JPS5918365B2 - Red tide treatment agent and its manufacturing method - Google Patents

Red tide treatment agent and its manufacturing method

Info

Publication number
JPS5918365B2
JPS5918365B2 JP13196781A JP13196781A JPS5918365B2 JP S5918365 B2 JPS5918365 B2 JP S5918365B2 JP 13196781 A JP13196781 A JP 13196781A JP 13196781 A JP13196781 A JP 13196781A JP S5918365 B2 JPS5918365 B2 JP S5918365B2
Authority
JP
Japan
Prior art keywords
red tide
hydrochloric acid
aluminum
treatment agent
substitutable
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.)
Expired
Application number
JP13196781A
Other languages
Japanese (ja)
Other versions
JPS5832805A (en
Inventor
亀丸 大須賀
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP13196781A priority Critical patent/JPS5918365B2/en
Publication of JPS5832805A publication Critical patent/JPS5832805A/en
Publication of JPS5918365B2 publication Critical patent/JPS5918365B2/en
Expired legal-status Critical Current

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  • Water Treatment By Sorption (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)

Description

【発明の詳細な説明】 この発明は、原料が入手容易で、しかも、二次公害の発
生危険度が小さいことを目的とする赤潮処理剤およびそ
の製造方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a red tide treatment agent whose raw materials are easily available and which has a low risk of secondary pollution, and a method for producing the same.

近年、日本領海沿岸、内陸潮沼もしくは河川等において
、工場廃水、家庭廃水、農業廃水、蓄産または水産関連
廃水等に基づ(水の富栄養化に起因すると言われる鞭毛
藻類や珪藻類等の浮遊生物の異常発生、すなわち、いわ
ゆる赤潮による被害が各地で話題になり、一度赤潮が発
生すると従来はほとんど打つ手がなく、養魚区付近で起
きたときは、養魚区域を赤潮区域から遠ざけると言うよ
うなきわめて消極的かつ原始的な手段しか取り得なかっ
たが、最近になってアルミニウムイオンが赤潮の撲滅に
きわめて有効であることが明らかとなって以来、天然鉱
物または化学薬剤が赤潮処理剤として注目されるように
なった。
In recent years, in Japan's territorial waters, inland tidal marshes, rivers, etc., wastewater from factories, domestic wastewater, agricultural wastewater, stockpiling or fisheries-related wastewater (such as flagellates and diatoms, which are said to be caused by water eutrophication) has been detected. The damage caused by the abnormal occurrence of floating organisms, or so-called red tide, has become a hot topic in various places, and once red tide occurs, there is little that can be done, but when it occurs near a fish farming area, it is said to move the fish farming area away from the red tide area. However, since it has recently become clear that aluminum ions are extremely effective in eradicating red tide, natural minerals or chemical agents have gained attention as red tide treatment agents. It became so.

しかし、天然鉱物としては、青森、山形、福島、新潟、
富山、島根、福岡、鹿児島等のように、はぼ全国的と言
える広域に産出するモンモリロナイトのうち、鹿児島産
のものが水中で最もアルミニウムイオンを放出する(置
換性アルミニウムが1〜2me/100?で、天然鉱物
では最高値であるとされている)ものとして使用されて
いるが、これとても、赤潮発生水面1771”当り15
0〜500グを散布しなげればならず、散布量が多く、
これの沈降後のスラッジによる魚礁の汚染等による二次
公害の発生が懸念されており、その散布量が少な(とも
十分の一以下(そのためには、置換性アルミニウムを2
0me/100?以上)であるよう強(要望されている
However, as natural minerals, Aomori, Yamagata, Fukushima, Niigata,
Among the montmorillonites produced in wide areas such as Toyama, Shimane, Fukuoka, and Kagoshima, which can be said to be nationwide, the one from Kagoshima releases the most aluminum ions in water (substituted aluminum is 1 to 2 me/100? It is said to have the highest value among natural minerals), but this is extremely high, with a red tide of 15 per 1,771" of water surface.
It is necessary to spray 0 to 500g, and the amount of spraying is large.
There are concerns about the occurrence of secondary pollution due to the contamination of fish reefs by the sludge after settling, and the amount of spraying is small (less than one tenth).
0me/100? It is requested that the requirements be strong (or higher).

