KR101854016B1 - Feed additive including organic compounds in biofloc and method for production thereof - Google Patents

Abstract

The present invention provides a feed additive comprising a bioflavable organic material, wherein the feed additive comprises, as a main component, a suspended material suspended in water formed in the breeding water in a biofract form, A step (B) of cultivating cultured fish in the bioflocculation water produced in the step (A), a step (C) of collecting a bioflak solid adiabatic fluid in the water of step (B), the step (C) (D) a step of drying the bioflavonoid fluid collected in step (D), and (E) a step (E) of pulverizing the dried biofloat in step (D) to produce a culture fish feed additive. The present invention provides a method for producing a feed additive including an organic matter, thereby reducing the cost associated with disposal of wastes generated in a bioflavon farm, It is possible to produce functional feed additive, which can contribute to increase income of aquaculture farmer.

Description

[0001] The present invention relates to a feed additive including bioflavable organic materials and a method for producing the same,

The present invention relates to a feed additive comprising a bioflavable organic material and a production method thereof, and more particularly, to a bioflavable organic material comprising a bioflavable organic material as a main component, To a feed additive and a production method thereof.

Korea's marine aquaculture can be classified into marine cage culture, onshore water tasting and festival ceremony, except for inland water culture. Of these, marine caged aquaculture is the largest and the supply of fish is also the largest. However, in the case of marine cage culture, there are many factors that can not be controlled, such as typhoons, high temperature or low temperature, which are highly influenced by the natural environment. On the other hand, land-based aquaculture has little impact on the natural environment while cultivating on land or indoors, and is easy to control factors such as water temperature, dissolved oxygen, water quality and disease.

However, on-shore aquaculture is difficult to raise in the case of sea-aquaculture, and in the case of continual return of breeding water, it is costly to sterilize or filter, or if filtration is not done properly, it is exposed to harmful bacteria and virus inflow There was difficulty. Therefore, a recirculating aquaculture system (RAS) for filtrating and reusing the reared water and a Shallow Raceway System (SRS) for constantly feeding the reared water in a multi-layer water tank have been developed in the aquacultural aquaculture system. Biofloat technology, which is capable of decomposing pollutants and cultivating beneficial microorganisms in fish farms with fish, has gained popularity in recent years.

BioFloc technology is used to cultivate useful microorganisms and cultured species of heterotrophic bacteria and autotrophic bacteria and to cultivate ammonia in breeding water It is a method of cultivation that can decompose harmful organic byproducts into fish and turn them into food that can be consumed by the aquaculture fish, as well as purifying the water, thereby eliminating the need for water or filtration in the aquaculture process.

Biofloat technology was first applied to actual farming in Israel in the early 1990s, and in Korea in the mid-2000s, it started researching the ecosystem of non-recirculating ecological shrimp farming. In 2009, the National Fisheries Research & At the center, the first commercial-scale house facility was used to successfully establish the circulation-free ecological circulation of shrimp.

Biofrok cultivation technology is an eco-friendly method that purifies the water quality by converting ammonia into organic matter in the raising water by inducing nitrification, denitrification, and photosynthesis process of environmentally beneficial microorganisms by controlling the ratio of carbon and nitrogen in the raising water. Using biofloat technology, organic matter can be degraded about 10 to 100 times faster than algae degradation, which makes it possible to keep the water quality suitable for aquaculture. In addition, this technology can create a closed breeding system that can prevent the inflow of viruses, pathogens and parasites, etc., by the return of water during the aquaculture process, so that it can control the viral infection, etc., and the use of antibiotics It can be dramatically reduced. It is also possible to produce aquaculture regardless of the season, because the aquaculture facility can control the environmental conditions and cultivate the aquaculture.

Biofloat technology, which can continuously produce environmentally friendly and clean food, is currently expanding its target species with white prawns, eels, yellow pheasant, mudfish and nidan koi, and it can supply eco- It also contributes to the income increase of the farm household.

As described above, the aquaculture using biofloat technology can increase the yield by densely packed breeding, prevent disease damage, facilitate the management of water quality in breeding water, and have a high feed efficiency, It takes time for microbial settlement suitable for cultured fish species and environment, increases oxygen supply for microorganisms and aquaculture fish, and it is necessary to control titratable acidity of breeding water. Especially, for the oxygen supply, the bubbles are continuously generated in the breeding water. Organic byproducts of bioflak are adsorbed on the surface of the bubbles and accumulate and accumulate along the breeding water.

