专利摘要:
The present invention relates to a method of producing biomass for use as a substrate for the production of biogas or fertilizer. The method used is to grow aquatic organisms, where the lake Ciona íntestínalis, is described as a model organism which is to be grown and harvested with industrial and accepted cultivation techniques. Furthermore, the invention comprises a method of growing macroalgae together with the sea urchins when a large part of the nutrition that the animals do not use is released again as easily accessible nutrient for the macroalgae, which promotes their growth.
公开号:SE0901154A1
申请号:SE0901154
申请日:2009-09-04
公开日:2011-03-05
发明作者:Fredrik Noren
申请人:Fredrik Noren;
IPC主号:
专利说明:

its explanation should not be construed as a limitation of the present invention. The scope of the present invention is defined by the appended claims. 1. MARIN ßlomAssA - SEA POINTS Sea urchins, Ascid / 'acea, are a class of shellfish with about 2300 species in the world, of which about 50 on the Swedish west coast. They are attached, solitary or colony-forming filters. The body is sac-like and completely surrounded by the mantle. An example is the sea urchin Ciona intestinalis L. which can occur in very high numbers and has been reported in densities of over 5000 individuals per m2. The weight of biomass has been measured in Norwegian waters to 7 kg TS / mz and in Canadian waters to 200 kg wet weight / mz. If a dry matter content of 4% is used, this value corresponds to 8 kg TS / mz. They live by filtering plankton out of the water and have a very fast growth compared to many other animals. They can have a daily length growth of 2 ~ 3% and a doubling time in weight of 10 days. Ciona íntestina / ice multiplies in boreal waters twice a year and in warmer waters three times, possibly four. The growth rate of Ciona intestina / ice has also been measured in the sea by applicants and was found to be 8.5 cm (n = 350, sd. = 3.2 cm) in 93 days and a growth in biomass, measured as wet weight per m2, of 33 kg during the same time (location: Lysekil, Sweden, time May 2009 to August 2009, depth 1-2 meters on vertical concrete foundation, approximate salinity 20-34 psu, approximate temperature 10 »2o °).
Other solutions aimed at extracting biomass from the sea have only discussed macroalgae, obtained by cultivation or harvesting, as well as macroalgae which have been washed ashore on the beaches. Digestion of microalgae taken from the algal blooms in the Baltic Sea has also been put forward as an idea, as has the digestion of mussels which are grown in the Baltic Sea. An idea to grow micro- or macroalgae in nutrient-rich wastewater from treatment plants has also been presented. Among the filed patent applications are several applications which claim the right to use biomass based on micro- or macroalgae and their extracts (US2008 / 0050800, CN101414316, US2009081744, EP2014759, CN101285075, CN10125S075, UA24101, DE102008, DE102007, WO102007 ). The genus Ciona has the following species Cíona edwardsí, Cíonafascícularís, Cíona gelatínosa, C íona írnperffècta, C iona intestínalis, Cíona mollis and (Iiona savignyi which are all suitable for use in the same way as Ciona intestinalís. MUSHROOMS In addition to cultivating the species we have chosen as an example, Ciona intestinalis, which is suitable for cultivation in Swedish waters, other species of the genus Ciona, other sea urchins, can also be cultivated where the conditions so require or if Cionu intestinu / ice does not occur naturally. See Table 1 for a phylogenetic overview of the sea urchin class (Ascidiacea Nielsen 1995). Family Agnesiidae ll Family Ascidiidae ll Famiiy @ ggg ll Family pja fl gu fi | Family Hygobythiidae ll l Family Pe roghoridae ll l Genus Didemnum l_L _____ L__t __; ______; llllll Family coreiiidae lllll Order Pleurogona Suborder Stolidobranchia Family Pyuridae Family Styelidae Genus Eusynstyela Genus Size / a Family Botyllidae Genus Botryl / oides Genus Botry // us Other fast-growing species of both coral animals and fungi can be grown in the sea, or in lakes, mentioned above, for the purpose of producing biomass for digestion or bioethanol production. Some of these animals may be suitable for breeding at greater depths further out at sea. To broaden the example of possible organisms, we point to the high prevalence and productivity of animals around so-called "thermal vents" (hot underwater volcanoes) where many life forms use chemotrophic bacteria as primary producers. We have chosen to describe sea urchins in the continuation of the text, but that this also includes fungal animals and coral animals which have also never been grown industrially to produce biomass. 2. EFFECT soivi ROTATION SUBSTRATE The background to the invention that seaweeds can be used as biomass in digestion processes lies in the fact that Swedish biogas industries use waste materials from the fish processing industry, in the form of pickled brine and fish residues, and thus can increase their production of biogas, both in quantity produced gas per year and gas production of biogas with a higher content of methane. . Waste from the fish processing industry is considered a very good biomass complement in digestion with sewage sludge, a possible explanation for this is that such waste is very rich in nitrogen, which benefits the general digestion process if other biomass has a higher carbon content. In the digestion process, the ratio between carbon and nitrogen (molar ratio) should generally be between 30: 1 and: 1 (CN). Sea urchins have a carbon-nitrogen ratio of 4: 1, which is too low for optimal digestion with only sea urchins as biomass. However, it is very appropriate to co-feed with more carbon-rich biomasses. The waste from the fish processing industry has a carbon-nitrogen ratio of 5: 1, which is an argument that the low carbon-nitrogen ratio in sea urchins is not a problem in industrial digestion processes. There are also indications that salt in small amounts stimulates biogas production.
