JPS6133291A - Treatment of waste water containing heavy metal - Google Patents

Treatment of waste water containing heavy metal

Info

Publication number
JPS6133291A
JPS6133291A JP15260684A JP15260684A JPS6133291A JP S6133291 A JPS6133291 A JP S6133291A JP 15260684 A JP15260684 A JP 15260684A JP 15260684 A JP15260684 A JP 15260684A JP S6133291 A JPS6133291 A JP S6133291A
Authority
JP
Japan
Prior art keywords
water
phosphoric acid
soluble
heavy metals
calcium
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
Application number
JP15260684A
Other languages
Japanese (ja)
Other versions
JPH0128632B2 (en
Inventor
Isamu Kato
勇 加藤
Itsuko Sugimoto
杉本 伊津子
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP15260684A priority Critical patent/JPS6133291A/en
Publication of JPS6133291A publication Critical patent/JPS6133291A/en
Publication of JPH0128632B2 publication Critical patent/JPH0128632B2/ja
Granted legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents

Landscapes

  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PURPOSE:To precipitate and treat heavy metals selectively by adding water-soluble phosphoric acid compds. and water-soluble calcium comps. to the waste water contg. heavy metals and organic acids. CONSTITUTION:Water-soluble calcium compds. such as calcium chloride plus slaked lime and water-soluble phosphoric acid compds. such as phosphoric acid plus sodium phosphate are added to the waste water contg. heavy metals such as iron, copper, cadmium plus nickel and organic acids and the mixture is suitably stirred in the state of 7-12pH and allowed to react with each other to generate the precipitate. The generated precipitate is separated by the settling separation, the filter separation and the centrifugal separation means and removed.

Description

【発明の詳細な説明】 本発明は、有機酸を共存する重金属含有廃水を処理する
方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating heavy metal-containing wastewater coexisting with organic acids.

鉄、銅、カドミウム、ニッケル等の重金属を含有する廃
水の最も一般的な方法は、廃水にアルカリを添加し、重
金gを水酸化物として沈殿分離するアルカリ沈殿法であ
る。しかし、廃水に有機酸、特にオキシカルぎン酸(ク
エン酸、酒石酸、グルコン酸等)が共存する場合にはア
ルカリ沈殿法では処理が困難であった。例えば、クエン
酸は 酒石酸は の如き錯体を形成すると言われ、これらの錯体は安定な
ものであるため、上記方法では沈殿分離しえず、液中に
残留する。tた有機酸は鉄イオンとも安定な錯体を形成
するため、鉄イオンが錯体となって残存し、さらに鉄錯
体が分散剤として作用し他の重金属の沈殿を妨害するこ
とが明らかになった。重金属廃水の処理に最も有効と考
えられている硫化物法も、過剰の硫化すトリウム全沈殿
させるに添加した鉄塩が上述した分散剤としての作用を
示すことになる窺め、適用が困難であった。
The most common method for treating wastewater containing heavy metals such as iron, copper, cadmium, and nickel is an alkali precipitation method in which an alkali is added to the wastewater and heavy gold g is precipitated and separated as hydroxide. However, when organic acids, especially oxycarginic acid (citric acid, tartaric acid, gluconic acid, etc.) coexist in the wastewater, it is difficult to treat the wastewater using the alkaline precipitation method. For example, citric acid is said to form complexes such as tartaric acid, and since these complexes are stable, they cannot be precipitated and separated by the above method and remain in the liquid. It has been revealed that the iron ions remain as complexes because the organic acids also form stable complexes with iron ions, and that the iron complex acts as a dispersant and interferes with the precipitation of other heavy metals. The sulfide method, which is considered to be the most effective method for treating heavy metal wastewater, is difficult to apply because the iron salt added to completely precipitate the excess thorium sulfide acts as a dispersant as described above. there were.

本発明の目的は、有機rn′fr、共存する重金属含有
廃水に対し、鉄イオンの存在の有無にかかわらず重金属
t−十分に沈殿処理でき、従来のアルカリ沈殿法、鉄塩
共沈法及び硫化物法のいずれの方法にも適用できる重金
属含有廃水の処理方法を提供することにある。
The object of the present invention is to be able to sufficiently precipitate heavy metals in organic rn'fr and coexisting heavy metal-containing wastewater regardless of the presence or absence of iron ions. An object of the present invention is to provide a method for treating heavy metal-containing wastewater that can be applied to any of the physical methods.

