JP2001061370A - Aquatic life based on microorganism-culture solution, activating agent for hydrosphere for breeding it, activation of aquatic life by using the same and breeding of aquatic life - Google Patents
Aquatic life based on microorganism-culture solution, activating agent for hydrosphere for breeding it, activation of aquatic life by using the same and breeding of aquatic lifeInfo
- Publication number
- JP2001061370A JP2001061370A JP28466399A JP28466399A JP2001061370A JP 2001061370 A JP2001061370 A JP 2001061370A JP 28466399 A JP28466399 A JP 28466399A JP 28466399 A JP28466399 A JP 28466399A JP 2001061370 A JP2001061370 A JP 2001061370A
- Authority
- JP
- Japan
- Prior art keywords
- hydrosphere
- aquatic life
- aquatic
- activating
- breeding
- 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
- 230000003213 activating effect Effects 0.000 title claims abstract description 17
- 238000009395 breeding Methods 0.000 title claims description 12
- 230000001488 breeding effect Effects 0.000 title claims description 12
- 230000004913 activation Effects 0.000 title 1
- 244000005700 microbiome Species 0.000 claims abstract description 25
- 241000894006 Bacteria Species 0.000 claims abstract description 21
- 238000000034 method Methods 0.000 claims abstract description 20
- 102000004190 Enzymes Human genes 0.000 claims abstract description 15
- 108090000790 Enzymes Proteins 0.000 claims abstract description 15
- 239000002207 metabolite Substances 0.000 claims abstract description 10
- 230000000243 photosynthetic effect Effects 0.000 claims abstract description 10
- 241000221198 Basidiomycota Species 0.000 claims abstract description 6
- 241000222350 Pleurotus Species 0.000 claims abstract description 5
- 239000012190 activator Substances 0.000 claims description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 16
- 239000013543 active substance Substances 0.000 claims description 9
- 238000000354 decomposition reaction Methods 0.000 claims description 6
- 241000233866 Fungi Species 0.000 claims description 5
- 238000012851 eutrophication Methods 0.000 claims description 4
- 238000009629 microbiological culture Methods 0.000 claims description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 2
- 229910052799 carbon Inorganic materials 0.000 claims description 2
- 241000251468 Actinopterygii Species 0.000 abstract description 14
- 241000195493 Cryptophyta Species 0.000 abstract description 7
- 239000005432 seston Substances 0.000 abstract description 2
- 239000003795 chemical substances by application Substances 0.000 abstract 3
- 241000195628 Chlorophyta Species 0.000 abstract 1
- 230000000740 bleeding effect Effects 0.000 abstract 1
- 238000004140 cleaning Methods 0.000 abstract 1
- 230000009471 action Effects 0.000 description 9
- -1 aromatic organic compound Chemical class 0.000 description 5
- 125000001183 hydrocarbyl group Chemical group 0.000 description 5
- LSDPWZHWYPCBBB-UHFFFAOYSA-N Methanethiol Chemical compound SC LSDPWZHWYPCBBB-UHFFFAOYSA-N 0.000 description 4
- 241000238424 Crustacea Species 0.000 description 3
- 241000192700 Cyanobacteria Species 0.000 description 3
- 241000238557 Decapoda Species 0.000 description 3
- 241001465754 Metazoa Species 0.000 description 3
- 238000009360 aquaculture Methods 0.000 description 3
- 244000144974 aquaculture Species 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 238000012258 culturing Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 230000009467 reduction Effects 0.000 description 3
- 235000015170 shellfish Nutrition 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- UBOXGVDOUJQMTN-UHFFFAOYSA-N 1,1,2-trichloroethane Chemical compound ClCC(Cl)Cl UBOXGVDOUJQMTN-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- VZCYOOQTPOCHFL-OWOJBTEDSA-N Fumaric acid Chemical compound OC(=O)\C=C\C(O)=O VZCYOOQTPOCHFL-OWOJBTEDSA-N 0.000 description 2
- 241000192710 Microcystis aeruginosa Species 0.000 description 2
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 230000004099 anaerobic respiration Effects 0.000 description 2
- MVPPADPHJFYWMZ-UHFFFAOYSA-N chlorobenzene Chemical compound ClC1=CC=CC=C1 MVPPADPHJFYWMZ-UHFFFAOYSA-N 0.000 description 2
- 238000007865 diluting Methods 0.000 description 2
- 125000005843 halogen group Chemical group 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 230000007774 longterm Effects 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 230000009965 odorless effect Effects 0.000 description 2
- 150000002894 organic compounds Chemical class 0.000 description 2
- ZFRKQXVRDFCRJG-UHFFFAOYSA-N skatole Chemical compound C1=CC=C2C(C)=CNC2=C1 ZFRKQXVRDFCRJG-UHFFFAOYSA-N 0.000 description 2
- VZGDMQKNWNREIO-UHFFFAOYSA-N tetrachloromethane Chemical compound ClC(Cl)(Cl)Cl VZGDMQKNWNREIO-UHFFFAOYSA-N 0.000 description 2
- UOORRWUZONOOLO-OWOJBTEDSA-N (E)-1,3-dichloropropene Chemical compound ClC\C=C\Cl UOORRWUZONOOLO-OWOJBTEDSA-N 0.000 description 1
- UOCLXMDMGBRAIB-UHFFFAOYSA-N 1,1,1-trichloroethane Chemical compound CC(Cl)(Cl)Cl UOCLXMDMGBRAIB-UHFFFAOYSA-N 0.000 description 1
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- 241000252229 Carassius auratus Species 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 241000252233 Cyprinus carpio Species 0.000 description 1
