JP2004049960A - Environmental cleaning method for eutrophication water area - Google Patents
Environmental cleaning method for eutrophication water area Download PDFInfo
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- JP2004049960A JP2004049960A JP2002207767A JP2002207767A JP2004049960A JP 2004049960 A JP2004049960 A JP 2004049960A JP 2002207767 A JP2002207767 A JP 2002207767A JP 2002207767 A JP2002207767 A JP 2002207767A JP 2004049960 A JP2004049960 A JP 2004049960A
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- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Abstract
Description
【0001】
【発明の属する技術分野】
本発明は、富栄養化水域の環境を浄化し、水産業に資する手法の開発に関する。
【0002】
【従来の技術】
沿岸の水域は古くから水に親しむ場あるいは生産の場として、人類に多大の貢献をしてきたが、昨今は流入負荷の増大や、自然の浄化系の減衰に起因する、貧酸素水塊の発生等の問題が生じ、本来の水の機能が損なわれつつある。
【0003】
これは、主に水域に過剰に溜まった有機物の分解に酸素が消費されてしまうことが原因であるが、流入してくる家庭排水等を無機化するだけでは対処できない問題である。
【0004】
従来、富栄養化水域の環境を浄化する方法としては、浚渫・覆砂が行われていたが、いずれも一時的な効果でしかなく、覆砂や水流動促進は根本的な富栄養化物質の除去ができず、浚渫は富栄養化物質の除去はできるが、その浚渫土の処理において別の問題が発生する恐れがある。
また、その他の手法にしても富栄養化物質の再利用ができず、しかも継続的な資金の投入を強いられ、自治体等実施主体の経済的負担が大きかった。
【0005】
【発明が解決しようとする課題】
富栄養化物質を簡便に除去し、水域の浄化を持続的に行える方法の開発を課題とする。
【0006】
【課題を解決するための手段】
本発明者等は、上記課題を解決するために鋭意努力した結果、水底からの曝気と無給餌型養殖との組み合わせにより解決できることを見出した。
【0007】
すなわち、本発明は
(1) 底質表層に空気を送りこみ、生物の生残を助長させることによる水の浄化方法、
(2) 生物が無給餌養殖可能な生物であって濾過食性生物であることを特徴とする(1)記載の水の浄化方法、
(3) 濾過食性生物がカキ、アサリあるいはナマコのいずれかであることを特徴とする(2)記載の水の浄化方法
に関する。
生物を成長させるには多くの餌が必要であるが、一方で大量の擬糞が生ずる。
【0008】
本発明者等は、この擬糞をも含めて浄化することで初めて持続的な浄化が行われるとの観点から本発明を完成した。
【0009】
本発明は、底質表層においても溶存酸素を十分に確保し、養殖生物の擬糞も底生生物に取り込ませ、栄養分を最後まで徹底的に利用し尽くすことで、水浄化を達成させようとするものである。底質の生き物、例えばゴカイ等が増えれば、これらは魚介類の餌となり、ひいては魚介類の増加につながることとなる。
【0010】
水底付近で曝気することにより、水塊は溶存酸素濃度が上昇すると同時に緩やかな鉛直循環流が発生する。このことで底生の生物にあっても貧酸素で死ぬこともなくなり、特に濾過食性生物は曝気によって誘起された流れにのってくるエサを多く捉えることができる。
また、カキやアサリ等は水を澄ませる働きがあることから、太陽光の水中への透過量が大きくなり、藻場の造成を促進し魚介類の産卵場の形成に役立つことができる。
【0011】
富栄養化物質を回収するには、濾過食性二枚貝を用いると良い。例えば、ムラサキイガイやマガキのような基盤に固着するもの、ホタテガイのような堆積物表層に出ているもの、アサリやハマグリのような海底の堆積物に埋没するもの等が挙げられ、これらは水中の懸濁物や低次生産レベルのプランクトンを取り込むので、富栄養化物質を効率よく回収することとなる。
【0012】
さらに、ナマコは底質の砂泥を呑み込みその中に含まれる有機物、すなわち小型甲殻類、魚卵、軟体動物の幼生、デトライタス、珪藻類等を栄養分としているので、海底の有機物はナマコが浄化する。
以上のような総合的、複合的な内湾生態系の活性化が本発明の意図するところである。
【0013】
本発明の一つの特徴である経済的効果について試算してみると、大村湾を例として、年間の流入負荷を全て取り上げるために必要な浄化システムの占有面積は、湾全体の3分の1程度であり、年間経費は約780億円、収入は2,370億円となり、年間の収益は約1,590億円となった。
【0014】
【発明の実施の形態】
(実験例1) アサリを用いた懸濁物濾過実験
図1に示すように、左右のビーカーに攪拌とエアレーションを行う装置を取り付け、100ミクロンのフィルターで濾過した水を満たす。右側のビーカーにのみアサリ10個を入れる。
【0015】
左右のビーカーに粘土を溶かした泥水を同量注入し、1時間、2時間、2時間30分、3時間、4時間放置して観察を行った。3時間すると右のアサリの入ったビーカーはほとんど透明となったが、左のアサリが入っていないビーカーは変化なく泥水状態であった。
カキについて同様の実験を行うと、アサリの場合よりも10倍早く透明となった。
【0016】
(実験例2)曝気の特性実験
図2に示すように、浮桟橋に近い個所▲1▼から遠い個所▲9▼までの9箇所の水温、塩分、DO濃度について、各水深ごとに曝気前と曝気後の数値を測定した。測定結果をグラフ化したものが図3である。なお、曝気量は曝気管1m当たり約1L/分であった。
【0017】
このグラフを見ると、2時間弱の短い経過時間であっても曝気したことにより水深の如何にかかわらず水温がほぼ一定となり、塩分・DO濃度も水深による差が縮まったことがわかる。すなわち、開放区画においても鉛直方向の混合が実際に起こっていることが証明された。
【0018】
曝気量に関しては、「漁場の適正溶存酸素濃度の検討」(漁場環境容量策定事業報告書、社団法人 日本水産資源保護協会編 p931〜1003(1989))に本発明者等の研究として、「これらの検討結果を総括して、内湾の漁場において最低限維持しなくてはならない溶存酸素量は、3.0ml/lであるとの結論を得た。」(p1003)と記載しているように、底質表層を3.0ml/l以上のDO濃度とすることが求められる。
【0019】
【実施例】
海底に曝気管を敷設し、水域が貧酸素化しやすい夏季の約3ヶ月間にわたり曝気を行う。
曝気管の敷設間隔、曝気量は、曝気による誘起流れ、生物や水塊、底泥による酸素消費量を考慮した上で、溶存酸素濃度が水底に至るまで3ml/l以上の濃度となるよう調整する。
【0020】