FIG. 1 is a photograph showing a biofloccullery sludge produced in a biofloat technique. Although bioflavonoids are degraded by microorganisms and reduced to breeding water, if they are not removed at an appropriate concentration level, bioflavonoids will form a thickly packed cake on top of the breeding water, which is disadvantageous in the cultivation process. In other words, the amount of oxygen input is reduced by reducing the surface area of the water in contact with the atmosphere, and it prevents the phytoplankton, the autotrophic bacteria, and the fish from being exposed to the light of appropriate illumination. In addition, the inside of the cake may become a potential source of disease such as an anaerobic environment is formed and decayed. Therefore, bioflavon sludge has been removed and removed in order to manage the aquaculture in the bioflavon farm. In this process, the management cost has increased.

In recent years, the results of analyzing the components of biofloat sludge have been revealed. Bioflakes sludge has been widely used in many fields such as feed waste, photosynthetic bacteria, attached algae, phytoplankton, phytoplankton, zooplankton, copepods, It is said that more than 80% of these bodies are organic matter. It contains 25 ~ 41% of crude protein and 20 ~ 30% of crude fat 2 ~ 3%, especially amino acids such as highly unsaturated fatty acids, carotenoids, phosphorus, methionine, lysine and arginine It has been shown that it contains a large amount of useful ingredients. These beneficiaries are increasing the likelihood that bioflavon sludge will be offered as a feed composition for aquaculture fish or as a feed additive to increase growth and immunity.

Therefore, it has been necessary to conduct studies to appropriately collect and utilize biofloat sludge which has been collected and discarded, because it has been generated in the conventional process and obstructs efficient culture.

Korean Patent No. 10-0400352 discloses a low molecular weight lipid which is obtained from microbial cells of gram negative and has a molecular weight of 5000 占 2000 2000 measured by SDS-PAGE using a protein marker and which does not substantially contain a high molecular weight lipopolysaccharide A feed additive for crustaceans or fishes having an immunosuppression and an infectious disease-preventing effect, which comprises a polysaccharide as an active ingredient, and a feed for crustaceans or fishes characterized by adding the feed additive. In Korean Patent No. 10-0908928, the present invention relates to a pharmaceutical composition comprising Bacillus subtilus KS-3, Bacillus amyloliquefaciens KS-4, Bacillus agaradhaerens KS-5 Paenibacillus lentimorbus KS-6, Bacillus laevolacticus KS-7, Leuconostoc paramesenteroides KS-9, Kurthia sibirica, At least one microorganism selected from the group consisting of KS-13 and Sphingobacterium spirificiborum-GG subgroup B (Flavobacterium) K subunit B (Flavobacterium) KS-18 And a feed additive or feed composition for aquaculture. In Korean Patent No. 10-1420392, a mushroom mixture containing at least two of mushroom extract, mushroom, mushroom and mushroom is added, and then a mixture of mash and skim milk is added to the mixture, followed by addition of a mushroom containing lactic acid fermentation broth Wherein the mushroom fermented milk contains 0.05 to 20 parts by weight of a mushroom mixture containing at least two of mushroom, oyster mushroom and gingko mushroom when the mushroom extract is 0.05 to 20 parts by weight, Wherein the mushroom-containing fermented milk is prepared by fermenting the fermented milk itself or by freeze-drying the fermented milk as an additive to an eel diet. Eel eel feed and feed for energy savings It discloses a claim. Korean Patent No. 10-0860111 discloses a novel microbial strain, Truce Tokatrium SP. (Bacillus polyfermenticus KJS-2), and two new microorganisms and Bacillus licheniformis (Bacillus < RTI ID = 0.0 > licheniformis) Feed additives and feedstuffs. However, these prior inventions differ from the present invention in that the present invention provides a bioflavable feed additive and a production method for the same, characterized in that the bioflavable feedstock is composed mainly of a floating substance in water formed in the breeding water in the bioflag form .

Biofloat aquaculture technology, which has recently become increasingly popular, has been attracting attention because it is capable of breeding densely, facilitating the management of water quality in breeding water, and having high feed efficiency. It is forecast. However, biofloat suspended solids floating in the breeding water during biofrost cultivation process are piled up at the top of the breeding water to make a cake shape that is thickly packed, thereby reducing the surface area of the breeding water contacted with the atmosphere and making the anaerobic environment become a potential source of disease The bioflavonable sludge has been removed by removing the bioflavonable sludge and the maintenance cost has increased in the process. Recently, however, it has been reported that these biofloat agglomerations are composed of useful organic materials such as feed residue, various microorganisms, phytoplankton, zooplankton, copepods, protozoa, etc., and are rich in useful nutrients necessary for aquaculture. It is an object of the present invention to provide a method of recycling a floating solid material as feed additive without throwing it as it is.