- 241000605056 Cytophaga Species 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical group S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 241001559542 Hippocampus hippocampus Species 0.000 description 1
- 241000699670 Mus sp. Species 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- IOVCWXUNBOPUCH-UHFFFAOYSA-N Nitrous acid Chemical compound ON=O IOVCWXUNBOPUCH-UHFFFAOYSA-N 0.000 description 1
- 206010058667 Oral toxicity Diseases 0.000 description 1
- 241000269799 Perca fluviatilis Species 0.000 description 1
- 241000605118 Thiobacillus Species 0.000 description 1
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 1
- 229930003448 Vitamin K Natural products 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 239000004480 active ingredient Substances 0.000 description 1
- 230000004103 aerobic respiration Effects 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical group N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 235000012501 ammonium carbonate Nutrition 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- 239000000987 azo dye Substances 0.000 description 1
- 239000012867 bioactive agent Substances 0.000 description 1
- 230000008238 biochemical pathway Effects 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- KFUSEUYYWQURPO-UPHRSURJSA-N cis-1,2-dichloroethene Chemical group Cl\C=C/Cl KFUSEUYYWQURPO-UPHRSURJSA-N 0.000 description 1
- 238000003776 cleavage reaction Methods 0.000 description 1
- 229910017052 cobalt Inorganic materials 0.000 description 1
- 239000010941 cobalt Substances 0.000 description 1
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 238000005695 dehalogenation reaction Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 238000006356 dehydrogenation reaction Methods 0.000 description 1
- 230000001079 digestive effect Effects 0.000 description 1
- 239000003085 diluting agent Substances 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 230000027721 electron transport chain Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000006911 enzymatic reaction Methods 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 230000004151 fermentation Effects 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 239000001530 fumaric acid Substances 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000001963 growth medium Substances 0.000 description 1
- 229910052736 halogen Inorganic materials 0.000 description 1
- 238000005658 halogenation reaction Methods 0.000 description 1
- 150000002367 halogens Chemical class 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- 230000001771 impaired effect Effects 0.000 description 1
- 150000002484 inorganic compounds Chemical group 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 239000011133 lead Substances 0.000 description 1
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 230000004060 metabolic process Effects 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000005457 optimization Methods 0.000 description 1
- 231100000418 oral toxicity Toxicity 0.000 description 1
- 150000002896 organic halogen compounds Chemical class 0.000 description 1
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N phenol group Chemical group C1(=CC=CC=C1)O ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 1
- SHUZOJHMOBOZST-UHFFFAOYSA-N phylloquinone Natural products CC(C)CCCCC(C)CCC(C)CCCC(=CCC1=C(C)C(=O)c2ccccc2C1=O)C SHUZOJHMOBOZST-UHFFFAOYSA-N 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 150000003071 polychlorinated biphenyls Chemical class 0.000 description 1
- 230000000384 rearing effect Effects 0.000 description 1
- 238000006479 redox reaction Methods 0.000 description 1
- 239000013535 sea water Substances 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 229940074386 skatole Drugs 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- UOORRWUZONOOLO-UHFFFAOYSA-N telone II Natural products ClCC=CCl UOORRWUZONOOLO-UHFFFAOYSA-N 0.000 description 1
- 229910052718 tin Inorganic materials 0.000 description 1
- 239000011135 tin Substances 0.000 description 1
- VZCYOOQTPOCHFL-UHFFFAOYSA-N trans-butenedioic acid Natural products OC(=O)C=CC(O)=O VZCYOOQTPOCHFL-UHFFFAOYSA-N 0.000 description 1
- UYPYRKYUKCHHIB-UHFFFAOYSA-N trimethylamine N-oxide Chemical compound C[N+](C)(C)[O-] UYPYRKYUKCHHIB-UHFFFAOYSA-N 0.000 description 1
- 235000019168 vitamin K Nutrition 0.000 description 1
- 239000011712 vitamin K Substances 0.000 description 1
- 150000003721 vitamin K derivatives Chemical class 0.000 description 1
- 229940046010 vitamin k Drugs 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Landscapes
- Farming Of Fish And Shellfish (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、(a)好気性微生物
群、(b)嫌気性微生物群、(c)少なくとも1種のヒ
ラタケ科に属する担子菌類、(d)光合成菌類とが共生
し、かつこれらの微生物群代謝物由来の酵素及び炭素分
解酵素を含む微生物培溶液(以下、OMEと略称する)
を、水性生物を活性化するのと同時にその生活環境であ
る水圏を改善する用途に関する。The present invention relates to (a) an aerobic microorganism group, (b) an anaerobic microorganism group, (c) a basidiomycete belonging to at least one kind of Pleurotus, and (d) a photosynthetic fungus. And a microorganism culture solution containing an enzyme derived from these microorganism group metabolites and a carbon-decomposing enzyme (hereinafter abbreviated as OME)
The present invention relates to a use for activating an aquatic organism and at the same time improving a hydrosphere as its living environment.