こうして水塊全体が年間を通して3ml/l以上の溶存酸素濃度を確保できる水域を対象に、濾過食性二枚貝などの無給餌型養殖を行う。例えば、カキ養殖では100m四方の海面に8×18m程度の大きさのカキ筏を16基設置し、年間を通して養殖を行う。このとき必要な曝気は7.5kW程度の空気圧縮機を用いて7〜9月の3ヶ月間程度終夜連続稼動させて行う。曝気管は100mの長さで、水域の深度にもよるが、2〜3本が好適である。
【0021】
【発明の効果】
本発明により、富栄養化水域を簡便かつ利益を上げながら持続的に浄化することを可能ならしめた。
【図面の簡単な説明】
【図1】本発明の概要を示す図。
【図2】アサリを用いた懸濁物濾過実験を示す図。
【図3】曝気の特性実験を示す図。
【図4】曝気の特性実験の結果をグラフで示した図。[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to the development of a method for purifying the environment of a eutrophic water area and contributing to the fishing industry.
[0002]
[Prior art]
Coastal waters have long contributed to mankind as a place of familiarity with water or a place of production, but recently, the generation of anoxic water mass due to an increase in inflow load and attenuation of natural purification systems And the like, the original function of water is being impaired.
[0003]
This is mainly due to the fact that oxygen is consumed for decomposing the organic matter excessively accumulated in the water area, but it is a problem that cannot be dealt with merely by mineralizing incoming domestic wastewater and the like.
[0004]
Conventionally, dredging and sedimentation have been used as a method of purifying the environment of eutrophic waters, but both are only temporary effects, and sand covering and water flow promotion are fundamental eutrophic substances. Although dredging can remove eutrophic substances, other problems may arise in the treatment of the dredged soil.
Even with other methods, the eutrophic substances could not be reused, and the continuous input of funds was required, and the economic burden on the implementing bodies such as local governments was heavy.
[0005]
[Problems to be solved by the invention]
It is an object of the present invention to develop a method for easily removing eutrophic substances and continuously purifying water bodies.
[0006]
[Means for Solving the Problems]
The present inventors have made intensive efforts to solve the above-described problems, and as a result, have found that it can be solved by a combination of aeration from the water bottom and non-feeding type aquaculture.
[0007]
That is, the present invention provides (1) a method of purifying water by sending air to the surface of the sediment and promoting survival of living things;
(2) The method for purifying water according to (1), wherein the organism is a feed-free aquaculture organism and is a filter-eating organism.
(3) The method for purifying water according to (2), wherein the filtered food-eating organism is any of oysters, clams, and sea cucumber.
Growing an organism requires a lot of food, but it produces a lot of false feces.
[0008]
The present inventors have completed the present invention from the viewpoint that continuous purification is performed for the first time by purifying also including the artificial feces.
[0009]
The present invention seeks to achieve water purification by ensuring sufficient dissolved oxygen even in the surface layer of sediments, incorporating pseudofeces of cultured organisms into benthos, and using nutrients thoroughly to the end. Is what you do. If the number of creatures with bottom sediment, for example, creatures, increases, they become food for fish and shellfish, and eventually lead to an increase in fish and shellfish.
