JPH034988A - Water and bottom purifying material - Google Patents
Water and bottom purifying materialInfo
- Publication number
- JPH034988A JPH034988A JP13644789A JP13644789A JPH034988A JP H034988 A JPH034988 A JP H034988A JP 13644789 A JP13644789 A JP 13644789A JP 13644789 A JP13644789 A JP 13644789A JP H034988 A JPH034988 A JP H034988A
- Authority
- JP
- Japan
- Prior art keywords
- water
- slug
- cao
- effective
- green
- 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.)
- Pending
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 22
- 239000000463 material Substances 0.000 title claims abstract description 12
- 239000002893 slag Substances 0.000 claims description 10
- 239000013049 sediment Substances 0.000 claims description 9
- 238000009628 steelmaking Methods 0.000 claims description 8
- 238000000746 purification Methods 0.000 claims description 6
- 235000008733 Citrus aurantifolia Nutrition 0.000 abstract description 7
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 abstract description 7
- 235000011941 Tilia x europaea Nutrition 0.000 abstract description 7
- 230000000694 effects Effects 0.000 abstract description 7
- 229910000037 hydrogen sulfide Inorganic materials 0.000 abstract description 7
- 239000004571 lime Substances 0.000 abstract description 7
- 241000894006 Bacteria Species 0.000 abstract description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 abstract description 3
- 229910052586 apatite Inorganic materials 0.000 abstract description 3
- VSIIXMUUUJUKCM-UHFFFAOYSA-D pentacalcium;fluoride;triphosphate Chemical compound [F-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O VSIIXMUUUJUKCM-UHFFFAOYSA-D 0.000 abstract description 3
- 229910052698 phosphorus Inorganic materials 0.000 abstract description 3
- 239000011574 phosphorus Substances 0.000 abstract description 3
- 229910052717 sulfur Inorganic materials 0.000 abstract description 3
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 abstract description 2
- 238000001179 sorption measurement Methods 0.000 abstract description 2
- -1 sulfide ions Chemical class 0.000 abstract description 2
- 239000011593 sulfur Substances 0.000 abstract description 2
- 229910000831 Steel Inorganic materials 0.000 abstract 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 abstract 2
- 238000004519 manufacturing process Methods 0.000 abstract 2
- 239000007787 solid Substances 0.000 abstract 2
- 239000010959 steel Substances 0.000 abstract 2
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 abstract 1
- 230000006641 stabilisation Effects 0.000 abstract 1
- 238000011105 stabilization Methods 0.000 abstract 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 10
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 5
- 239000000920 calcium hydroxide Substances 0.000 description 5
- 235000011116 calcium hydroxide Nutrition 0.000 description 5
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 5
- 239000000292 calcium oxide Substances 0.000 description 5
- 235000012255 calcium oxide Nutrition 0.000 description 5
- 239000013535 sea water Substances 0.000 description 4
- 239000000654 additive Substances 0.000 description 3
- 230000000996 additive effect Effects 0.000 description 3
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 239000006028 limestone Substances 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 1
- MBMLMWLHJBBADN-UHFFFAOYSA-N Ferrous sulfide Chemical compound [Fe]=S MBMLMWLHJBBADN-UHFFFAOYSA-N 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Landscapes
- Removal Of Specific Substances (AREA)
Abstract
Description
【発明の詳細な説明】
[産業上の利用分野コ
本発明は、水質・底質浄化材、特に海域、湖沼の青潮、
赤潮対策に使用する水質・底質浄化材に関するものであ
゛る。[Detailed Description of the Invention] [Industrial Field of Application] The present invention is a water quality/sediment purification material, particularly a blue tide of sea areas, lakes and marshes,
This relates to water quality and bottom sediment purification materials used for red tide countermeasures.