In order to solve the above problems, the present invention provides a feed additive comprising a bioflavable organic material, wherein the bioflavable organic material comprises as a main component a suspended solids formed in the water for breeding in biofract form, (B) cultivating the cultured fish in the biofloat breeding water produced in the step (A), collecting the bioflag solid flocculant in the breeding water of the step (B) (C), (D) drying the biofuel solid flocculant collected in step (C), and (E) milling the dried bioflak of step (D) to produce a culture fish feed additive The present invention also provides a method for producing a feed additive comprising bioflavable organic materials.

The present invention can collect the sludge that occurs during the bioflavicultural process and can be used as a feed additive in aquaculture, thereby reducing the cost associated with the disposal of waste generated in a bioflag farm, while reducing the amount of waste Can contribute to the improvement of survival rate, growth rate, immunity and productivity of aquaculture biotech feed additives and contribute to the increase of income of aquaculture farmers.

FIG. 1 is a photograph showing bioflak sludge that appears during mass production of biofloat.
FIG. 2 is a schematic view showing a process for producing a feed additive containing bioflavable organic materials according to the present invention.
FIG. 3 is an exploded perspective view of a bioflavon collecting apparatus used in the production of a feed additive comprising the bioflavable organic material of the present invention. FIG.
FIG. 4 is a graph comparing the compositions of essential and non-essential amino acids of a white fish meal from Chile with a feed additive comprising bioflavable organic materials according to the present invention. The fact that the amino acid composition of the fish meal in Chile and bioflavon sludge is similar suggests that bioflavon sludge can replace fish meal with similar effect.
FIG. 5 is a graph showing growth factors after addition of a feed additive containing bioflavable organic material according to the present invention to a feed according to concentration; FIG. In all treatment groups treated with bioflavant feed additives, survival rates and growth rates were higher than control groups without bioflavant feed additives, suggesting that bioflavonoid feed additives may contribute to the survival and growth rate of aquaculture.
FIG. 6 is a graph showing feed conversion efficiency and feed conversion ratio after feeding a feed additive containing bioflavable organic material according to the present invention to a feed according to concentration; FIG. Compared with the control group, the feed conversion efficiency and feed conversion ratio of the feed supplemented with bioflavant feed additives were improved, indicating that the use of bioflavant feed additives reduces feed costs.
FIG. 7 is a graph showing the total haemocyte count (THC) and phenoloxidase activity (PO) of the aquatic organisms fed the feed additives containing the bioflavable organic material according to the present invention in the feed according to the concentration for 8 weeks. THC and PO are one of the indicators of immunity. The results of this experiment show that the immune enhancement effect was obtained in aquaculture using bioflack feed additive.
FIG. 8 is a graph showing superoxide dismutase (SOD) activity and immunoglobulin (IG) concentration of P. vannamei fed with feed additives containing bioflavable organic materials according to the present invention for 8 weeks . Increased SOD and IG activity in the treated group treated with bioflavant feed additive suggests improved immunity in the treated group.
FIG. 9 is a graph showing the Nitro blue tetrazolium (NBT) reducing ability of P. vannamei supplemented with feed additives containing bioflavable organic materials according to the present invention for 8 weeks after feeding into feeds at various concentrations. It was shown that the NBT reduction potential was increased in the treated group fed with bioflavag diet, indicating that the immunity was improved in the treated group.

The present invention relates to a feed additive comprising a useful organic material generated in the aquaculture process and a production method thereof in a bioflocculation method. Hereinafter, the present invention will be described in detail with reference to specific examples.

FIG. 2 is a schematic view showing a process for producing a bioflavag feed additive according to the present invention. FIG. The bioflavon feed additive of the present invention collects bioflocculant sludge accumulated in the breeding water due to increased concentration of suspended solids in the biofloat breeding tank, and is dried and crushed.

A. Biofrok production and formulation process

A. 1. Breeding for biofroking

Disinfects the water in the breeding tank after receiving the water to prevent deadly viruses and disease bacteria in the aquaculture. Inoculated with phytoplankton culture solution and phytoplankton in the disinfected water, let it flourish for 3-7 days. Phytoplankton used for inoculation can be selected from Raphidocelis subcapitata, Chlorella vulgaris, Spirulina platensis, Spirulina subsalta, Skeletonema costatum, Isochrysis galbana, Chaetoceros gracilis, Dunnaliella tertiolecta, Tetraselmis suecica and Nannochloropsis oculata depending on freshwater or seawater characteristics.