The salinity of biomass from freshly harvested sea urchins is more or less the same as the surrounding water. This is largely due to the fact that when they are harvested, the sea urchins close their inflow and outflow openings and close in a quantity of water. In sea urchins from the water outside Lysekil, Sweden, which we have used in digestion experiments, the salinity has been between 20 and 30% »but can in these water areas vary between 10 and 35% @. The waste from the fish processing industry has a salinity of 60-70% ° and this salinity has not been shown to have a negative impact on the digestion process, provided that the digestion reactor can adapt to the amount of salt biomass. It is known that a digestion process can handle moderate salinities. In general, the bacterial community can handle a large range of biomass types as long as they have time to adapt. Methane-producing bacteria come evolutionarily from the sea but occur both in animal stomachs, in land soils and in marine and brackish aquatic environments.
The applicant has carried out its own digestion tests where the biogas production after 10 days was 600ml CHÅ / gr TS per day with biomass from sea urchins mixed with 30% (weight TS) carbon-rich biomass.
After harvesting, the cultivated biomass can, in addition to being used as a substrate for biogas production, also be used as fertilizer, both as fresh biomass or as dewatered and desalinated. Desalinated and dried biomass can be used as fertilizer in agricultural, horticultural or hobby cultivation. The background to this is that macroalgae have historically been used as a nitrogen-rich fertilizer in the fields on the Swedish west coast. The macroalgae were sprinkled over the plantations after rainwater had naturally desalinated the macroalgae. Then sea urchins, coral animals or fungi can also be used as fertilizer as they are rich in both nitrogen and phosphorus nutrients as well as trace elements. 3. OouNG Av oRGArusMER | WATER In general for systems to grow entrained organisms in water, whether in the sea or lakes, it consists of some form of surface that is immersed in the water where the organisms are either captured as larvae from the surrounding water or that care is also taken to larvae or spores get stuck on these surfaces already on land in water tanks by manipulating the parent generation. When harvesting, the surfaces, in the form of ropes, ropes, piles, nets, etc., are generally taken out of the water so that the organisms can be harvested over to a boat or to land. There is also cultivation of organisms on natural bottoms, which of course is also an opportunity for biomass production. Growing sea urchins, coral animals or fungi does not really require more than such a general cultivation method where the surface that is lowered must be of a suitable nature and enable the animals can attach, grow and not loosen. The time when the surfaces are immersed in the water is important with regard to the water's temperature, salinity or other physical parameters to ensure that the animals grow well. The time when the surfaces are lowered is also important to ensure that free-swimming larvae are present in the water depending on their life cycle. Below are a number of examples of cultivation methods that can be used to cultivate sea urchins but which also function as suitable methods for cultivating coral and fungal animals. Many of these methods are described in the literature for mussel and algae cultivation.
The Long-Lines method is the method most used in the cultivation of mussels in Sweden and which we see as the, in Swedish waters, currently the most suitable method. This is because the method is used industrially for cultivation and harvesting of about 3000 tons of mussels annually and the method is therefore reliable. All equipment is available for purchase and a harvesting boat is available for rent together with an experienced harvesting crew. The long-lines method consists of 5 cm polyprolyte bands which are immersed in the water for a long unbroken distance. In a Swedish long-line cultivation with a size of 20 * 100 meters, the total length of cultivation strip amounts to about 24km. The straps are fastened at regular intervals in carrying ropes which are kept afloat by means of floats. At the ends, the carrying ropes are anchored to keep the cultivation extended. The method is also called "one-dragon method" in China. By having the cultivation belts hanging above the bottom, you effectively avoid that bottom-dwelling animals can get up on the belts and eat what you grow, for cultivation of Ciona intestinalis it is important to avoid e.g. .