【0002】[0002]
【従来の技術】近年、各家庭、養殖業者や水族館等で、
金魚、鯉、熱帯魚等の観賞用の魚、熱帯産の蟹、海老等
の鑑賞用の甲殻、貝類類等の養殖や飼育や、食用の魚、
甲殻類等の養殖等において、いわゆる生簀や水槽等が使
用されている。以下、本発明においてこのような飼育に
供される水性の生物を水性生物と言う。これらの水性生
物は、生簀や水槽で長期間飼育されると、飼育環境によ
っては水性生物の排出物や藻類の繁殖により生活環境で
ある水圏が著しく汚染されてしまうことがあった。ま
た、釣堀や、養殖場等の開放型の環境では、水圏の冨栄
養化によるアオコ等の発生やセストンの発生等や、ケミ
カルハザード等の流入により、水性生物の飼育環境が著
しく阻害されてしまう場合がある。また、水性生物を水
槽等の閉鎖環境下で飼育する場合には、水圏の水質を一
定に維持するために、水を頻繁に交換したり、水槽、室
内用の生簀等の周りに付着した藻類を頻繁に洗浄する必
要があった。2. Description of the Related Art In recent years, at homes, aquaculture companies, aquariums, and the like,
Ornamental fish such as goldfish, carp, tropical fish, tropical crabs, shellfish for watching shrimp, etc., cultivation and rearing of shellfish, etc., edible fish,
In aquaculture of crustaceans and the like, so-called fish cages and aquariums are used. Hereinafter, in the present invention, the aqueous organisms provided for such breeding are referred to as aqueous organisms. When these aquatic organisms are bred for a long time in a cage or an aquarium, depending on the breeding environment, the aquatic environment, which is a living environment, may be significantly contaminated by the discharge of aquatic organisms and the propagation of algae. Also, in open environments such as fishing ponds and fish farms, the breeding environment of aquatic organisms is significantly impaired by the occurrence of blue-green algae and sestons due to eutrophication of the hydrosphere, and the inflow of chemical hazards and the like. There are cases. When breeding aquatic organisms in a closed environment such as an aquarium, the water must be changed frequently or algae attached to the aquarium, indoor cages, etc. must be maintained in order to maintain the water quality in the aquatic area. Had to be washed frequently.
【0003】また、鑑賞用の魚類等の水性生物は、高価
なものが多く、また遠方地、特に海外から船舶や飛行機
等により輸入される場合が多く、これらの場合には水圏
の汚染とともに、環境の変化により水性生物が著しく衰
弱する場合があり、これらの搬送には注意を要する。従
って、これらの衰弱した水性生物を賦活させたいという
要望がある。また、近年鑑賞用の水生植物に対する価値
観が変わってきており、種々の環境で水性生物を飼育し
たいという要望もある。[0003] In addition, many aquatic organisms such as fish for appreciation are expensive and are often imported from distant places, especially from overseas, by ship or airplane. Aquatic organisms can be significantly degraded due to environmental changes and care must be taken in their transport. Therefore, there is a demand for activating these weakened aquatic organisms. Also, in recent years, the value of aquatic plants for appreciation has changed, and there is a demand for raising aquatic organisms in various environments.
【0004】[0004]
【発明が解決しようとする課題】従って、本発明の課題
は、水槽等の閉鎖環境や、例えば海等に設けられた開放
型の環境に拘わらず、これらの水性生物を活性化させる
のと同時に、これらの水性生物の生活圏である水圏を一
定の状態に維持できる活性剤および方法を提供すること
である。本発明の別の課題は、多種多様となった水性生
物を閉鎖環境においても容易に飼育可能とする方法を提
供することである。SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to simultaneously activate these aqueous organisms regardless of the closed environment such as a water tank or the open environment provided in the sea or the like. It is an object of the present invention to provide an activator and a method capable of maintaining a constant state of the hydrosphere, which is the living area of these aquatic organisms. Another object of the present invention is to provide a method for easily breeding a wide variety of aquatic organisms even in a closed environment.
【0005】[0005]
【課題を解決するための手段】本発明者は、上記課題に
鑑みて鋭意検討した結果、(a)好気性微生物群、
(b)嫌気性微生物群、(c)少なくとも1種のヒラタ
ケ科に属する担子菌類、(d)少なくとも緑色細菌を必
須成分として含む光合成菌類とが共生し、かつこれらの
微生物群代謝物由来の酵素及び炭素分解酵素を含むこと
を特徴とする微生物培溶液を含むことを特徴とする微生
物培溶液を活性剤として使用すると、水性生物が生育す
る水圏が浄化されるだけでなく、水性生物そのものを賦
活化することができることを見出して、本発明を創作す
るに至った。Means for Solving the Problems The present inventors have made intensive studies in view of the above problems and found that (a) a group of aerobic microorganisms,
(B) anaerobic microorganisms, (c) basidiomycetes belonging to at least one kind of Pleurotus, (d) photosynthetic fungi containing green bacteria as an essential component, and enzymes derived from metabolites of these microorganisms The use of a microbial culture solution characterized by containing a microbial culture solution characterized by the fact that it contains carbon-degrading enzymes not only purifies the hydrosphere in which aquatic organisms grow, but also activates the aquatic organisms themselves. The inventors have found that the present invention can be used, and have led to the creation of the present invention.
【0006】すなわち、本発明は、水性生物を活性化さ
せ、かつ前記水性生物を飼育する水圏を最適化する微生
物およびその代謝物に基づく活性剤であって、(a)好
気性微生物群、(b)嫌気性微生物群、(c)少なくと
も1種のヒラタケ科に属する担子菌類、(d)少なくと
も緑色細菌を必須成分として含む光合成菌類とが共生
し、かつこれらの微生物群代謝物由来の酵素及び炭素分
解酵素を含む微生物培溶液を含むことを特徴とする、活
性剤に関する。That is, the present invention relates to an activator based on a microorganism and a metabolite thereof that activates an aqueous organism and optimizes the aquatic area in which the aqueous organism is bred, and (a) a group of aerobic microorganisms, b) anaerobic microorganisms, (c) basidiomycetes belonging to at least one kind of Pleurotus, (d) photosynthetic fungi containing green bacteria as an essential component, and enzymes derived from metabolites of these microorganisms. The present invention relates to an activator, comprising a microbial culture solution containing a carbon-decomposing enzyme.