本発明は重金属と有機酸を含む廃水に、水溶性リン酸化
合物と水溶性カルシウム化合物とを添加するか、又は水
溶性リン酸化合物と水溶性カルシウム化合物との反応直
後の生成物を添加し、pH7〜12に調整して沈殿処理
することを特徴とする重金属含有廃水の処理方法でおる
The present invention involves adding a water-soluble phosphoric acid compound and a water-soluble calcium compound to wastewater containing heavy metals and organic acids, or adding a product immediately after the reaction between a water-soluble phosphoric acid compound and a water-soluble calcium compound, This is a method for treating wastewater containing heavy metals, which is characterized by adjusting the pH to 7 to 12 and performing a precipitation treatment.

水溶性カルシウム化合物と水溶性リン酸化合物とはヒド
ロキシル7ノでタイトOaH(PO4)30Hに代表さ
れる沈殿を生成するが、廃水中に重金属が存在するとO
a xMy (PO4) Z L (2z42y−82
)に代表される複塩を形成して沈殿すると推定される。
Water-soluble calcium compounds and water-soluble phosphate compounds form a precipitate typified by tight OaH(PO4)30H at hydroxyl level, but if heavy metals are present in wastewater, OaH(PO4)30H is formed.
a x My (PO4) Z L (2z42y-82
) is presumed to form and precipitate.

式中、Mは鉄、銅、カドミウム、ニッケル等の重金属で
あυ、LはOH″″+ CI”” + 804”−等の
陰イオンであ夛、I H7+ ’LはM及びLのイオン
価数によって決定される整数を示す。廃水中に共在する
有機酸はこの沈殿物組成にほとんど関与せず、一部が吸
着あゐいは包含されるのみである。
In the formula, M is a heavy metal such as iron, copper, cadmium, nickel, etc., L is an anion such as OH""+ CI"" + 804"-, I H7+ 'L is an ion of M and L It shows an integer determined by the valence. Organic acids co-existing in the wastewater hardly contribute to the composition of the precipitate, and are only partially adsorbed or included.

本発明で使用する水溶性カルシウム化合物としては、塩
化カルシウム、消石灰、炭酸カルシウム等が挙げられ、
水溶性リン酸化合物としてはリン酸あるいはナトリウム
、カリウム等の各稚リン酸塩が挙げられる。リン酸ある
いはリン酸塩を含む廃水、例えばアルカリ脱脂液、リン
原塩を主体とするメッキ浴廃液でもよい。これらの使用
量は廃水中の重金属の種類等によって適宜決定されるが
、通常、カルシウム化合物とリン酸化合物の比はOa/
PO4(モル比)で1以上、重蚕属とリン酸化合物の比
はM/PO4(モル比)で3以下で使用される。
Water-soluble calcium compounds used in the present invention include calcium chloride, slaked lime, calcium carbonate, etc.
Examples of water-soluble phosphoric acid compounds include phosphoric acid and various juvenile phosphates such as sodium and potassium. Wastewater containing phosphoric acid or phosphates, such as alkaline degreasing solution or plating bath wastewater containing phosphorus salt as a main ingredient, may also be used. The amount of these used is determined depending on the type of heavy metal in the wastewater, etc., but usually the ratio of calcium compounds to phosphate compounds is Oa/
The PO4 (molar ratio) is used at 1 or more, and the ratio of M/PO4 (mole ratio) between the genus Silkworm and the phosphoric acid compound is 3 or less.

リン酸化合物とカルシウム化合物は、予め廃水中に添加
すればよいが、リン酸化合物とカルシウム化合物を反応
させたヒドロキシルア/々タイht添加してもよい。た
だし、予め反応させ友ヒドロキシルアノぞタイトは時間
と共に活性がなくなるため、反応後1時間以内のものを
使用する。この場合リン酸化合物とカルシウム化合物と
を反応槽で反応させt後、反応生成物を含む懸濁水を使
用できる。
The phosphoric acid compound and the calcium compound may be added to the wastewater in advance, but a hydroxyl compound prepared by reacting the phosphoric acid compound and the calcium compound may also be added. However, since hydroxyl annotite, which has been reacted in advance, loses its activity over time, it should be used within one hour after the reaction. In this case, after the phosphoric acid compound and the calcium compound are reacted in a reaction tank, suspension water containing the reaction product can be used.