Asterias rubens grazing on the species. Other methods that can be used to efficiently grow and harvest marine biomass can be mentioned (here their English term is used: Rack culture, hanging method, bitin culture, tulus culture, stake culture, tray culture, wigwam culture, rope-web culture, bouchout culture, raft culture, long-line culture 4. SAmootimc-s A specific procedure of the method of growing sea urchins in the sea with the aim of producing biomass for digestion is to co-cultivate the sea urchins with macroalgae.Different techniques for growing macroalgae are well known and described It is also known that macroalgae have a higher growth rate as the water contains higher levels of nutrients, mainly nitrogen and phosphorus compounds.It is also known that animals excrete nutrients as a by-product of metabolism in the form of eg urine, urea or substances with similar function to remove the organism's residual metabolites.These substances are rich in readily available nitrogenous substances, compare, for example, agricultural use of fertilizers.
With this background knowledge, we see that there is an improving effect in co-cultivating the sea urchins, or the organisms you choose to grow for the production of biomass for digestion, with macroalgae. The sea urchins simply secrete nutrients that make the macroalgae grow faster, which industrial producers strive for. From an environmental perspective, this also improves the entire cultivation's ability to absorb nutrients from the water, which is good when you want to sell emission rights for the de facto amount of nitrogen and phosphorus you take from the sea.
In practice, co-cultivation takes place in different ways: 1. That sea urchins and macroalgae are grown on different ropes / bands within the same cultivation unit. The advantage of this method is that the macroalgae come close to the release of nutrients from the sea urchins and that the sea urchins do not compete as strongly for available plankton food from the sea 2. That sea urchins and macroalgae are grown separately with adjacent cultivation units. The maximum distance between the cultivation units is determined by their size and biomass as well as the water area's currents and hydrography so that the macroalgae can assimilate the nutrients that the sea urchins release. . LIVEDIED SETTLING Ciona intestinalis multiplies at temperatures between 8 ° and 23 ° and releases larvae into Swedish and Norwegian waters between May and September with the highest larval production in June.
The method with mediated settling is used today for the cultivation of macroalgae, among other things for Porphyra species, which include the popular Japanese Nori algae for sushi cooking. Mediated settling means that through a certain technical procedure, such as manipulation of the amount and quality of the cultivation light and its temperature, the life cycle of the macroalgae can be regulated to produce propagating bodies (spores). For a person knowledgeable in the field, it is possible to practice the method.
However, no one has used it to get a secured settlement on cultivation areas in the sea for sea urchins. You have the knowledge of the water conditions required for sea urchins to release their eggs and sperm into the laboratory. This knowledge has been used there to constantly be able to produce new individuals of sea urchins for research purposes. But since no one has thought of cultivating sea urchins on a large scale at sea, no one has thought of improving that cultivation technique with mediated settling.
The process takes place by storing sexually mature individuals of sea urchins in water vessels where the water temperature is kept below 8 ° C, which is the temperature at which sea urchins become sexually mature if the temperature is exceeded. In these vessels, the cultivation bands, cultivation ropes or other cultivation surfaces on which the sea urchins are intended to settle as a new generation of larvae are laid down. Thereafter, the temperature in the water vessel rises above 8 ° C and the sexually mature individuals of the sea urchins release their eggs and sperm after a certain time, which combine into larvae. The larvae will then attach to the submerged culture bands, culture ropes or other culture surfaces.
The sea urchins can be stored in the same vessel cultivation belts or stored in an adjacent vessel with a communicating water connection.
After larvae have settled on the submerged belts, they are allowed to grow for a suitably limited time so that they have grown sufficiently to withstand being placed in a new aquatic environment where they are intended to be grown to a suitable size before harvest.
DEHNmoNER TS: Abbreviation for dry matter which is the anhydrous weight of organisms after drying (^ '80 °, 1 day).
Wet weight: Weight of the biomass in a wet state, which is weighed within 1 hour from harvest where the biomass is stored for at least half that time in a colander.
Marine / marine environment: Defined as the aquatic environment that is not clean seawater or consists of fresh water. That is, any aquatic environment that contains a salinity exceeding 0.5% a NaCl.
Sea: Same definition as marine environment.
Organism: Defined as all living organisms by the groups Eukaryota, Arkea and Prokaryota.
Animals: A group of organisms belonging to the group Animalia Sea urchin / sea urchins: Animals belonging to the group Ascidia Mediated settling: A human-controlled production of eggs and sperm in organisms whose zygotes (the fertilized egg) develop into larvae which settle on hard surfaces in water before they grow into adult animals.