【0007】本発明はまた、水性生物を活性化させるの
と同時に、かつ前記水性生物を飼育する水圏を最適化す
る方法であって、前記活性剤を、水性生物の生活圏であ
る水圏に投入し、水圏を浄化するとともに水性生物を活
性化させることを特徴とする、方法に関する。前記方法
は、冨栄養化現象により汚染された水圏や閉鎖型の水圏
に適用可能である。また、前記方法において、水圏1リ
ットルに対して、前記活性剤を0.01〜1.0cc添
加することが好ましい。なお、本発明において使用され
る用語「水性生物を活性化する」とは、水圏の汚染、高
い個体密度、長期間の輸送等で消耗、衰弱した水性動物
を賦活化することを意味する。[0007] The present invention is also a method for optimizing the aquatic zone for breeding the aquatic organisms while activating the aquatic organisms, wherein the activator is introduced into the aquatic area where the aquatic organisms live. And purifying the hydrosphere and activating aqueous organisms. The method is applicable to a hydrosphere contaminated by eutrophication or a closed hydrosphere. Further, in the above method, it is preferable to add 0.01 to 1.0 cc of the activator to 1 liter of hydrosphere. The term "activate aquatic organisms" used in the present invention means activating aquatic animals that have been consumed or weakened due to contamination of the aquatic area, high population density, long-term transportation, and the like.
【0008】本発明はさらに、水性生物を活性化する方
法であって、前記活性剤を、対象となる水性生物に適用
することを特徴とする、水性生物の活性化方法に関す
る。さらにまた、本発明は、水性生物の飼育方法であっ
て、前記の活性剤を飼育しようとする水性生物の水圏に
投入することを特徴とする、水性生物の飼育方法に関す
る。この方法によると、水性生物を密閉容器内、ペンダ
ント等のアクセサリ内で飼育することも可能となる。[0008] The present invention further relates to a method for activating an aqueous organism, wherein the activator is applied to a target aqueous organism. Furthermore, the present invention relates to a method for breeding an aqueous organism, which comprises introducing the active agent into the hydrosphere of the aqueous organism to be bred. According to this method, it is possible to breed an aqueous organism in a closed container or an accessory such as a pendant.
【0009】[0009]
【発明の実施の形態】以下、本発明を詳細に説明する。
本発明の対象となる水性生物とは、水中で生活し人によ
り飼育または養殖されるものであれば特に制限されるも
のではなく、鑑賞・食用の淡水産または海水産の魚類、
甲殻類、貝類が含まれる。また、本発明においける水圏
は、家庭用・養殖業社用、輸送用、食堂、水族館等の水
槽のような閉鎖系であっても、海や河川、湖沼等に設置
された生簀等の開放系であってもよい。本発明において
水性生物を活性化させ、かつ前記水性生物を飼育する水
圏を最適化する微生物およびその代謝物に基づく活性剤
とは、水性生物、例えば長期間の輸送や、個体密度が過
剰、水質の汚染等の種々の理由で消耗・衰弱した水性生
物を賦活させる能力を有し、かつその水性生物の生息す
る水圏に含まれる藻類、代表的にはアオコや、水槽に付
着した藻等を除去し、かつ水性生物の排出物、水中に含
まれる塩素イオン等の水性生物の繁殖に好ましくない環
境を改善する能力を有するものであり、具体的には本願
発明者が出願した非公開のPCT/JP99/1234
6号明細書に詳細に記載されているOMEまたはその希
釈液がベースとなる。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail.
Aqueous organisms that are the subject of the present invention are not particularly limited as long as they live in the water and are bred or cultivated by humans, and appreciable and edible freshwater or marine fish,
Crustaceans and shellfish are included. In addition, the hydrosphere in the present invention may be used for homes and aquaculture companies, for transportation, in canteens, and in closed systems such as aquariums such as aquariums, but also for fish cages installed in the sea, rivers, lakes and marshes. It may be an open system. In the present invention, an activator based on a microorganism and a metabolite thereof that activates the aquatic organism and optimizes the hydrosphere in which the aquatic organism is bred refers to an aquatic organism, for example, long-term transport, an excessively high individual density, and water quality. It has the ability to activate aquatic organisms that have been depleted or weakened due to various reasons such as pollution, and removes algae contained in the aquatic area where the aquatic organisms inhabit, such as blue-green algae and algae attached to the aquarium. And has the ability to improve the environment unfavorable for the propagation of aquatic organisms such as effluents of aqueous organisms and chloride ions contained in water. Specifically, the PCT / JP99 / 1234
The base is OME or a diluent thereof as described in detail in the specification of US Pat.
【0010】具体的には本発明において活性剤として使
用されるOMEとは、特定の培養基として本発明者が先
に出願した生物活性剤中で好気性微生物および特定の担
子菌類とを培養し、次いでこの培養液中で嫌気性微生物
を培養することによって得られた微生物群とその代謝物
である酵素との混合液に植物由来の炭素源を添加して炭
素分解酵素を産生させた、異なる微生物群が共生し、こ
れらの代謝物としての酵素と炭素分解酵素とを含む溶液
をベースとして、光合成細菌として少なくとも緑色細菌
を含む溶液のことを言う。かかる活性剤は、PCT/J
P99/12346号明細書に記載されたOMEの製造
方法において、光合成細菌の培養する際に、緑色細菌を
投入して培養することによって得られる。また、OME
に緑色細菌を添加してもよい。[0010] Specifically, the OME used as an active agent in the present invention means that an aerobic microorganism and a specific basidiomycete are cultured in a bioactive agent previously applied for by the present inventors as a specific culture medium, Next, a different microorganism obtained by adding a plant-derived carbon source to a mixture of a microorganism group obtained by culturing an anaerobic microorganism in this culture solution and an enzyme that is a metabolite thereof to produce a carbon-degrading enzyme. It refers to a solution containing at least green bacteria as a photosynthetic bacterium based on a solution in which a group coexists and contains an enzyme as a metabolite and a carbon-degrading enzyme. Such activators are PCT / J
In the method for producing OME described in the specification of P99 / 12346, when culturing photosynthetic bacteria, it is obtained by introducing and culturing green bacteria. Also, OME
Green bacteria may be added to the mixture.