After phytoplankton cultivation, it is a functional microorganism for removal of harmful substances such as ammonia, nitrite and nitrate according to the characteristics of fresh water or seawater. It is a functional microorganism for removing microorganisms, organics, hydrogen sulfide, digestive power and immunity. Nitrosomonas europaea, Nitrosococcus oceani, Nitrobacter winogradskyi , Bowmanella denitrificans , Bacillus subtilis, Oceanobacillus sojae , Rhodobacter capsulata , Rhodobacter sphaeroides, Lactobacillus plantarum , Lactobacillus casei , Saccharomyces cerevisiae and the like can be used for inoculation.

For the ecological food chain formation at the upper echelon according to freshwater or seawater characteristics, calyciflorus , Brachionus plicatilis Etc.), Paramecium caudatum , Daphnia ( Daphnia magna, etc.), aquatic plants ( Hyarella azteca ), abundant shrimp ( Branchinella kugenumaensis ), copepods ( Tigriopus japonicus, etc.), benthic algae ( Haustorioides koreanus , Monocoropium uenoi , grandidierella japonica Etc.), Artemia saline , Etc.), the neighbors awatschensis Etc.) can be used.

A. 2. How to breed aquaculture in biofloat breeding water

This technology artificially implements ecological food chain structure leading to bacterial - phytoplankton - zooplankton - protozoan - protozoan organism in sterilized breeding water, and it is self-purified and ecologically stable structure without pollution without complicated water treatment system. Ecological food chain ecological circulation technology.

In this technology, cultured fish such as P. vannamei are placed at the top of the food chain in an aquaculture water tank that is composed of various functional microorganisms, phytoplankton, zooplankton and protozoa, Allow circulation to circulate within itself. Aquaculture grows and feeds the feed and the livestock in the tank. Contaminants such as ammonia and nitrite, which are generated during feeding and excretion of food, are decomposed by bacteria or converted into other organic materials, and thus are removed and purified in the culture system itself.

As aquaculture grows to feed, more ammonia and nitrite are produced, and pre-formed ammonia and nitrite-removing bacteria are also proliferating, which can remove increasing amounts of ammonia and nitrite. If the ammonia and nitrite removal bacteria are deficient and the ammonia and nitrite concentrations increase, additional bacteria that remove ammonia and nitrous acid are cultured and inoculated. Existing natural transplanting bioprost cultivation methods that wait for functional bacteria to break down pollutants to occur spontaneously. Ammonia concentration over 10mg / L and nitrite concentration 20mg / L for cultivation for longer than 30-45 days It is known that aquaculture can be mass-killed if it is stressed or if it fails to pass this process well.

This technology is an artificial composition technology that separates and cultivates the functional microorganisms with decomposition function, which is different from the conventional natural transition method, so that the ammonia and nitrite concentration is less than 0.1 mg / L within 7 days And the maximum concentration of ammonia and nitrite can be controlled to 1 mg / L or less. This is more than 10 times the concentration value, and the time required to stabilize the water is 3 times longer.

In addition, in the conventional biofloat technology, when water is once broken and ammonia or nitrite rises, it is difficult to return it again. However, the present technology has the advantage of lowering the ammonia and nitrite concentration and returning the water quality to the original state by injecting functional bacteria at any time. In addition to its ability to degrade pollutants, it also provides natural immune enhancement and organic degradation with the help of taurine, which is naturally formed in the natural ecological food chain structure. The results of bioflack composition analysis also show that the beta carotene and taurine components, which are well known as immunosuppressive substances, contain 20 mg / L each.

Phytoplankton acts as a producer in the aquaculture system and purifies the water quality by removing excess nutrients such as nitrate and phosphate in the aquaculture, and provides organic matter in the ecosystem. The zooplankton and protozoa in the upper part of the food chain than the phytoplankton naturally regulate the lower level population by taking bacteria or phytoplankton, and become the food source of the upper echelon. Aquatic organisms directly feed on lower levels of bacteria, phytoplankton, zooplankton, or biofloat, an organic aggregate of these, to regulate the lower biogeochemical biomass and provide nitrogen sources for bacteria and phytoplankton through excretion processes.