Water: All environment that consists of H20 which includes both marine environment and lakes, both environments include both natural environments as well as artificial environments, e.g. dams and other water facilities.
Plankton: All organisms that live floating in the water is the scientifically correct definition that we also use here. Plankton can also be divided into, and covered by, zooplankton, phytoplankton and bacterial plankton depending on which organisms are referred to.
Settla: is a pre-Swedishization of the English term sett / e which translates to Swedish b / ifast, to sit down. The term sett / a (infinitive - att sett / a) is used by Swedish marine biologists.
Ascidia: The organism group is called sea urchins in Swedish. Ascidia is synonymous with Ascidiacea and is Defined according to Tree-of-life and the references therein.
Antozoa: The organism group is called corals in Swedish. Defined according to Tree-of-life and the references therein.
Porifera: The organism group is called fungal animals in Swedish. Defined according to Tree-of-life and the references therein.
Macroalgae: Visible algae. A collective term for the organism groups red algae (rhodophyta), green algae (chlorophyta) and brown algae (phaeophyta).
Microalgae: Unicellular organisms which are not visible to the naked eye which live floating in the sea .. Is not related to the macroalgae but belongs to many different groups of organisms such as dinoflagellates, diatoms, etc.
权利要求:
Claims (1)
[1]
A patent which is characterized by the cultivation of aquatic organisms, which belong to the group of animals ascidia, which are used after harvest as a substrate for biogas production. The method according to claim 1, characterized in that the animal group ascidia is used as a substrate to produce a manure. Process according to claims 1 and 2, characterized in that the animal group ascidia is used as a substrate to produce a number of emission rights for nitrogen, phosphorus and carbon dioxide. The method according to claims 1-3, which are characterized in that the organisms are a number of filtering animals which belong to the groups anthozoa or porifera. The method according to claims 1-4 which are characterized in that the cultivation takes place by utilizing a number of surfaces which are immersed in water, on which said surfaces the organisms are to be grown and to grow on before they are taken up for harvest. Method according to claim 5, characterized in that the cultivation takes place by the following named methods; rack culture, hanging method, bitin culture, tulus culture, stake culture, tray culture, wig-wam culture, rope-web culture, bouchout culture, raft culture and long-line culture. A process which is characterized in that aquatic organisms, which belong to the animal group ascidia, are grown together with macroalgae which belong to the groups rhodophyta, chlorophyta or phaeophyta so that the macroalgae thus have a higher growth rate through the water-soluble nutrients that the ascidies release from their metabolism. Process according to Claim 7, characterized in that the macroalgae are used as a substrate for biogas production. Process according to Claim 7, characterized in that the macroalgae are used as a substrate for producing manure. A method according to claim 7, characterized in that the macroalgae are used as a substrate to produce a number of emission rights for nitrogen, phosphorus and carbon dioxide. A method for attaching larval stage ascidies to a number of culture lines which is characterized by storing said culture lines immersed in water vessels together with sexually mature individuals of ascidia which are caused to release their sexual products by regulating the water temperature in the vessel in such a way that the release of larvae starts and that the formed larvae then settle on the submerged surfaces in the form of ropes, bands or ropes, to then placed on the cultivation site.
类似技术:
公开号 | 公开日 | 专利标题
Yang et al.2006|Growth of Gracilaria lemaneiformis under different cultivation conditions and its effects on nutrient removal in Chinese coastal waters
CN103340165B|2015-05-20|Mandarin fish pond ecological high and stable yield method
KR20170129129A|2017-11-24|Method of land form of oysters
CN103238542B|2014-09-17|Bottom sowing culture method of giant clams
Sahoo et al.2005|Mariculture of seaweeds
CN104642221A|2015-05-27|Penaeus japonicus pond culture technology
Wu et al.2017|Nutrient removal ability of seaweeds on Pyropia yezoensis aquaculture rafts in China’s radial sandbanks