[0010]
By aeration near the water bottom, the water mass increases the dissolved oxygen concentration and at the same time generates a gentle vertical circulation flow. As a result, even in the case of benthic organisms, they do not die due to anoxia, and in particular, the filter-eating organisms can capture a large amount of food in the flow induced by aeration.
Oysters and clams also have the function of clearing water, so that the amount of sunlight that permeates into the water increases, thereby promoting the creation of seaweed beds and helping to form a spawning ground for fish and shellfish.
[0011]
In order to recover the eutrophic substance, it is preferable to use a filter-eating bivalve. For example, those that adhere to the base such as mussels and oysters, those that appear on the surface of sediments such as scallops, and those that are buried in sediments on the seabed such as clams and clams, and the like, By taking in suspensions and plankton at lower production levels, eutrophic substances can be recovered efficiently.
[0012]
In addition, sea cucumber swallows the bottom mud and feeds on organic matter contained in it, such as small crustaceans, fish eggs, mollusk larvae, detritus, and diatoms, so sea cucumber purifies organic matter on the sea floor. .
The comprehensive and complex activation of the inner bay ecosystem as described above is intended by the present invention.
[0013]
Estimation of the economic effect, which is one of the features of the present invention, shows that, taking Omura Bay as an example, the area occupied by the purification system required to take in all the annual inflow load is about one-third of the entire bay. Annual expenses were about 78 billion yen, revenue was 237.0 billion yen, and annual revenue was about 159.0 billion yen.
[0014]
BEST MODE FOR CARRYING OUT THE INVENTION
(Experimental example 1) Suspension filtration experiment using clams As shown in Fig. 1, left and right beakers were equipped with devices for stirring and aeration, and filled with water filtered through a 100-micron filter. Insert 10 clams only in the right beaker.
[0015]
The same amount of muddy water in which the clay was dissolved was injected into the left and right beakers, and left for 1 hour, 2 hours, 2 hours 30 minutes, 3 hours, and 4 hours for observation. After 3 hours, the beaker with the right clam became almost transparent, but the beaker without the left clam remained muddy.
In a similar experiment on oysters, it became clear 10 times faster than in clams.
[0016]
(Experimental example 2) Aeration characteristics experiment As shown in Fig. 2, the water temperature, salinity, and DO concentration at nine points from point (1) near the floating pier to point (9) far from the floating pier were compared before and after aeration at each water depth. The value after aeration was measured. FIG. 3 is a graph of the measurement result. The amount of aeration was about 1 L / min per meter of the aeration tube.
[0017]
From this graph, it can be seen that the water temperature becomes almost constant irrespective of the water depth due to the aeration even for a short elapsed time of less than 2 hours, and the difference between the salinity and the DO concentration depending on the water depth is reduced. That is, it was proved that the mixing in the vertical direction actually occurred even in the open section.
[0018]
Regarding the amount of aeration, “Study of appropriate dissolved oxygen concentration in fishing grounds” (Fishing ground environmental capacity development project report, Japan Fisheries Resource Conservation Association, pp.931-1003 (1989)), as a study by the present inventors and others, In summary, we concluded that the minimum amount of dissolved oxygen that must be maintained at the fishing bay in the bay was 3.0 ml / l. "(P1003) In addition, it is required that the bottom layer has a DO concentration of 3.0 ml / l or more.
[0019]
【Example】
Aerating pipes will be laid on the sea floor, and aeration will be performed for about three months in summer, when the water area tends to become anoxia.
Laying spacing aeration pipe, an aeration amount of induced flow by aeration, in consideration of the oxygen consumption by the organism and the water mass, mud, so that the dissolved oxygen concentration of 3 ml / l or more concentrations up to water bottom adjust.
[0020]
In this way, non-feeding aquaculture such as filter-eating bivalves is performed in a water area where the whole water mass can secure a dissolved oxygen concentration of 3 ml / l or more throughout the year. For example, in oyster cultivation, 16 oyster rafts with a size of about 8 × 18 m are installed on a 100 m square sea surface and cultured throughout the year. At this time, the necessary aeration is performed by using an air compressor of about 7.5 kW and operating continuously for about three months from July to September. The length of the aeration tube is 100 m, and depending on the depth of the body of water, two to three tubes are suitable.
[0021]
【The invention's effect】
ADVANTAGE OF THE INVENTION By this invention, it became possible to purify a eutrophic water area easily and continuously, and to purify continuously while increasing profit.
[Brief description of the drawings]
FIG. 1 is a diagram showing an outline of the present invention.
FIG. 2 shows a suspension filtration experiment using clams.
FIG. 3 is a diagram showing a characteristic experiment of aeration.
FIG. 4 is a graph showing the results of an aeration characteristic experiment.
Claims (3)
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Cited By (1)
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US7832657B2 (en) | 2005-02-18 | 2010-11-16 | Kabushiki Kaisha Isekogyo | Apparatus for lowering water temperature of sea surface |
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US7832657B2 (en) | 2005-02-18 | 2010-11-16 | Kabushiki Kaisha Isekogyo | Apparatus for lowering water temperature of sea surface |
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