MD4244C1 - Combined anaerobic reactor for the production of biomethane - Google Patents
Combined anaerobic reactor for the production of biomethaneInfo
- Publication number
- MD4244C1 MD4244C1 MDA20120052A MD20120052A MD4244C1 MD 4244 C1 MD4244 C1 MD 4244C1 MD A20120052 A MDA20120052 A MD A20120052A MD 20120052 A MD20120052 A MD 20120052A MD 4244 C1 MD4244 C1 MD 4244C1
- Authority
- MD
- Moldova
- Prior art keywords
- bioreactor
- liquid
- biomethane
- receiver
- valve
- Prior art date
Links
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 18
- 239000007788 liquid Substances 0.000 claims abstract description 39
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims abstract description 23
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 13
- 239000001257 hydrogen Substances 0.000 claims abstract description 13
- 244000005706 microflora Species 0.000 claims abstract description 10
- 230000005672 electromagnetic field Effects 0.000 claims abstract description 8
- 239000010802 sludge Substances 0.000 claims abstract description 7
- 125000004435 hydrogen atom Chemical class [H]* 0.000 claims abstract 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 23
- 238000000746 purification Methods 0.000 claims description 10
- 238000010521 absorption reaction Methods 0.000 claims description 6
- 150000001875 compounds Chemical class 0.000 claims description 5
- 239000002923 metal particle Substances 0.000 claims description 5
- 230000033228 biological regulation Effects 0.000 claims description 3
- 239000000696 magnetic material Substances 0.000 claims description 3
- 238000007599 discharging Methods 0.000 claims description 2
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- 239000000203 mixture Substances 0.000 abstract description 11
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- 210000002445 nipple Anatomy 0.000 abstract 4
- 239000003245 coal Substances 0.000 abstract 1
- 238000000605 extraction Methods 0.000 abstract 1
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 26
- 238000000034 method Methods 0.000 description 17
- 230000008569 process Effects 0.000 description 17
- 239000001569 carbon dioxide Substances 0.000 description 13
- 229910002092 carbon dioxide Inorganic materials 0.000 description 13
- 238000000855 fermentation Methods 0.000 description 11
- 230000003851 biochemical process Effects 0.000 description 9
- 239000007789 gas Substances 0.000 description 8
- 239000002245 particle Substances 0.000 description 8
- 230000009471 action Effects 0.000 description 6
- 230000004151 fermentation Effects 0.000 description 6
- 150000002431 hydrogen Chemical class 0.000 description 6
- 230000000696 methanogenic effect Effects 0.000 description 6
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 5
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 5
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 5
- 229910052799 carbon Inorganic materials 0.000 description 5
- 230000018109 developmental process Effects 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 244000005700 microbiome Species 0.000 description 4
- 239000012071 phase Substances 0.000 description 4
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 3
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 3
- 239000007791 liquid phase Substances 0.000 description 3
- 239000010808 liquid waste Substances 0.000 description 3
- 229910052717 sulfur Inorganic materials 0.000 description 3
- 239000011593 sulfur Substances 0.000 description 3
- 241000196324 Embryophyta Species 0.000 description 2
- 238000007792 addition Methods 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 230000000739 chaotic effect Effects 0.000 description 2
- 230000005611 electricity Effects 0.000 description 2
- 238000011049 filling Methods 0.000 description 2
- XLYOFNOQVPJJNP-ZSJDYOACSA-N heavy water Substances [2H]O[2H] XLYOFNOQVPJJNP-ZSJDYOACSA-N 0.000 description 2
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 230000033001 locomotion Effects 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000010815 organic waste Substances 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 238000005507 spraying Methods 0.000 description 2
- 230000004936 stimulating effect Effects 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- 244000075850 Avena orientalis Species 0.000 description 1
- 235000007319 Avena orientalis Nutrition 0.000 description 1
- 229910003296 Ni-Mo Inorganic materials 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 239000005864 Sulphur Substances 0.000 description 1
- 241000209140 Triticum Species 0.000 description 1
- 235000021307 Triticum Nutrition 0.000 description 1
- 240000008042 Zea mays Species 0.000 description 1
- 235000005824 Zea mays ssp. parviglumis Nutrition 0.000 description 1
- 235000002017 Zea mays subsp mays Nutrition 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000000789 acetogenic effect Effects 0.000 description 1
- 239000013543 active substance Substances 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000004520 agglutination Effects 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- UYJXRRSPUVSSMN-UHFFFAOYSA-P ammonium sulfide Chemical compound [NH4+].[NH4+].[S-2] UYJXRRSPUVSSMN-UHFFFAOYSA-P 0.000 description 1
- 230000003321 amplification Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000013065 commercial product Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 235000005822 corn Nutrition 0.000 description 1
- 238000005202 decontamination Methods 0.000 description 1
- 230000003588 decontaminative effect Effects 0.000 description 1
- 238000007872 degassing Methods 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000000265 homogenisation Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 239000013067 intermediate product Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- DDTIGTPWGISMKL-UHFFFAOYSA-N molybdenum nickel Chemical compound [Ni].[Mo] DDTIGTPWGISMKL-UHFFFAOYSA-N 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 238000003199 nucleic acid amplification method Methods 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 239000005077 polysulfide Substances 0.000 description 1
- 229920001021 polysulfide Polymers 0.000 description 1
- 150000008117 polysulfides Polymers 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000006479 redox reaction Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 239000007779 soft material Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 150000004763 sulfides Chemical class 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- -1 triterpene compounds Chemical class 0.000 description 1
- 150000003648 triterpenes Chemical class 0.000 description 1
- 235000019195 vitamin supplement Nutrition 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/36—Hydrogen production from non-carbon containing sources, e.g. by water electrolysis
Landscapes
- Apparatus Associated With Microorganisms And Enzymes (AREA)
Abstract
Description
Invenţia se referă la instalaţii pentru obţinerea biometanului în componenţa biogazului şi poate fi utilizată în diferite ramuri ale agriculturii şi industriei de prelucrare. The invention refers to installations for obtaining biomethane in the composition of biogas and can be used in different branches of agriculture and the processing industry.