CN103314903B|2015-09-09|The breeding method of Tarim Basin schizothoracin yearlings
CN104823898A|2015-08-12|Sillago sihama fry mouth opening bait culturing, selecting and feeding method
Gibbs et al.2005|Benthic nutrient fluxes along an estuarinegradient: Influence of the pinnid bivalve Atrina zelandica in summer
JP2011244795A|2011-12-08|Method for producing on land of sand-submerged bivalves, such as littleneck clam
CN105191845A|2015-12-30|Three-dimensional ecological mixed culture method for sea cucumbers and sea horses
SE0901154A1|2011-03-05|Production system for the production of biomass for gas production
WO2018124963A1|2018-07-05|Device and system for trophic cultivation of organisms in water
Yu et al.2013|Pond culture of seaweed Sargassum hemiphyllum in southern China
CN105532518A|2016-05-04|LutrariasieboldiiReeve sea area beach plastic large tub artificial culture method
Hendri et al.2017|Optimization of cultivated seaweed land gracilaria sp using vertikultur system
Cheshire et al.2019|Understanding the macroalgal value chain: from production to post-harvest processing
CN103828744B|2015-05-20|Method suitable for ecology breeding of Hong Kong oyster juvenile mollusks of coastal region of south China
KAWAI et al.2015|Harvest and cultivation of Saccharina japonica in Northern Hokkaido, Japan, and southern Sakhalin and Primorye, Russia: A review
CN100377640C|2008-04-02|Method of improving ecological environment of enclosed seawater pond
Loka2015|Importance of water quality in mariculture
Dampin et al.2016|EFFECTS OF ECOLOGICAL IMBALANCE IN FIVE-CONSECUTIVE OXIDATION PONDS ON COMMUNITY WASTEWATER TREATMENT EFFICIENCY TOWARDS WEALTHY AND HEALTHY NILE TILAPIA PRODUCTS
Goldman et al.1977|Topical report on sources and systems for aquatic plant biomass as an energy resource
Abdullah et al.2020|Seaweed Kappaphycus alvarezii cultivation using longline method in Kastela waters, Ternate Island, Indonesia
同族专利:
公开号 | 公开日
CN102597249A|2012-07-18|
EP2473611B1|2016-12-07|
CN102597249B|2014-07-16|
ES2620229T3|2017-06-28|
WO2011028163A1|2011-03-10|
EP2473611A4|2015-05-13|
HRP20170369T1|2017-05-05|
DK2473611T3|2017-03-13|
SE535011C2|2012-03-13|
PT2473611T|2017-03-13|
EP2473611A1|2012-07-11|
引用文献:
公开号 | 申请日 | 公开日 | 申请人 | 专利标题

US4975106A|1985-12-16|1990-12-04|Biotherm International, Inc.|Anaerobic digestion of fish wastes|
JPH0247282A|1988-08-08|1990-02-16|Takao Miyanoo|Method for preventing leaching of iron ion|
JPH0857462A|1994-08-23|1996-03-05|Kankyo Project Kk|Method and apparatus for separating and treating shell meat and sheet of organic solid such as shellfish or the like|
DK1076486T3|1998-05-05|2006-01-09|Pharma Mar Sa|Cultivation of sessile marine animals|
JP3973294B2|1998-07-17|2007-09-12|鹿島建設株式会社|Shell Methane Fermentation Processing Equipment|
CN1431188A|2003-01-09|2003-07-23|王长海|Method for preparing sea squirt fatty acids and methyl ester, ethyl ester, triglyceride and its preparing method as well as application infunctional food and drugs|
CN100335495C|2006-01-23|2007-09-05|南方医科大学|Acidian polypeptide and preparation method thereof|
JP2008049273A|2006-08-25|2008-03-06|Tama Tlo Kk|Treatment apparatus and treatment method of shellfish|
CN101250222A|2008-03-05|2008-08-27|深圳市圣西马生物技术有限公司|Ascidian antibacterial peptide, precursor peptide, coding gene and use thereof|GB201010176D0|2010-06-17|2010-07-21|Bergen Teknologioverforing As|Method|
WO2018124963A1|2016-12-30|2018-07-05|Marin Biogas|Device and system for trophic cultivation of organisms in water|
法律状态:
2019-04-30| NUG| Patent has lapsed|
优先权:
申请号 | 申请日 | 专利标题
SE0901154A|SE535011C2|2009-09-04|2009-09-04|Production system for the production of biomass for gas production|SE0901154A| SE535011C2|2009-09-04|2009-09-04|Production system for the production of biomass for gas production|
DK10814024.5T| DK2473611T3|2009-09-04|2010-09-03|System for producing raw material for biogas production|
ES10814024.5T| ES2620229T3|2009-09-04|2010-09-03|A system to produce a raw material for biogas production|
PT108140245T| PT2473611T|2009-09-04|2010-09-03|A system to produce feedstock for biogas production|
PCT/SE2010/000215| WO2011028163A1|2009-09-04|2010-09-03|A system to produce feedstock for biogas production|
EP10814024.5A| EP2473611B1|2009-09-04|2010-09-03|A system to produce feedstock for biogas production|
CN201080046332.3A| CN102597249B|2009-09-04|2010-09-03|A system to produce feedstock for biogas production|
HRP20170369TT| HRP20170369T1|2009-09-04|2017-03-06|A system to produce feedstock for biogas production|
[返回顶部]