【0011】このようにして得られた本発明の活性剤
は、通常300〜3000倍、好ましくは500〜20
00倍に水で希釈して使用する。この活性剤のベースと
なるOMEは、前記国際特許出願で明らかにされている
通りマウスの経口毒性試験で無害であることが証明され
ており、種々の対象となる水性生物に適用可能である。
また、水圏の最適化に関して以下に挙げるような特徴を
有している。The activator of the present invention thus obtained is usually 300 to 3000 times, preferably 500 to 20 times.
Dilute with water 00 times before use. The OME on which this active agent is based has been shown to be harmless in oral toxicity tests in mice, as disclosed in the international patent application, and is applicable to various aqueous organisms of interest.
It also has the following features regarding optimization of the hydrosphere.
【0012】炭素質の溶解作用を有している。OME活
性成分中には、炭素質分解酵素が含まれているためと仮
定できる。処理対象物により選択的に下記の微生物・酵
素反応を起こす I. 加水分解反応 a. RCO−NHR’+H2O→RCOOH+R’NH2 b. RCO−OR’+H2O→RCOOH+4R’OH c. RCO−SR’+H2O→RCOOH+4R’SH d. R−CH−OR’+H2O→RH+HO−CH−OR’ (式中、R、R’は各々独立して置換されてもよい炭化水素基を表す。) II 開裂反応 a. RCOOH→RH+CO2 b. HOCRH−CR’H−OH→RCH2OH+R’CHO (式中、R、R’は各々独立して置換されてもよい炭化水素基を表す。) III.酸化還元反応 a. AH2+B→A+BH2 b. AH2+O2→A+H2O2 IV 脱水素反応 a. CRR’H−CR”H−OH→RR’C=CR”H+H2O b. CRR’H−CR”H−NH2→RR’C=CR”H+NH2 (式中、R、R’、R”は各々独立して置換されてもよい炭化水素基を表す。) V. 脱水素ハロゲン化反応 a. RCX−CR’H→RC=CR’+HX (式中、Rは置換されてもよい炭化水素基を表し、そしてXはハロゲン原子を表 す。) VI. 置換反応 a. RXCH2+H2O→RCH2OH+HX b. RXCH2+HS−→RCH2SH+X− (式中、Rは置換されてもよい炭化水素基を表し、そしてXはハロゲン原子を表 す。)フェノール性OHおよびハロゲンの脱離反応It has a carbonaceous dissolving action. It can be assumed that the OME active ingredient contains a carbon-degrading enzyme. The following microbial / enzymatic reactions occur selectively depending on the substance to be treated. Hydrolysis reaction a. RCO-NHR ′ + H 2 O → RCOOH + R′NH 2 b. RCO-OR ′ + H 2 O → RCOOH + 4R′OH c. RCO-SR ′ + H 2 O → RCOOH + 4R′SH d. R—CH—OR ′ + H 2 O → RH + HO—CH—OR ′ (wherein, R and R ′ each independently represent a hydrocarbon group which may be substituted.) II Cleavage reaction a. RCOOH → RH + CO 2 b. HOCRH-CR'H-OH → RCH 2 OH + R'CHO ( where, R, R 'each represent independently optionally substituted hydrocarbon group.) III. Redox reaction a. AH 2 + B → A + BH 2 b. AH 2 + O 2 → A + H 2 O 2 IV dehydrogenation reaction a. CRR'H-CR "H-OH → RR'C = CR" H + H 2 O b. CRR'H-CR "H-NH 2 → RR'C = CR" H + NH 2 ( wherein, R, R ', R "each represent independently optionally substituted hydrocarbon group.) V. dehydration Halogenation reaction a. RCX-CR'H → RC = CR '+ HX (wherein R represents an optionally substituted hydrocarbon group and X represents a halogen atom) VI. Substitution reaction a. RXCH 2 + H 2 O → RCH 2 OH + HX b. RXCH 2 + HS − → RCH 2 SH + X − (wherein R represents a hydrocarbon group which may be substituted, and X represents a halogen atom.) Phenolic OH And halogen elimination reactions
【0013】重金属除去作用 OMEは、亜鉛、鉛、錫、ニッケル、クロム、銅、コバ
ルト、マンガン、水銀、カドミウム、半導体中のドロス
成分等の重金属を除去する作用がある。 有機化合物の分解作用 上記の脱ハロゲン作用により、有機ハロゲン化合物、例
えばダイオキシン類、ポリ塩化ビフェニル類、クロロベ
ンゼン等のハロゲン置換された芳香族有機化合物やテト
ラクロロエチレン、トリクロロエチレン、ジクロロメタ
ン、四塩化炭素、1,2−ジクロロエチレン、1,1−
ジクロロエチレン、シス−1,2−ジクロロエチレン、
1,1,1−トリクロロエタン、1,1,2−トリクロ
ロエタン、1,3−ジクロロプロペン等の脂肪族有機ハ
ロゲン化合物の分解が可能である他、アゾ染料等の色素
の分解、メチルメルカプタン、カプタン類、イドール、
スカトール等の有機化合物の分解作用を有している。Heavy Metal Removal Action OME has an action of removing heavy metals such as zinc, lead, tin, nickel, chromium, copper, cobalt, manganese, mercury, cadmium, and dross components in semiconductors. Decomposition action of organic compound By the above dehalogenation action, an organic halogen compound, for example, a halogen-substituted aromatic organic compound such as dioxins, polychlorinated biphenyls, and chlorobenzene, tetrachloroethylene, trichloroethylene, dichloromethane, carbon tetrachloride, 1,2 -Dichloroethylene, 1,1-
Dichloroethylene, cis-1,2-dichloroethylene,
It is capable of decomposing aliphatic organic halogen compounds such as 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,3-dichloropropene, decomposing pigments such as azo dyes, methyl mercaptan, and captans. , Idol,
It has the action of decomposing organic compounds such as skatole.
