004A (en) | 1992-01-10 |
JP2532293B2 JP2532293B2 (en) | 1996-09-11 |
Family
ID=14436557
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2106554A Expired - Lifetime JP2532293B2 (en) | 1990-04-24 | 1990-04-24 | Flocculant and manufacturing method thereof |
Country Status (2)
Country | Link |
---|---|
JP (1) | JP2532293B2 (en) |
KR (1) | KR910018057A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006524537A (en) * | 2003-03-12 | 2006-11-02 | スリーエム イノベイティブ プロパティズ カンパニー | POLYMER COMPOSITION, MEDICAL ARTICLE, AND METHOD CONTAINING BIOLOGICALLY ACTIVE SILVER, COPPER OR ZINC COMPOUND |
US7666311B2 (en) | 2005-12-26 | 2010-02-23 | Eccera Co., Ltd. | Flocculating agent |
FR2950619A1 (en) * | 2009-09-25 | 2011-04-01 | Serge Ferlay | PROCESS FOR DEULFATATION OF ACID RELEASES FROM THE TITANIUM INDUSTRY |
JP2012250225A (en) * | 2011-06-07 | 2012-12-20 | Horibe Yoshikazu | Method for treating palm waste oil |
-
1990
- 1990-04-24 JP JP2106554A patent/JP2532293B2/en not_active Expired - Lifetime
- 1990-05-31 KR KR1019900008074A patent/KR910018057A/en not_active Application Discontinuation
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006524537A (en) * | 2003-03-12 | 2006-11-02 | スリーエム イノベイティブ プロパティズ カンパニー | POLYMER COMPOSITION, MEDICAL ARTICLE, AND METHOD CONTAINING BIOLOGICALLY ACTIVE SILVER, COPPER OR ZINC COMPOUND |
US7666311B2 (en) | 2005-12-26 | 2010-02-23 | Eccera Co., Ltd. | Flocculating agent |
FR2950619A1 (en) * | 2009-09-25 | 2011-04-01 | Serge Ferlay | PROCESS FOR DEULFATATION OF ACID RELEASES FROM THE TITANIUM INDUSTRY |
JP2012250225A (en) * | 2011-06-07 | 2012-12-20 | Horibe Yoshikazu | Method for treating palm waste oil |
Also Published As
Publication number | Publication date |
---|---|
JP2532293B2 (en) | 1996-09-11 |
KR910018057A (en) | 1991-11-30 |
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