また、特にわが国においては、天然鉱物はその鉱脈が小
規模であって、局地的に限定生産されるものが多く、同
一組成のものを長期間安定して大量供給することはきわ
めて困難であることから、鹿児島産のモンモリロナイト
もその例外ではな(、資源的に安定供給のできるものが
切望されている。
In addition, especially in Japan, many natural minerals have small-scale mines and are locally produced in limited quantities, making it extremely difficult to stably supply large quantities of the same composition over a long period of time. Therefore, montmorillonite from Kagoshima is no exception (there is a strong need for a stable supply of resources).

このような天然鉱物に対して、化学薬剤である硫酸アル
ミニウム、塩化アルミニウム等のアルミニウム塩も、赤
潮を死滅させる効力を有することが知られてはいるが、
魚介類をも死滅させる恐れがあって、水産資源の生息し
ていない特殊な区域を除いては使用することはできない
ので、天然鉱物、化学薬剤のいずれも好ましい赤潮処理
剤であるとは言えない。
Although it is known that aluminum salts such as aluminum sulfate and aluminum chloride, which are chemical agents, have the effect of killing red tide against these natural minerals,
Neither natural minerals nor chemical agents can be said to be preferable red tide treatment agents, as they may also kill fish and shellfish and cannot be used except in special areas where marine resources do not exist. .

この発明は、このような現状に着目してなされたもので
あり、置換性アルミニウムが20me/1001以上の
アルミ型粘土鉱物からなる赤潮処理剤、および、塩基置
換容量が大きく多孔質である粘土質鉱物を塩酸水溶液で
処理し、水洗、乾燥することを特徴とする赤潮処理剤の
製造方法を提供するものである。
This invention has been made in view of the current situation, and includes a red tide treatment agent consisting of an aluminum-type clay mineral with a substitutable aluminum content of 20 me/1001 or more, and a porous clay mineral with a large base substitution capacity. The present invention provides a method for producing a red tide treatment agent, which comprises treating minerals with an aqueous hydrochloric acid solution, washing with water, and drying.

以下にその詳細を述べる。まず、この発明における塩基
置換容量が太き((20me/100P以上)多孔質で
ある粘土質鉱物の代表的なものは、農業、工業の多方面
で、土壌改良剤、触媒担体、結合剤、吸着剤、濾過剤、
イオン交換剤等として広(用いられているモンモリロナ
イト、ペンナイト、ゼオライト等を挙げることができる
The details are described below. First, typical clay minerals that are porous and have a large base substitution capacity (20 me/100 P or more) are used in various agricultural and industrial fields as soil conditioners, catalyst carriers, binders, adsorbent, filtration agent,
Examples of ion exchange agents include montmorillonite, pennite, zeolite, etc., which are widely used.

これら鉱物は、天然に産出されるままの状態では組成に
かなりの変動がある。
These minerals vary considerably in composition in their naturally occurring state.

したがって、これら鉱物を塩酸水溶液で処理し、多孔質
部位に深(侵入した塩酸によって、置換性塩類(カルシ
ウム塩やマグネシウム塩等)は追い出されて置換性水素
に置き換えられ、それがさらに置換性アルミニウムに変
る性質を利用して、置換性アルミニウムの数値が20m
e/100P以上(このような値のものは天然産品には
見られない)のアルミニウムイオンを放出しやすいアル
ミ型粘土鉱粉とするのである。
Therefore, by treating these minerals with an aqueous solution of hydrochloric acid, the hydrochloric acid that penetrates deeply into the porous region drives out the substituting salts (calcium salts, magnesium salts, etc.) and replaces them with substitutable hydrogen, which in turn in turn turns into substitutable aluminum. By utilizing the property of changing to
The aluminum-type clay powder is made to easily release aluminum ions with a value of e/100P or higher (such values are not found in natural products).

なお、塩基置換容量が太き、多孔質である粘土質鉱物を
塩酸処理するに当っては、粘土質鉱物は、微粉末状のも
のでは塩酸処理後の水洗工程における沈降、濾過、脱水
等の操作が困難となることがら、予め5〜10mrn程
度に整粒してお(と好都合である。
In addition, when treating clay minerals, which have a large base substitution capacity and are porous, with hydrochloric acid, clay minerals in fine powder form may undergo sedimentation, filtration, dehydration, etc. in the water washing process after the hydrochloric acid treatment. Since the operation becomes difficult, it is convenient to size the particles in advance to about 5 to 10 mrn.