【0014】無機化合物の分解作用 窒素の還元:OME中に含まれる嫌気性及び通性嫌気性
化学合成従属栄養菌は、嫌気的呼吸か発酵のどちらかの
しくみを持つ。嫌気的呼吸は、好気的代謝(好気的呼
吸)と本質的に同じ生化学経路であり、電子伝達鎖の最
終電子受容体が酸素の代わりに、硝酸(NO3 −)、硫
酸(SO4 2−)、フマル酸又はトリメチルアミンオキ
シドである。NO3 −、SO4 2−の場合、還元産物の
最終電子受容体として働く。NO3 −の還元の際、脱窒
菌により、NO3 −はNO2 −となり、更に還元されて
N2Oとなり、最終的にはN2ガスを生産する、OM及
びOME中の脱窒能を持つ代表的細菌は、Rhodob
acter、Thiobacillus、Cytoph
aga等である。Decomposition of inorganic compounds Reduction of nitrogen: Anaerobic and facultative anaerobic chemoheterotrophs contained in OME have a mechanism of either anaerobic respiration or fermentation. Anaerobic respiration is essentially the same biochemical pathway as aerobic metabolism (aerobic respiration), where the final electron acceptor of the electron transport chain is nitrate (NO 3 − ), sulfuric acid (SO 2) instead of oxygen. 4 2-), fumaric acid or trimethylamine oxide. In the case of NO 3 − and SO 4 2− , it functions as a final electron acceptor of a reduction product. During the reduction, the denitrifying bacteria, NO 3 - - NO 3 is NO 2 -, and the further reduced N 2 O, and the ultimately produce N 2 gas, the denitrification in the OM and OME A typical bacterium having is Rhodob.
acter, Thiobacillus, Cytoph
aga and the like.
【0015】アンモニアの分解 OM又はOME中で下記反応によりアンモニアは無臭と
なる。 2NH3+H2O+CO2→(NH4)2CO3 2(NH4OH)+H2O+CO2 →(NH4)2C
O3+2H2O アンモニア水の場合も、炭酸アンモニウムを呈し、酸素
の供給が少ない場合はアンモニウムイオン(NH4 −)
は、消化細菌等により亜硝酸から硝酸へと変化し無臭と
なる。 2NH3+202→2NHO+H2O 2NHO2+O2→2NHO3 Decomposition of ammonia Ammonia is made odorless in OM or OME by the following reaction. 2NH 3 + H 2 O + CO 2 → (NH 4) 2 CO 3 2 (NH 4 OH) + H 2 O + CO 2 → (NH 4) 2 C
O 3 + 2H 2 O ammonia water also presents ammonium carbonate, and when the supply of oxygen is small, ammonium ions (NH 4 − )
Is changed from nitrous acid to nitric acid by digestive bacteria and the like, and becomes odorless. 2NH 3 +20 2 → 2NHO + H 2 O 2NHO 2 + O 2 → 2NHO 3
【0016】硫化水素(H2S)の分解 2H2S+O2→2NHO2+H2O メチルメルカプタン(CH3SH)の分解 2CH3SH+O2→2CH3OH+S 2CH3OH+2O2→2CO2+H2O セストンの分解作用 OMEをセストンを含有する水圏に投入すると、セスト
ンを分解する作用を有している。 アオコの除去作用 OMEを水圏の富栄養化によって水面に発生したアオコ
に適用すると瞬時にして分解除去する作用を有してい
る。OMEは無害である。Decomposition of hydrogen sulfide (H 2 S) 2H 2 S + O 2 → 2NHO 2 + H 2 O Decomposition of methyl mercaptan (CH 3 SH) 2CH 3 SH + O 2 → 2CH 3 OH + S 2CH 3 OH + 2O 2 → 2CO 2 + H 2 O Seston When OME is put into a hydrosphere containing sestone, it has an effect of decomposing sestone. Water-bloom removal action When OME is applied to water-bloom generated on the water surface due to eutrophication of the hydrosphere, it has an action of instantly decomposing and removing it. OME is harmless.
【0017】このようなOMEの特徴に加えて、光合成
菌類として少なくとも緑色細菌を含んだ本発明による活
性剤は、さらに驚くべきことに、このような水性生物を
飼育する水圏に投入すると、また水槽、生簀のガラスや
コンクリート等に付着した藻類を分解除去する作用を有
していることを見出した。In addition to these OME features, the activators according to the invention, which comprise at least green bacteria as photosynthetic fungi, are, more surprisingly, introduced into the aquatic zone where such aquatic organisms are raised, and It has been found that it has an action of decomposing and removing algae adhering to glass, concrete and the like of a fish cage.