In aquaculture ecosystem, the nitrogen source is relatively abundant and the carbon source is always insufficient, so the insufficient carbon source is supplied with molasses, fructose, sludge, etc. to maintain proper carbon / nitrogen ratio. If the pH is lowered due to biological action such as nitrification process, it can be added as sodium bicarbonate or calcium carbonate to increase the bicarbonate ion. Over time, biomass increases in the ecosystem and bioflash sludge increases.

If it is necessary to remove the amount of biofloat sludge, use a sludge removal device to remove it. In general, the sludge concentration can be maintained at an appropriate concentration of 1-10 mg / L depending on the characteristics of the cultured fish species, but the biofloat sludge concentration is increased to several tens mg / Can be increased or bioflak sludge recovery can be increased. The recovered sludge can be used for various purposes such as feed, feedstuff, feed additive, water quality improvement agent, low quality improvement agent, and fertilizer.

A. 3. Bioflag collection

Biofrock breeding tanks vary in size from a few tons to tens of tons to hundreds of tons for mass production. Particularly, in order to improve energy efficiency and productivity, a large biofloat tank having a size of several hundred tons is advantageous as shown in Fig. However, such large-scale breeding tanks are not easy to collect biofloat because they are widely exposed to air, and biofloat sludge deposited on rearing water is widely distributed. Therefore, it is convenient to collect biofloat using a biofloack collector connected to large-scale biofloat breeding tanks in order to increase the efficiency of collection of bioflag sludge without entering the tank.

FIG. 3 is an exploded perspective view of a bioflavack collecting apparatus used in the production of the bioproduct feed additive of the present invention. FIG. In one embodiment of the present invention, a bioflag collection tank capable of interlocking with a 300-ton long oval biofloat breeding tank was manufactured.

When the amount of Suspended Solid (SS) in the 300 - ton biofloat breeding tank was measured, it was introduced into the bioflag collection tank. The breeding water of the large breeding tank moves into the collection tank 100 through the breeding water injection pipe 100 and collects the bioflakes contained in the breeding water in the collection tank together with the bubbles generated in the bubble generator near the tank bottom. It reaches the upper part of the water tank and forms sludge on the breeding water surface and is concentrated. Concentration was carried out for 12 hours, and Bioflakes sludge concentrated in cake form on the breeding surface was collected on collection plate. In this process, since a large amount of the breeding water is removed through the through holes formed in the collecting plate, it is efficient in the process such as drying of bioflag thereafter.

The breeding water introduced from the breeding tank through the breeding water inlet pipe 120 is returned to the bioflak breeding tank through the breeding water collection pipe 130 after the bioflare sludge is sufficiently removed and is continuously used for breeding aquaculture . Since biofloat breeding tank and bioflag sludge collecting device are interlocked, biofloack breeding tanks are continuously supplied with slaughtered feed, and bioflag can be conveniently collected.

A. 4. Biofloat drying and grinding

FIG. 2 is a schematic view showing a process for producing a feed additive containing bioflavable organic materials according to the present invention. The biofloat collected through the biofloat collector was dried for 4 to 24 hours with a moisture content of 13% or less by using a drying device such as a hot air dryer, a microwave vacuum dryer or a freeze dryer, This was pulverized to prepare a bioflav powder sample.

B. Analysis of bioflavonoid components

B. 1. Biofloat General ingredient content

Nutritional and functional materials were analyzed using bioflavable powder samples obtained through bioflag production and pulverization process. First, general components were analyzed to evaluate the nutritional value of bioflak powder.

 The biofloat collected through biofloat collector was lyophilized and pulverized to produce a bioflag powder sample. Table 1 shows the general component content of Bioflak powder. As shown in Table 1, it was confirmed that the general component of bioflak had an inorganic content of about 43.5% and a protein of 30.3%.

General ingredient content of bioflavonoid powder Biofloc powder % Protein (DM) 30.3 ± 2.1 Lipid (DM) 0.3 ± 0.1 Ash (DM) 43.5 ± 0.5 Moisture 4.9 ± 0.2 Fiber (DM) 6.6 ± 0.3

Values are mean of triplicate groups and presented as mean ± SD.

B. 2. Bioflavonic amino acid composition

The composition of the constituent amino acids of bioflak powder was analyzed by dividing it into essential and nonessential amino acids. Table 2 shows the composition of essential and non-essential amino acids of bioflavonoid powder.

As shown in Table 2, the essential and non-essential amino acid composition of bioflak was excellent. Especially, Methionine lysine and arginine, which are important essential amino acids in aquaculture, are excellent, and bioflavon which has been abolished in the process of bioflavonification can improve nutrition of cultured fish. It was confirmed that it was sufficient value as a feed additive.