また、塩酸水溶液の塩酸濃度は1規定またはその前後(
たとえば、水1リットル中に塩酸を0.8〜1.2当量
の割合)とし、使用する塩酸水溶液の量は、塩酸が粘土
質鉱物中から追い出す置換性塩類に対して1,5〜2.
0倍当量であることが望ましい。
In addition, the hydrochloric acid concentration of the hydrochloric acid aqueous solution is at or around 1N (
For example, the ratio of hydrochloric acid to 1 liter of water is 0.8 to 1.2 equivalents), and the amount of hydrochloric acid aqueous solution used is 1.5 to 2.0 equivalents per liter of displacing salts that hydrochloric acid drives out of the clay mineral.
It is desirable that the amount is 0 times equivalent.

なぜならば、前記制限を遥かに越えて塩酸の量を増加す
ることは、粘土質鉱物の組織を破壊することになり、一
方、前記制限以下に塩酸の量を減少することは、塩酸処
理の効果を現わし得ないからである。
This is because increasing the amount of hydrochloric acid far beyond the above limit will destroy the structure of clay minerals, while decreasing the amount of hydrochloric acid below the above limit will reduce the effect of hydrochloric acid treatment. This is because it cannot be expressed.

そして、このような塩酸処理は、常温付近(温度を高(
するほど塩酸の反応性は必要以上に激しくなり、組織破
壊を起す危険性が高(なり好ましくない)で、適時攪拌
を反復しながら、通常4時間またはそれ体以上の間、粘
土質鉱物を塩酸水溶液中に浸漬した状態で行なうのであ
る。
Such hydrochloric acid treatment is carried out at around room temperature (at high temperature).
The more the hydrochloric acid reacts, the more intense the reactivity of the hydrochloric acid becomes than necessary, and the risk of tissue destruction is high (which is undesirable). This is done while immersed in an aqueous solution.

そうすれば、約4時間で塩酸は粘土質鉱物中の置換性塩
類のおよそ70〜80%程度を置換性アルミニウムに置
き変えることができる。
In this way, hydrochloric acid can replace approximately 70 to 80% of the substitutable salts in the clay mineral to substitutable aluminum in about 4 hours.

塩酸処理を終れば、水洗工程に移る。After completing the hydrochloric acid treatment, the process moves to a water washing process.

水洗は、傾瀉法、濾過法など通常用いられるいずれの方
法によっても何等の支障はないが、熱水の使用は粘土質
鉱物の組織破壊を防ぐ目的から避ける方がよく、塩素イ
オンが出な(なる時点で水洗を終わる。
There is no problem with washing with water by any of the commonly used methods such as decanting or filtration, but it is better to avoid using hot water to prevent tissue destruction of clay minerals, and avoid emitting chlorine ions ( Finish washing with water at this point.

塩酸処理および水洗が終った粘土質鉱物は、つぎに乾燥
される。
The clay mineral that has been treated with hydrochloric acid and washed with water is then dried.

このとき乾燥方式は特に限定する必要はないが、乾燥温
度は、粘土質鉱物の組織破壊を防ぐために、90℃を越
えないように心掛けなければならない。
At this time, there is no need to particularly limit the drying method, but care must be taken to ensure that the drying temperature does not exceed 90° C. in order to prevent tissue destruction of the clay mineral.

乾燥が終れば、固結して塊状となるものもあるので、粉
砕して粒径が2朋以下の粉粒にする。
After drying, some of the particles solidify into lumps, so they are crushed into powder with a particle size of 2 mm or less.

このようにしておけば、水面に均一に散布することがで
き、また表面積も大きくなって、置換性アルミニウムイ
オンを効率よ(溶出するようになる。
By doing so, it is possible to uniformly spray the water surface, and the surface area is also increased, so that the displaceable aluminum ions can be efficiently (eluted).

なお、乾燥しないで湿潤状態の粘土質鉱物のままで使用
することができるが、輸送の面では乾燥したものが好ま
しい。
Note that although the clay mineral can be used as it is in a wet state without being dried, it is preferable to dry it in terms of transportation.

以上述べたことから明らかなように、この発明によれば
、従来の天然鉱物よりも置換性アルミニウムイオンを多
量に溶出させる物質を、半恒久的に安定して供給するこ
とが可能となり、この発明の意義はきわめて大きいと言
うことができる。
As is clear from the above, according to the present invention, it is possible to stably supply semi-permanently a substance that elutes a larger amount of substitutable aluminum ions than conventional natural minerals. It can be said that the significance of this is extremely large.

以下に実施例を示す。Examples are shown below.