【0018】さらに、消耗・衰弱した水性動物、例えば
海外から長時間かけて輸送されている間に疲弊した魚類
や甲殻類が投入された水圏に本発明による活性剤を滴下
したところ瞬時にして賦活されることを見出した。具体
的にはフィリピンから空輸されその状態のままでは約1
日で半数以上が死滅するオトヒメエビに緑色細菌を含む
OMEを1000倍に希釈して得られた本発明の活性剤
を添加したところ、環境を変化させず、2週間以上の生
息が確認された。このことは、本発明による活性剤中に
含まれる緑色細菌やシアノバクテリア等の相互作用によ
り、水圏がビタミンKや酸素放出型の水圏へと転換され
るものと予測される。なお、本発明による活性剤は、光
合成細菌のうち、少なくとも緑色細菌を含むことが必須
であり、実質的に光合成細菌の全てが緑色細菌であるこ
とが好ましい。Furthermore, when the activator according to the present invention is dripped into a water sphere into which a depleted or weakened aqueous animal, for example, a fish or a crustacean exhausted while being transported from abroad for a long time, is activated instantaneously. Found to be. Specifically, it is about 1 in the state of airlift from the Philippines
When the activator of the present invention obtained by diluting OME containing green bacteria 1000-fold to the shrimp shrimp that kills more than half a day was added, the inhabitants for more than 2 weeks were confirmed without changing the environment. This is expected that the interaction of green bacteria and cyanobacteria contained in the active agent according to the present invention will convert the hydrosphere into vitamin K or an oxygen releasing hydrosphere. It is essential that the activator according to the present invention contains at least green bacteria among photosynthetic bacteria, and it is preferable that substantially all of the photosynthetic bacteria are green bacteria.
【0019】また、驚くべきことに、通常は飼育するの
が困難な密閉系、例えば直径数センチメートルの球体中
に約8割程度の水を入れた密閉系中で小型の魚類を数ヶ
月に渡って飼育することが可能であった。具体的には、
直径約2〜3cmのプラスチック製の容器に水1リット
ルに対してOMEの1000倍希釈液0.1ccを添加
した水を入れ、全長1〜1.5cm程度の魚であるアカ
ヒレを飼育することが可能となった。また、海水約2リ
ットルに対して緑色細菌を含むOMEを1000倍に希
釈して得られた本発明の活性剤約1ccを添加したした
ところ、従来飼育が困難であったタツノオトシゴを飼育
することが可能となった。Also, surprisingly, small fish can be stored in a closed system, which is usually difficult to breed, for example, in a closed system containing about 80% of water in a sphere having a diameter of several centimeters. It was possible to breed across. In particular,
A plastic container having a diameter of about 2 to 3 cm is filled with water in which 1 liter of OME is added with 0.1 cc of a 1000-fold diluted solution per liter of water, and a red fin, a fish having a total length of about 1 to 1.5 cm, can be bred. It has become possible. Further, when about 1 cc of the active agent of the present invention obtained by diluting OME containing green bacteria 1000 times with respect to about 2 liters of seawater was added, it was possible to breed a seahorse which was difficult to breed conventionally. It has become possible.
【0020】所望に応じて、本発明者によるPCT/J
P99/12346号明細書に記載されている、DCP
またはRCS等を水圏に散布することによって、本発明
による効果をさらに向上することも可能である。If desired, PCT / J by the inventor
DCP described in P99 / 12346
Alternatively, the effects of the present invention can be further improved by dispersing RCS or the like in the hydrosphere.
【0021】[0021]
【発明の効果】以上説明した通り、本発明は次の優れた
効果を奏する。 1.本発明の活性剤を使用すると、閉鎖環境や開放環境
に拘わらず、疲弊した水性生物を賦活可能であるのと同
時に、水性生物の水圏中に存在するアオコ、藻類、排泄
物、セストン等や化学工業等から放出されたケミカルハ
ザード等を浄化処理可能である。 2.また、このようにして本発明による活性剤を含む水
圏において、水性動物を有効に飼育することが可能とな
る。特に、密閉系においても、小魚等を長期間にわたっ
て飼育することが可能となる。As described above, the present invention has the following excellent effects. 1. When the activator of the present invention is used, exhausted aquatic organisms can be activated irrespective of a closed environment or an open environment, and at the same time, blue water, algae, excrement, seston, etc. existing in the aquatic sphere of the aquatic organism. It is possible to purify chemical hazards and the like released from industry and the like. 2. In addition, in this way, it is possible to effectively breed aqueous animals in the hydrosphere containing the active agent according to the present invention. In particular, even in a closed system, small fish and the like can be bred for a long period of time.
Claims (9)
を飼育する水圏を最適化する微生物およびその代謝物に
基づく活性剤であって、(a)好気性微生物群、(b)
嫌気性微生物群、(c)少なくとも1種のヒラタケ科に
属する担子菌類、(d)少なくとも緑色細菌を必須成分
として含む光合成菌類とが共生し、かつこれらの微生物
群代謝物由来の酵素及び炭素分解酵素を含む微生物培溶
液を含むことを特徴とする、活性剤。1. An activator based on a microorganism and a metabolite thereof for activating an aquatic organism and optimizing a hydrosphere for breeding the aquatic organism, comprising: (a) a group of aerobic microorganisms;
Anaerobic microorganisms, (c) Basidiomycetes belonging to at least one kind of Pleurotus, (d) Photosynthetic fungi containing at least green bacteria as essential components, and enzymes and carbon decomposition derived from metabolites of these microorganisms An activator, comprising a microbial culture solution containing an enzyme.