FIG. 4 is a graph comparing the compositions of essential and non-essential amino acids of a white fish meal from Chile with a feed additive comprising bioflavable organic materials according to the present invention. As shown in FIG. 4, it was confirmed that the bioflavag powder according to the present invention contained essential and non-essential amino acids in a very good ratio as compared with the amino acid composition of the fish meal from Chile, and the possibility of bioflavag powder as a feed additive Respectively.

Amino acid composition of bioflavonoid powder Amino acid composition % of sample % of protein Essential AAs MET 0.36 1.51 ARG 1.17 4.92 PHE 1.16 4.88 LEU 1.81 7.60 ILE 1.02 4.29 LYS 1.11 4.67 VAL 1.51 6.42 THR 1.31 5.50 HIS 0.41 1.72 Non-essential AAs ASP 2.66 11.19 SER 1.14 4.81 GLU 3.40 14.34 GLY 1.60 6.74 ALA 1.84 7.75 PRO 0.77 3.19 CYS 0.23 0.95 TYR 0.73 3.08

B. 3. Analysis of functional materials in bioflakes

Previously known immunological active substances in fish feed were investigated through literature to analyze the content of functional materials contained in Bioflak powder. Table 3 shows total nucleotides, total pigment, beta-carotene, and taurine contents in Bioflack powder. As shown in Table 3, it was confirmed that Bioflack contained a large amount of immunologically active substances such as nucleotides, pigments, beta-carotene, and taurine, which are well known as functional substances in fish feed.

Functional content of bioflavons Functional material content Total nucleotides (%) 3.79 Total pigment (mg / kg) 660 Beta-carotene (mg / kg) 20 Taurine (mg / kg) 20

C. Bioflack  Identification of function as feed additive

C. 1. Preparation and experimental method of experimental feed

C. 1. 1. Production of experimental feed

To investigate the feasibility of bioflavag as a feed additive, bioflavag powder was added at 0, 0.5, 1.0, 2.0, 4.0, 6.0, and 8.0%, respectively.

The experimental diets were prepared by mixing the feed materials in a mixer, mixing them, adding fish oil, and adding distilled water equivalent to 20% of the total weight of the feed materials. Mixed dough was extracted to a suitable size using a small-sized digging machine (SMC-12, Kuposlice, Busan, Korea). The experimental diets were dried for 24 hours in a drier and stored at -20 ° C until feeding.

Experimental feed composition table (% dry matter) Ingredient Diets Con BF 0.5% BF 1.0% BF 2.0% BF 4.0% BF 6.0% BF 8.0% Brown fishmeal 28.0 28.0 28.0 28.0 28.0 28.0 28.0 Soy bean meal 30.0 30.0 30.0 29.5 28.5 27.5 26.5 Squid liver meal 3.00 3.00 3.00 3.00 3.00 3.00 3.00 Wheat flour 29.0 28.5 28.0 27.5 26.5 25.5 24.5 Starch 5.00 5.00 5.00 5.00 5.00 5.00 5.00 Squid liver oil 1.00 1.00 1.00 1.00 1.00 1.00 1.00 Mineral mix 1.00 1.00 1.00 1.00 1.00 1.00 1.00 Vitamin mix 1.00 1.00 1.00 1.00 1.00 1.00 1.00 Choline chloride 1.00 1.00 1.00 1.00 1.00 1.00 1.00 Licithin 1.00 1.00 1.00 1.00 1.00 1.00 1.00 Biofloc. 0.00 0.50 1.00 2.00 4.00 6.00 8.00 Chemical Composition ( % dry matte r) Dry matter 93.2 93.8 94.0 93.2 93.1 93.6 93.5 Protein 40.8 40.9 40.7 41.6 41.0 41.0 41.0 Lipid 6.70 7.50 7.10 7.00 7.60 7.30 7.50 Ash 8.00 8.40 8.30 8.60 9.30 10.0 10.8 Energy, MJ / kg diet 16.6 16.6 16.6 16.5 16.4 16.2 16.1

C. 1. 2. Experimental Method

The P. vannamei shrimp used in the experiments were fed for two weeks to commercial commercial feeds and adapted to the experimental environment. After preliminary breeding, the shrimp (initial mean weight: 1.01 ± 0.01 g) were randomly selected and placed in 21 75L water tanks, 18 each.