実施例 市販されているモンモリロナイトのうち、最も安価で入
手が容易なもの(産地不明)を選び、これを1規定の塩
酸水溶液(室温)で2時間および4時間の処理を行ない
、pH1水溶性全塩、置換性塩類、塩基置換容量を求め
、その結果を第1表にまとめた。
Example Among the commercially available montmorillonites, the cheapest and most easily available one (origin unknown) was selected and treated with a 1N hydrochloric acid aqueous solution (room temperature) for 2 and 4 hours to obtain a pH 1 water-soluble montmorillonite. The salts, substitutable salts, and base substitution capacities were determined, and the results are summarized in Table 1.

第1表の結果から明らかなように、酸処理を2時間行な
ったものは、置換性塩類の約33%が置換性アルミニウ
ムに、また、酸処理4時間後のものは置換性塩類の約7
2%のものが置換性アルミニウムに置き変えられ27.
8me / 100 ?というきわめて高い値のものが
得られた。
As is clear from the results in Table 1, about 33% of the substitutable salts were converted to substitutable aluminum after 2 hours of acid treatment, and about 7% of the substitutable salts after 4 hours of acid treatment were converted to substitutable aluminum.
2% is replaced with substituted aluminum27.
8me/100? An extremely high value was obtained.

このような置換性アルミニウムの多い物質は、天然物に
は未だ認められておらず、従来知られている最高値のも
のでも、前記したように、1〜2me/1001程度で
しかない。
Substances with a large amount of substituted aluminum have not yet been found in natural products, and even the highest value known so far is only about 1 to 2 me/1001, as described above.

したがって、この発明による赤潮処理剤は、酸処理時間
を調節することによって置換性アルミニウムの濃度を2
0me/1001以上に適宜調整することができること
から、赤潮撲滅に有効である鹿児島産モンモリロナイト
と同等の効果を現わすにしても、十分の一以下の量に縮
減することはきわめて容易であり、散布後のスラッジ化
による二次公害も遥かに起りに((なることがわかった
Therefore, the red tide treatment agent according to the present invention can reduce the concentration of replaceable aluminum by adjusting the acid treatment time.
Since it can be adjusted to 0me/1001 or more, it is extremely easy to reduce the amount to less than one tenth, even if it has the same effect as Kagoshima montmorillonite, which is effective in eradicating red tide. Secondary pollution due to subsequent sludge formation is also far more likely to occur.

Claims (1)

【特許請求の範囲】 1 置換性アルミニウムが20me/100?以上のア
ルミ型粘土鉱粉からなる赤潮処理剤。 2 塩基置換容量が大きく多孔質である粘土質鉱物を塩
酸水溶液で処理し、水洗、乾燥することを特徴とする赤
潮処理剤の製造方法。
[Claims] 1. Substitutable aluminum is 20me/100? A red tide treatment agent made of the above aluminum-type clay mineral powder. 2. A method for producing a red tide treatment agent, which comprises treating a porous clay mineral with a large base substitution capacity with an aqueous hydrochloric acid solution, washing with water, and drying.
JP13196781A 1981-08-20 1981-08-20 Red tide treatment agent and its manufacturing method Expired JPS5918365B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13196781A JPS5918365B2 (en) 1981-08-20 1981-08-20 Red tide treatment agent and its manufacturing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13196781A JPS5918365B2 (en) 1981-08-20 1981-08-20 Red tide treatment agent and its manufacturing method

Publications (2)

Publication Number Publication Date
JPS5832805A JPS5832805A (en) 1983-02-25
JPS5918365B2 true JPS5918365B2 (en) 1984-04-26

Family

ID=15070406

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13196781A Expired JPS5918365B2 (en) 1981-08-20 1981-08-20 Red tide treatment agent and its manufacturing method

Country Status (1)

Country Link
JP (1) JPS5918365B2 (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5921607A (en) * 1982-07-29 1984-02-03 Mizusawa Ind Chem Ltd Treatment for red tide
JPS60174703A (en) * 1984-02-21 1985-09-09 Mizusawa Ind Chem Ltd Agent for controlling algae in paddy field
JPS63224788A (en) * 1987-03-16 1988-09-19 Taguchi Kenkyusho:Kk Clarifying treatment technique of water
KR100325396B1 (en) * 1999-11-08 2002-03-04 김봉경 Exclusion Method For Microorganism of Seawater change color
KR20010077795A (en) * 2000-02-08 2001-08-20 조익환 Get rid of red tide and daitomic and clean water, mud

Also Published As

Publication number Publication date
JPS5832805A (en) 1983-02-25

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