廃水にリン酸化合物とカルシウム化合物を添加しに後は
、pt+ 7〜12、好ましくはpH7,5〜9に調整
し適宜攪拌を行って反応せしめ、生成し窺沈殿物を公知
の沈降分離、ろ過分離、遠心分離手段によって分離除去
する。沈殿処理に際しては単にpnt″中性ないしアル
カリ性にして重金FAヲ水酸化物として沈殿させること
ができるが、従来知られているような鉄塩共沈法、硫化
物法を使用することもできる。
After adding the phosphoric acid compound and the calcium compound to the wastewater, the pH is adjusted to pt+ 7 to 12, preferably pH 7.5 to 9, and the reaction is carried out with appropriate stirring, and the resulting precipitate is subjected to well-known sedimentation separation and filtration. Separate and remove by means of separation and centrifugation. In the precipitation treatment, the heavy metal FA can be simply made pnt' neutral or alkaline and precipitated as a hydroxide, but conventionally known iron salt coprecipitation methods and sulfide methods can also be used.

本発明によれば、水溶性リン酸化合物と水溶性カルシウ
ム化合物との併用によって重金属と有機酸との錨体形−
成が抑止され、重金属が選択的に沈殿物として生成する
。従って、有機W1t″共存する重金属含有廃水に対し
てアルカリ沈殿法(pH中性ないしアルカリ性)、鉄塩
共沈法、硫化物法の適用が可能となり効率よく重金属を
除去できる。
According to the present invention, by using a water-soluble phosphoric acid compound and a water-soluble calcium compound in combination, heavy metals and organic acids form an anchor structure.
heavy metals are selectively formed as precipitates. Therefore, it is possible to apply the alkaline precipitation method (pH neutral to alkaline), iron salt coprecipitation method, and sulfide method to heavy metal-containing wastewater in which organic W1t'' coexists, and heavy metals can be efficiently removed.

従来法に係る参考例と本発明に係る実施例を示す。A reference example according to a conventional method and an embodiment according to the present invention are shown.

参考例1(アルカリ沈殿法、鉄塩共沈法)Or”+ +
 04” 、Nk” 、Zn”、Qu” 、pb”+を
それぞれ20F含む溶液に、有機酸(シュウ酸、酒石酸
、グルコン酸)t−iooop添加し次。さらに鉄塩と
して硫酸第一鉄又は塩化第二鉄を添加して水酸化す) 
17クムでpH7,5又はpflllに調整し30分間
反応させfc0反応液を濾紙雁50を用いて濾過し、濾
液の分析を行い結果を表−1に示した。
Reference example 1 (alkali precipitation method, iron salt co-precipitation method) Or”+ +
Organic acids (oxalic acid, tartaric acid, gluconic acid) t-iooop were added to a solution containing 04", Nk", Zn", Qu", pb"+ at 20F each. Then, ferrous sulfate or chloride was added as an iron salt. Hydroxylation with addition of ferric iron)
The fc0 reaction solution was adjusted to pH 7.5 or pflll with 17 cum and reacted for 30 minutes, and the fc0 reaction solution was filtered using filter paper Gan 50, and the filtrate was analyzed, and the results are shown in Table 1.

いずれの場合も全ての重金属を十分に除失しえておらず
、鉄塩を添加しても共沈効果が認められず、むしろ鉄塩
の共存によって沈殿効果は悪化し、鉄塩は錯体、となっ
て残留し友。
In either case, all the heavy metals were not sufficiently removed, and no co-precipitation effect was observed even when iron salts were added.In fact, the co-precipitation effect was worsened by the coexistence of iron salts, and the iron salts were considered to be complexes. I stayed behind and became a friend.