[従来の技術]
従来技術において、海域、湖沼の青潮、赤潮による水質
・底質における汚染を防止するため、その一つの対策で
ある薬剤を用いる方法として、石灰が用いられていた2
石灰の種類としては、石灰原石、生石灰、消石灰がある
が、石灰原石は溶解、、性が無い、生石灰は水と反応し
て危険である、消石灰は湖水、海水を汚染する等の欠点
があった。[Conventional technology] In the conventional technology, lime was used as a method of using chemicals as one of the countermeasures to prevent contamination of water quality and bottom sediment due to blue tide and red tide in sea areas, lakes and marshes2.
Types of lime include limestone, quicklime, and slaked lime, but limestone has disadvantages such as soluble and non-stick, quicklime reacts with water and is dangerous, and slaked lime pollutes lake water and seawater. Ta.
このため、消石灰を造粒化した顆粒状消石灰が提案され
ている。For this reason, granular slaked lime obtained by granulating slaked lime has been proposed.
[発明が解決しようとする課題]
しかしながら、前記顆粒状消石灰は、高価であり、青潮
の発生原因である硫化水素を硫化鉄として固定するため
、酸化鉄を混合する必要がある、また、pHの制御が困
難で水質が高アルカリになる場合があるなどの問題点が
ある0本発明は上記の問題点を解決し、青潮、赤潮の有
効な対策となる水質・底質浄化材を提案することをその
目的とするものである。[Problems to be Solved by the Invention] However, the granular slaked lime is expensive, and it is necessary to mix iron oxide in order to fix hydrogen sulfide, which is the cause of blue tide, as iron sulfide. The present invention solves the above problems and proposes a water and bottom sediment purification material that is an effective measure against blue tide and red tide. Its purpose is to
[課題を解決するための手段]
本発明に係る水質・底質浄化材は、製鋼スラグの粒状体
を主要成分とする水質・底質浄化材である。[Means for Solving the Problems] The water/sediment purifying material according to the present invention is a water/sediment purifying material containing granulated steelmaking slag as a main component.
[作用]
本発明における水質・底質浄化材は製鋼スラグの粒状体
が主要成分であるので、これを海域、湖沼中に投与した
場合、下記の作用がある。[Function] Since the main component of the water/sediment purification material of the present invention is granulated steelmaking slag, when it is administered into sea areas, lakes, and marshes, it has the following effects.
■製鋼スラグの粒状体は砂状であるので、底泥を覆う覆
砂効果がある(石灰の場合は、山砂を底泥覆砂材として
投与する必要がある)。■Since the granules of steelmaking slag are sand-like, it has the effect of covering the bottom mud (in the case of lime, it is necessary to administer mountain sand as a bottom mud covering material).
■硫酸還元菌(硫化物イオンを青潮の原因となる硫黄や
硫化水素に化学変化させる蔀)の活動を、製鋼スラグに
含まれるCaOの溶出によって抑制する。この際、活動
抑制に必要なpHは8.5以上であるが、製鋼スラグの
場合は8.5以上9.0以下に保持される(石灰の場合
は、pHが10以上となり、水質が劣化する)。■The activity of sulfate-reducing bacteria (sulfuric acid-reducing bacteria that chemically converts sulfide ions into sulfur and hydrogen sulfide, which causes blue tide) is suppressed by elution of CaO contained in steelmaking slag. At this time, the pH required to suppress activity is 8.5 or more, but in the case of steelmaking slag, it is kept at 8.5 or more and 9.0 or less (in the case of lime, the pH is 10 or more, and the water quality deteriorates. do).
■CaO分、Fe20z分によって、水中のH2Sを固
定化する。■H2S in water is fixed by CaO and Fe20z.
■CaO分によって、水中のP O4S−を固定する0
反応の結果、Ca s(P Oah (アパタイト)
となるが、アパタイトは製鋼スラグ中に存在するので、
石灰分単体より吸着効果が大きい、燐分の固定は、青潮
、赤潮の発生原因である富栄養価の防止に効果がある。■ Fixed P O4S- in water by CaO content0
As a result of the reaction, Ca s(P Oah (apatite)
However, since apatite exists in steelmaking slag,
Fixing phosphorus, which has a greater adsorption effect than lime alone, is effective in preventing eutrophication, which is the cause of blue tide and red tide.