Air stones were installed in all experimental tanks to maintain dissolved oxygen, and the temperature of the reared water was maintained in the range of 26-29 ℃ during the whole experimental period. The feeding was divided into four times (08:00, 12:00, 16:00, 18:00) for 8 weeks (8 ~ 10% of total body weight).

After 8 weeks of feeding experiment, the final weight and feeding rate of shrimp were measured and the weight gain, specific growth rate, feed conversion ratio, protein efficiency ratio, Feed intake and survival rate were calculated. After final weighing, 5 shrimp were randomly selected for each shrimp and anesthetized in ice water. Blood was collected using a 1 mL syringe containing 200 μl of an anti-coagulant (Alsever's solution, Sigma). The collected blood was first used for total haemocyte count and respiratory burst analysis, and the remaining blood samples were centrifuged at 700 ° C for 20 minutes at 4 ° C and stored at -70 ° C for immunological analysis.

C. 2. Growth factors of P. vannamei fed with bioflavag powder

C. 2. 1. Identification of growth rate, daily growth rate, protein conversion efficiency, and survival rate

To investigate the effect of bioflavonoid powder on the growth of P. vannamei, bioflavag powder was added to the experimental diets so as to be 0% (control), 0.5%, 1.0%, 2.0%, 4.0%, 6.0% and 8.0% (WG), specific growth ratio (SGR), protein efficiency ratio (PER), and survival rate of the P. vannamei shrimp during 8 weeks of culture. Respectively.

WG (%) = 100 x (final weight - initial weight) / initial weight

SGR (%) = [(log e final weight - log e initial weight) / days of rearing] × 100

PER = wet weight gain / protein feed

FIG. 5 is a graph showing growth factors after addition of a feed additive containing bioflavable organic material according to the present invention to a feed according to concentration; FIG. Protein efficiency ratio (PER), weight gain (WG), specific growth ratio (SGR) and bioflavon (4.0%) were significantly higher than control. The survival rate was 98.1%, which was significantly higher than that of the control group. Growth rate, daily growth rate, protein conversion efficiency, and survival rate were higher in Bioflag powder than in the control.

C. 2. 2. Identification of feed conversion efficiency and feed conversion rate

FIG. 6 is a graph showing the feed conversion ratio (FCR) and feed intake (FI) after the feed additive including the bioflavable organic material according to the present invention is added to the feed according to the concentration.

FCR = feed rate / weight gain

FI = feed intake / shrimp

Feed conversion efficiency, which means the amount of feed to the weight gain, shows that the lower the value, the better the efficiency. In the 8 - week experiment, 4.0% bioflavonoid powder showed significantly higher feed efficiency than non - additive, similar to growth factors. Other experimental groups with bioflavon powder did not show any significant difference, but showed higher feed efficiency than non - additive group. Especially, the feed conversion efficiency increased by 0.41 compared to the control. However, except for 8.0% bioflavonoid powder, the treatments showed a relatively good overall yield.

C. 3. Nonspecific immunological analysis of P. vannamei fed with bioflavag powder

C. 3.1. Total Haemocyte Count ( THC ), Phenoloxidase activity ( PO ) analysis

Total haemocyte counts were determined by dilution of 9: 1 ratio of distilled water and blood samples, and then 10 μl of a blood sample diluted in a haemocytometer was injected and measured using an optical microscope (Leica DMIL, Leica Microsystems GmbH, Wetzlar, Germany).

Phenoloxidase activity was analyzed by the method of Hernandez-Lopez et al (1996). First, each blood sample is dispensed into a 96-well plate at 50 ° C and incubated at 25 ° C for 30 minutes at 50 ° C with trypsin (3 mg ml ^-1 in CAC buffer). Then add 50 μl of L-dihydroxyphenylalanine (L-DOPA, Sigma). 10 mMJ sodium cacodylate and 10 mM CaCl ₂ are prepared by using CAC buffer and mixed to pH 7.0. After incubation in a 25 ° C incubator for 10 min, measurements were taken at 490 nm in a microplate reader (UVM 340, Biochrom, Cambridge, UK).

FIG. 7 is a graph showing the total haemocyte count (THC) and phenoloxidase activity (PO) of P. vannamei fed with feed additives containing bioflavable organic material according to the present invention for 8 weeks . Total haemocyte count (THC (× 10 ³ cells / ml)) and phenoloxidase activity (PO) were higher in the bioflavant feed additive treatments than the control, although no statistically significant difference was found.