実施例1 クエン酸1000F、塩化第二鉄100Wn(鉄として
)t−含む試料液に、塩化カルシウム又はリン識ナトリ
ウム或いは岬者を添神して水酸化ナトリウムによりpl
isに1!!整し30分間反応させ友、。反応液を濾紙
ム50を用いて濾過し・濾液の分析を行い結果を表−3
に示し比。
Example 1 A sample solution containing 1000 F citric acid and 100 Wn (as iron) of ferric chloride was added with calcium chloride, sodium phosphorus, or chloride, and then plipped with sodium hydroxide.
1 for is! ! Set it up and let it react for 30 minutes. The reaction solution was filtered using filter paper M50, the filtrate was analyzed, and the results are shown in Table 3.
Shown in the ratio.

表−3に°示すように、カルシウム化合物とリン酸化合
物が共存すると鉄イオンは処理可能となった。t 7’
j OODの低下は小さく、クエン酸はほとんど沈殿し
ないことが分る。
As shown in Table 3, iron ions could be treated when calcium compounds and phosphate compounds coexisted. t7'
j It can be seen that the decrease in OOD is small and citric acid hardly precipitates.

表−3 実施例2 06” + N1” r Zn” 、 Ou” t P
b” + Fe”+をそれぞれ20 P sクエンW!
を1000F含む溶液に塩化カルシウムとリン酸ナトリ
ウム′f!:添加し、水酸化ナトリウムでpH8K調整
した。30分間反応援、反応液t−濾紙A50を用いて
濾過し、濾液の分析を行い結果を表−4に示した。
Table-3 Example 2 06" + N1" r Zn", Ou" t P
b” + Fe”+ each for 20 Ps Quen W!
Calcium chloride and sodium phosphate'f in a solution containing 1000F! : was added and the pH was adjusted to 8K with sodium hydroxide. The reaction solution was incubated for 30 minutes, filtered using T-filter paper A50, and the filtrate was analyzed, and the results are shown in Table 4.

貴−4に示すように、カルシウム化合物とリン酸化合物
が共存しない場合(&1)は処理困難であったが、共存
する場合(A2〜A5 )では重金属は処理可能であっ
た。特にA4及び煮5に示すようにアルカリ性にすると
Ni 、 Ouも十分に処理できた。
As shown in No. 4, treatment was difficult when calcium compounds and phosphate compounds did not coexist (&1), but heavy metals could be treated when they coexisted (A2 to A5). In particular, Ni and Ou could be treated satisfactorily when made alkaline as shown in A4 and Boil 5.

(以下余白) 表−4 実施例3 参考例2で述べ次男法でカルシウム化合物とリン酸化合
物の共存試料液の硫化物処理を行った。重金属濃度と有
機酸濃度も参考例2と同じである。結果は表−5に示す
とおシである。
(The following is a blank space) Table 4 Example 3 A sample solution in which a calcium compound and a phosphoric acid compound coexisted was treated with sulfide by the second son method described in Reference Example 2. The heavy metal concentration and organic acid concentration were also the same as in Reference Example 2. The results are shown in Table 5.

表−5に示すように、カルシウム化合物とリンm化合物
が共存すれば硫化物法の適用は十分可能であることが明
らかとなった。
As shown in Table 5, it has become clear that the sulfide method can be applied as long as a calcium compound and a phosphorus m compound coexist.

実施例4 りx 7 ’7500 PS11g化第二鉄100 p
p (Fe”として) 、Zn”+とCd”をそれぞれ
20F含む溶液を水酸化す) +7ウムでpH8に調整
し、これを被処理液とした。
Example 4 Ri x 7 '7500 PS11g ferric chloride 100p
A solution containing 20F each of p (as Fe''), Zn''+ and Cd'' was hydroxylated and adjusted to pH 8 with +7 um, and this was used as the liquid to be treated.

別容器で坦化カルシウム1011/It (Oaとして
)とリン醗ナトリウム41/l (Pとして)を混合し
、pm 9〜1oでθ〜2時間反応させ友リン酸カルシ
ウムを準備した。上記被処理液にリン酸カルシウムf 
s o o yp (Oaとして、Pとしては20 o
炉)添加してpH8で30分間反応させ九。
In a separate container, 1011/It of flattened calcium (as Oa) and 41/L of sodium phosphate (as P) were mixed and reacted for 2 hours at 9 to 1 o pm to prepare calcium phosphate. Calcium phosphate f is added to the above-mentioned liquid to be treated.
s o o yp (as Oa, as P is 20 o
Furnace) and react for 30 minutes at pH 8.9.