[実施例]
第1図は本発明の一実施例を示す説明図である。底泥(
海底より採取したもの)の上に予め窒素ガスを通気した
海水を静かに満たし、嫌気状態を保ち数日間放置して、
H2Sを発生させた。この海水1を250m容ガラス瓶
2.20本に分取してそれぞれの実験区とし、所定の添
加材3を加え、これをインキュベーター(図示せず)で
温度を24℃に保ち暗状態でマグネチックスターラー4
および攪伴子5によって緩やかに攪伴し、一定時間経過
後に水質の変化を測定した。水域に実験区を設定するこ
とを模擬して促進試験を行った。[Example] FIG. 1 is an explanatory diagram showing an example of the present invention. Bottom mud (
(collected from the seabed) is gently filled with seawater that has been aerated with nitrogen gas, maintained in an anaerobic state, and left for several days.
H2S was generated. This seawater 1 was divided into 2.20 250m glass bottles, each used as an experimental group, the prescribed additive 3 was added, and the temperature was kept at 24°C in an incubator (not shown) and magnetically heated in the dark. Stirrer 4
The water was then gently agitated using the stirrer 5, and changes in water quality were measured after a certain period of time had elapsed. An accelerated test was conducted simulating setting up an experimental area in a body of water.
それぞれの実験条件を第1表に示す。Table 1 shows the experimental conditions for each.
第 1 表
(A区、B区;発明例、対象区:比較例)添加材の種類
は転炉スラグでその成分を第2表に示す0粒径は11程
度である。Table 1 (A section, B section; Invention example, Target section: Comparative example) The type of additive is converter slag, and its components are shown in Table 2. The zero particle size is about 11.
第2表 (%)
[発明の効果1
以上のように、本発明によれば製鋼スラグを水質・底質
浄化材として使用することにより、環境保全、魚獲損失
の回避が可能となる効果がある。Table 2 (%) [Effect of the invention 1 As described above, according to the present invention, by using steelmaking slag as a water and bottom sediment purification material, it is possible to conserve the environment and avoid loss of fish catches. be.
第2図はpHの経時変化を示すグラフである。FIG. 2 is a graph showing changes in pH over time.
A区、B区ニツイテは、pHは8.5〜9.0の範囲で
安定しているが、対象区においては、PHは8.0以下
である。比較区(石灰を200 g/loz添加したも
の)では、PHは10、まで上昇した。第3図はH,S
の経時変化を示すグラフである。A区、B区については
、5日後にほぼ0になるが、対象区は殆ど変化しない、
第4図はFe4−P (PO4の形態をとる燐分)の経
時変化を示すグラフである。A区、B区については、5
日後にほぼOになるが、対象区は殆ど変化しない、これ
らの実験結果から、転炉スラグはその水中の投与によっ
て、青潮、赤潮の発生を抑制する事が明らかである。The pH of the plants in Ward A and Ward B is stable in the range of 8.5 to 9.0, but in the target area, the pH is 8.0 or lower. In the comparative plot (200 g/loz of lime added), the pH increased to 10. Figure 3 shows H, S
It is a graph showing the change over time. For Wards A and B, it becomes almost 0 after 5 days, but there is almost no change in the target wards.
FIG. 4 is a graph showing the change over time of Fe4-P (phosphorus in the form of PO4). For A and B wards, 5
After a few days, it becomes almost O, but there is almost no change in the target area.From these experimental results, it is clear that by administering converter slag into water, the occurrence of blue tide and red tide can be suppressed.
第1図は本発明の一実施例を示す説明図、第2図はpH
の経時変化を示すグラフ、第3図はH2Sの経時変化を
示すグラフ、第4図はFe4Pの経時変化を示すグラフ
である。
1・・・海水、2・・・ガラス瓶、3・・・添加材、4
・・・マグネチックスター、5・・・攬伴子。Figure 1 is an explanatory diagram showing one embodiment of the present invention, Figure 2 is a pH
3 is a graph showing the change over time of H2S, and FIG. 4 is a graph showing the change over time of Fe4P. 1...Seawater, 2...Glass bottle, 3...Additive material, 4
...Magnetic Star, 5...Yinbanko.