C. 3. 2. Superoxide dismutase (SOD), Immunoglobulin (IG) analysis

Superoxide dismutase (SOD) activity was analyzed using the superoxide dismutase assay kit (Sigma, 19160). Add 20 μl of radical detector to 96-well plates and add 10 μl of blood sample. After incubation for 20 minutes with 20 μl xanthine oxidase, the absorbance was measured at 450 nm using a microplate reader (Themo, USA).

Total immunoglobulin (Ig) was analyzed based on the analysis method of Siwicki and Anderson (1993). After immunoglobulin molecules were precipitated using 12% polyethylene glycol (Sigma) solution, plasma proteins were measured using microprotein assay (Sigma C-690).

FIG. 8 is a graph showing superoxide dismutase (SOD) activity and immunoglobulin (IG) concentration of P. vannamei fed with feed additives containing bioflavable organic materials according to the present invention for 8 weeks . In the SOD analysis, no significant difference was found in all experimental groups. However, the addition of Bioflack powder tended to show a higher value than that of the non-additive group, and the SOD activity was the highest in the 4.0% added group.

The results of IG analysis showed no significant differences in all experimental groups, but bioflavonoid powder addition groups showed higher tendency than non - supplemented groups.

C. 3. 3. Nitro blue tetrazolium (NBT) reduction analysis

The respiratory burst of blood samples is a method of quantifying formazan reduction of NBT (Nitroblue Tetrazolium). First, 200 μl of mHBSS solution (Sigma) is placed in a 2-mL Eppendorf tube, and 50 μl of the blood sample is transferred to an Eppendorf tube and reacted at 25 ° C for 30 minutes. Next, 100 μl of Zymosan (0.1% in Hank's solution) (Sigma) was added and reacted at 37 ° C for 2 hours. Then, 100 μl of NBT solution (0.3%) (Sigma) was added and reacted at 37 ° C for 2 hours. Next, add 600 μl of 100% methanol, centrifuge at 6500 rpm for 10 minutes, discard the supernatant, wash with 100 μl of 70% methanol for 3 times, and then dry for 5 minutes. Finally, Formazan was dissolved in 700 μl of 2M KOH and 800 μl DMSO (Sigma) and then measured at 620 nm in a microplate reader (UVM 340, Biochrom, Cambridge, UK).

FIG. 9 is a graph showing the Nitro blue tetrazolium (NBT) reducing ability of P. vannamei supplemented with feed additives containing bioflavable organic materials according to the present invention for 8 weeks after feeding into feeds at various concentrations.

As a result of NBT analysis, the addition of 0.5% and 4.0% of bioflavag powder was significantly higher than that of the control, and NBT reduction activity was higher in all experimental groups with addition of bioflavant feed additive.

As a result of the above analysis, the bioflavonoid solid component that has been produced in the biofloat culture process and discarded after collection has been completed as a feed additive which is excellent in nutrition and nutritional and immunity enhancement of cultured fish.

The present invention can collect sludge that occurs during the bioflavicultural process, and can be used as a feed additive in aquaculture, thereby reducing the cost of disposing waste generated in bioflavicultural farms, Which can contribute to the increase of income of aquaculture farmers, it is possible to be used industrially.

100: Collection tank 120: Breeding water injection tube
130: Breeding water collection pipe 150: Water pipe
160: air supply
200: collecting plate 250: handle

Claims (5)

Freshwater or seawater is stored in the breeding tanks and disinfected. Phytoplankton cultures and phytoplankton are inoculated into the disinfected water for 3 to 7 days. After phytoplankton cultivation, the microorganisms are inoculated with fresh water or seawater. ,
Wherein the phytoplankton is selected from the group consisting of Raphidocelis subcapitata, Chlorella vulgaris, Spirulina platensis, Spirulina subsalsa, Skeletonema costatum, Isochrysis galbana, Chaetoceros gracilis, Dunnaliella tertiolecta, Tetraselmis suecica ,
Wherein the functional microorganism is selected from the group consisting of Nitrosomonas europaea, Nitrosococcus oceani, Nitrobacter winogradskyi, Bowmanella denitrificans, Oceanobacillus sojae, Rhodobacter capsulata, Rhodobacter sphaeroides, Lactobacillus plantarum, Lactobacillus casei, Saccharomyces cerevisiae , (A) producing a number;
(B) culturing and culturing the cultured fish in the bioflocculation water produced in the step (A); And (C) collecting the bioflavonoid fluid from the breeding water in step (B), drying and pulverizing the bioflavonoid fluid in step (B).
A feed additive comprising a bioflavable organic material according to claim 1, which is produced by a method for preparing a feed additive using the biofluck useful organic material delete delete delete

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