前記水性生物を飼育する水圏を最適化する方法であっ
て、請求項1に記載の活性剤を、水性生物の生活圏であ
る水圏に投入し、水圏を浄化するとともに水性生物を活
性化させることを特徴とする、方法。2. A method for optimizing the aquatic zone for breeding said aquatic organisms simultaneously with activating the aquatic organisms, wherein the activator according to claim 1 is used as a living area for the aquatic organisms. A method for purifying a hydrosphere and activating aquatic organisms.
水圏であることを特徴とする請求項2に記載の方法。3. The method of claim 2, wherein said hydrosphere is a hydrosphere contaminated by eutrophication.
とする請求項2に記載の方法。4. The method of claim 2, wherein said hydrosphere is a closed hydrosphere.
01〜1.0cc添加することを特徴とする、請求項2
ないし4のいずれか一つに記載の方法。5. The method according to claim 1, wherein the activator is used in an amount of 0.1 to 1 liter of the hydrosphere.
3. The method according to claim 2, wherein the addition amount is from 0.1 to 1.0 cc.
5. The method according to any one of items 4 to 4.
て、請求項1に記載の活性剤を、対象となる水性生物に
適用することを特徴とする、水性生物の活性化方法。6. A method for activating a weakened aqueous organism, the method comprising activating the active agent according to claim 1 to a target aqueous organism.
記載の活性剤を飼育しようとする水性生物の水圏に投入
することを特徴とする、水性生物の飼育方法。7. A method for breeding aquatic organisms, which comprises introducing the active agent according to claim 1 into the hydrosphere of the marine organism to be bred.
ることを特徴とする請求項6に記載の水性生物の飼育方
法。8. The method according to claim 6, wherein the aqueous organism is bred in a closed container.
項1に記載の活性剤を含む水、および少なくとも1匹の
水性生物を含むアクセサリー。9. An accessory comprising an airtight container, water containing the active agent of claim 1 enclosed in said airtight container, and at least one aqueous organism.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP28466399A JP2001061370A (en) | 1999-08-30 | 1999-08-30 | Aquatic life based on microorganism-culture solution, activating agent for hydrosphere for breeding it, activation of aquatic life by using the same and breeding of aquatic life |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP28466399A JP2001061370A (en) | 1999-08-30 | 1999-08-30 | Aquatic life based on microorganism-culture solution, activating agent for hydrosphere for breeding it, activation of aquatic life by using the same and breeding of aquatic life |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2001061370A true JP2001061370A (en) | 2001-03-13 |
Family
ID=17681380
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP28466399A Pending JP2001061370A (en) | 1999-08-30 | 1999-08-30 | Aquatic life based on microorganism-culture solution, activating agent for hydrosphere for breeding it, activation of aquatic life by using the same and breeding of aquatic life |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2001061370A (en) |
-
1999
- 1999-08-30 JP JP28466399A patent/JP2001061370A/en active Pending
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Bentzon‐Tilia et al. | Monitoring and managing microbes in aquaculture–Towards a sustainable industry | |
| Rurangwa et al. | Microorganisms in recirculating aquaculture systems and their management | |
| Tanikawa et al. | Effluent treatment in an aquaponics-based closed aquaculture system with single-stage nitrification–denitrification using a down-flow hanging sponge reactor | |
| Menasveta et al. | Design and function of a closed, recirculating seawater system with denitrification for the culture of black tiger shrimp broodstock | |
| DeLong et al. | How to start a biofilter. | |
| Pérez-Rostro et al. | Biofloc, a technical alternative for culturing Malaysian prawn Macrobrachium rosenbergii | |
| CN104150612A (en) | Methods of improving the yield and/or quality of aquatic or marine animals | |
| Gross et al. | Soil nitrifying enrichments as biofilter starters in intensive recirculating saline water aquaculture | |
| WO2003053143A2 (en) | Method and apparatus for butane-enhanced aquatic plant and animal growth | |
| CN113308377A (en) | Microalgae culture medium, culture method thereof and culture water purification method | |
| JP6512467B1 (en) | Method of reforming aquaculture tank, and method of aquaculture | |
| CN109650546A (en) | A kind of method of method and water purifying based on Daphnia magna removal water body cyanobacteria | |
| JP2001061370A (en) | Aquatic life based on microorganism-culture solution, activating agent for hydrosphere for breeding it, activation of aquatic life by using the same and breeding of aquatic life | |
| Rejish Kumar et al. | Mass production of nitrifying bacterial consortia for the rapid establishment of nitrification in saline recirculating aquaculture systems | |
| Suantika et al. | Closed aquaculture system: Zero water discharge for shrimp and prawn farming in Indonesia | |
| WO2009128770A1 (en) | Method of treating a marine object | |
| JP2001220306A (en) | Activator for animal and plant based on microorganism/ enzyme culture fluid, method for activating aquatic organism using the same, activation method for animal tissue and activation method for plant | |
| JPH09192690A (en) | Biological nitrating and denitrifying method | |
| JP2005058137A (en) | Water quality-purifying agent, immunopotentiator and method for rearing or culturing aquatic life | |
| Dahle | Microbial community dynamics in water and biofilm of recirculating aquaculture systems (RAS) | |
| JP5876487B2 (en) | Aquatic organism and liquid treatment method | |
| Horowitz et al. | Toxicity tests to assess the effect of a synthetic tank liner on shrimp survival and nitrification in a recirculating superintensive production system | |
| JP2005328735A (en) | Method for culturing fishes or shellfishes and fish or shellfish-culturing apparatus used for the method | |
| JP2974097B2 (en) | How to maintain the aquatic environment | |
| CN206462214U (en) | The device of nitrogen content is not increased while a kind of low power consuming increase oxygen content of water |