Claims (1)
成分とすることを特徴とする水質・底質浄化材。A water and bottom sediment purification material characterized by containing granulated steelmaking slag as a main component.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13644789A JPH034988A (en) | 1989-05-30 | 1989-05-30 | Water and bottom purifying material |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13644789A JPH034988A (en) | 1989-05-30 | 1989-05-30 | Water and bottom purifying material |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH034988A true JPH034988A (en) | 1991-01-10 |
Family
ID=15175326
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP13644789A Pending JPH034988A (en) | 1989-05-30 | 1989-05-30 | Water and bottom purifying material |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH034988A (en) |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100306444B1 (en) * | 1999-04-13 | 2001-09-13 | 정종수 | The manufacture method of bacteria activated by sewage and wastes water treatment |
US6379543B1 (en) | 1999-02-26 | 2002-04-30 | Ecologic Holdings Pty Limited | Water treatment system |
JP2002238401A (en) * | 2000-12-14 | 2002-08-27 | Nkk Corp | Method for improving underwater environment |
KR100423414B1 (en) * | 1999-08-10 | 2004-03-19 | 주식회사 포스코 | A method for purifying water and sediment pollutants by using basic oxygen furnace slags |
KR100435429B1 (en) * | 1999-08-10 | 2004-06-10 | 주식회사 포스코 | A method for inhibiting contaminants-liberation from sediments |
WO2006083146A1 (en) * | 2005-02-07 | 2006-08-10 | Sang-Deuk Park | Material for seawater ecosystem preservation and red-tide prevention |
JP2007105676A (en) * | 2005-10-14 | 2007-04-26 | Nippon Steel Corp | Method for improving quality of water by utilizing steel slag |
JP2010094619A (en) * | 2008-10-17 | 2010-04-30 | Nisshin Steel Co Ltd | Sand replacement material and method for manufacturing the same |
JP2017087085A (en) * | 2015-11-02 | 2017-05-25 | 宍道湖漁業協同組合 | Method to render hydrogen sulfide generated in lake bed or bay bed harmless and system thereof |
CN108314167A (en) * | 2018-04-08 | 2018-07-24 | 南宁市夏阳化工科技有限责任公司 | One kind is except compound alkali of spent acid and preparation method thereof |
-
1989
- 1989-05-30 JP JP13644789A patent/JPH034988A/en active Pending
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6379543B1 (en) | 1999-02-26 | 2002-04-30 | Ecologic Holdings Pty Limited | Water treatment system |
KR100306444B1 (en) * | 1999-04-13 | 2001-09-13 | 정종수 | The manufacture method of bacteria activated by sewage and wastes water treatment |
KR100423414B1 (en) * | 1999-08-10 | 2004-03-19 | 주식회사 포스코 | A method for purifying water and sediment pollutants by using basic oxygen furnace slags |
KR100435429B1 (en) * | 1999-08-10 | 2004-06-10 | 주식회사 포스코 | A method for inhibiting contaminants-liberation from sediments |
JP2002238401A (en) * | 2000-12-14 | 2002-08-27 | Nkk Corp | Method for improving underwater environment |
WO2006083146A1 (en) * | 2005-02-07 | 2006-08-10 | Sang-Deuk Park | Material for seawater ecosystem preservation and red-tide prevention |
JP2007105676A (en) * | 2005-10-14 | 2007-04-26 | Nippon Steel Corp | Method for improving quality of water by utilizing steel slag |
JP2010094619A (en) * | 2008-10-17 | 2010-04-30 | Nisshin Steel Co Ltd | Sand replacement material and method for manufacturing the same |
JP2017087085A (en) * | 2015-11-02 | 2017-05-25 | 宍道湖漁業協同組合 | Method to render hydrogen sulfide generated in lake bed or bay bed harmless and system thereof |
CN108314167A (en) * | 2018-04-08 | 2018-07-24 | 南宁市夏阳化工科技有限责任公司 | One kind is except compound alkali of spent acid and preparation method thereof |
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