反応液t−濾紙&50を用いて濾過し、濾液の分析を行
い結果を表−6に示した。
The reaction solution was filtered using T-filter paper &50, and the filtrate was analyzed, and the results are shown in Table 6.

表−6に示すように熟成の進んだリン酸カルシウムの反
応性は乏しいことが明らかである。
As shown in Table 6, it is clear that the reactivity of aged calcium phosphate is poor.

表−゛6Table-゛6

Claims (1)

【特許請求の範囲】[Claims] 1、重金属と有機酸を含む廃水に、水溶性リン酸化合物
と水溶性カルシウム化合物とを添加するか、又は水溶性
リン酸化合物と水溶性カルシウム化合物との反応直後の
生成物を添加し、pH7〜12に調整して沈殿処理する
ことを特徴とする重金属含有廃水の処理方法。
1. Add a water-soluble phosphoric acid compound and a water-soluble calcium compound to wastewater containing heavy metals and organic acids, or add a product immediately after the reaction between a water-soluble phosphoric acid compound and a water-soluble calcium compound, and adjust the pH to 7. 1. A method for treating heavy metal-containing wastewater, which comprises adjusting the concentration to 12 to 12 and subjecting it to precipitation.
JP15260684A 1984-07-23 1984-07-23 Treatment of waste water containing heavy metal Granted JPS6133291A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15260684A JPS6133291A (en) 1984-07-23 1984-07-23 Treatment of waste water containing heavy metal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15260684A JPS6133291A (en) 1984-07-23 1984-07-23 Treatment of waste water containing heavy metal

Publications (2)

Publication Number Publication Date
JPS6133291A true JPS6133291A (en) 1986-02-17
JPH0128632B2 JPH0128632B2 (en) 1989-06-05

Family

ID=15544072

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15260684A Granted JPS6133291A (en) 1984-07-23 1984-07-23 Treatment of waste water containing heavy metal

Country Status (1)

Country Link
JP (1) JPS6133291A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2728812A1 (en) * 1994-12-30 1996-07-05 Electricite De France Heavy, toxic or radioactive metal confinement in apatite
EP0695224A4 (en) * 1992-09-22 1997-07-23 James Hamilton Kyle Compositions and methods for waste treatment
JP2000202461A (en) * 1999-01-11 2000-07-25 Kurita Water Ind Ltd Treatment of heavy metal complex-containing waste liquid
WO2007074751A1 (en) * 2005-12-26 2007-07-05 Toagosei Co., Ltd. Method for treating wastewater
JP2010521297A (en) * 2007-03-21 2010-06-24 オムヤ・デイベロツプメント・アー・ゲー Surface treated calcium carbonate and its use in wastewater treatment
CN104211221A (en) * 2014-09-03 2014-12-17 上海丰信环保科技有限公司 Treatment method for low-concentration cadmium-containing wastewater

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0695224A4 (en) * 1992-09-22 1997-07-23 James Hamilton Kyle Compositions and methods for waste treatment
FR2728812A1 (en) * 1994-12-30 1996-07-05 Electricite De France Heavy, toxic or radioactive metal confinement in apatite
JP2000202461A (en) * 1999-01-11 2000-07-25 Kurita Water Ind Ltd Treatment of heavy metal complex-containing waste liquid
WO2007074751A1 (en) * 2005-12-26 2007-07-05 Toagosei Co., Ltd. Method for treating wastewater
JP5223338B2 (en) * 2005-12-26 2013-06-26 東亞合成株式会社 Wastewater treatment method
JP2010521297A (en) * 2007-03-21 2010-06-24 オムヤ・デイベロツプメント・アー・ゲー Surface treated calcium carbonate and its use in wastewater treatment
CN104211221A (en) * 2014-09-03 2014-12-17 上海丰信环保科技有限公司 Treatment method for low-concentration cadmium-containing wastewater

Also Published As

Publication number Publication date
JPH0128632B2 (en) 1989-06-05

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