Biogazul reprezintă o sursă regenerabilă de energie, şi are drept obiectiv intensificarea procesului de obţinere a biometanului prin implementarea unor particularităţi constructive şi prin introducerea în el a unor adaosuri biologic active stimulatoare pentru majorarea producţiei de biometan, creşterea gradului de purificare şi reducerea costului. Invenţia include un proces complex tehnic, tehnologic şi biochimic de obţinere a biogazului, folosind ca materie primă deşeurile agricole şi ale industriei prelucrătoare, cum ar fi borhotul de alcool sau divin. În această ordine de idei invenţia propusă poate fi aplicată pentru epurarea apelor uzate de înaltă încărcare ale întreprinderilor agroindustriale pentru obţinerea biogazului şi pe baza acestuia a energiei electrice şi termice, a nămolurilor stabilizate, care pot servi în calitate de fertilizanţi sau adaosuri vitaminizate pentru hrana animalelor, cu asigurarea aceluiaşi timp de protecţie a mediului înconjurător şi de dezvoltare socio-economică durabilă. Biogas represents a renewable source of energy, and its objective is to intensify the process of obtaining biomethane by implementing some constructive features and by introducing into it some biologically active additives to increase the production of biomethane, increase the degree of purification and reduce the cost. The invention includes a complex technical, technological and biochemical process for obtaining biogas, using as raw material agricultural and processing industry waste, such as alcohol or divine borhot. In this sense, the proposed invention can be applied for the treatment of high-load wastewater of agro-industrial enterprises to obtain biogas and, based on it, electricity and thermal energy, of stabilized sludge, which can serve as fertilizers or vitamin supplements for animal feed , ensuring at the same time environmental protection and sustainable socio-economic development.
Este cunoscut un bioreactor anaerob pentru decontaminarea compuşilor organici greu biodegradabili, care conţine un corp, conducte de admisie şi de evacuare a lichidului tratat, un suport solid pentru fixarea microflorei şi un strat de microfloră granulară, precum şi conducte de evacuare a nămolului şi biogazului, un hidrolizor şi un generator de câmp electromagnetic rotativ [1]. An anaerobic bioreactor for the decontamination of hard-to-biodegradable organic compounds is known, which contains a body, inlet and outlet pipes for the treated liquid, a solid support for fixing the microflora and a layer of granular microflora, as well as sludge and biogas outlet pipes, a hydrolyzer and a rotating electromagnetic field generator [1].
Acest bioreactor nu asigură o capacitate suficientă a procesului şi o producţie majoră de biometan pentru utilizare. This bioreactor does not provide sufficient process capacity and major biomethane production for use.
Problema tehnică pe care o rezolvă invenţia este majorarea producţiei de biometan şi a gradului de purificare a lui, asigurarea eficienţei procesului în flux continuu şi reducerea cheltuielilor materiale şi de exploatare. The technical problem that the invention solves is to increase biomethane production and its degree of purification, ensure the efficiency of the process in continuous flow and reduce material and operating expenses.
Reactorul anaerob combinat pentru obţinerea biometanului înlătură dezavantajele menţionate mai sus prin aceea că este constituit dintr-un bioreactor cu corp cilindric cu fund conic, unit cu un ştuţ de evacuare a nămolului. În bioreactor este amplasată o încărcătură pentru fixarea microflorei şi un indicator de nivel. În partea superioară a bioreactorului este instalat un rezervor, dotat cu un indicator de nivel, iar la trecerea din rezervor în corp este amplasată o supapă cu flotor. Pe rezervor este amplasat un agitator electromagnetic, care conţine particule metalice dintr-un material magnetic moale, un generator de câmp electromagnetic rotativ, conectat la un variator de curent trifazat, un ştuţ de alimentare cu lichid supus tratării şi un ventil pentru evacuarea lui în rezervor. În partea inferioară a bioreactorului este instalat un receiver, care este dotat cu un indicator de nivel automat, conectat la un bloc de comandă, cuplat cu o pompă, dotată cu un ejector metan-lichid, care, prin intermediul unei conducte de aspiraţie a biometanului, comunică cu partea superioară a bioreactorului. Ejectorul este racordat la un pulverizator şi la un aspirator, amplasat la fundul corpului. În partea inferioară a receiverului este racordat un ştuţ cu un ventil de reglare şi o conductă de recirculare, unită la o pompă, care este cuplată cu blocul de comandă şi unită cu un ejector de lichid, unit cu un electrogenerator cu diafragmă de hidrogen şi un distribuitor perforat, amplasat deasupra aspiratorului. În partea superioară a receiverului este montat un furtun, unit printr-un sifon cu o cameră de absorbţie, umplută cu cărbune activat pentru purificarea biometanului de compuşi sulfuroşi, racordată la corp şi dotată cu un dispozitiv de acţionare cu vibrare şi un ştuţ de evacuare a metanului cu un ventil. The combined anaerobic reactor for obtaining biomethane removes the disadvantages mentioned above in that it consists of a bioreactor with a cylindrical body with a conical bottom, joined with a sludge discharge nozzle. In the bioreactor there is a charge for fixing the microflora and a level indicator. A reservoir is installed in the upper part of the bioreactor, equipped with a level indicator, and a float valve is placed at the transition from the reservoir to the body. An electromagnetic stirrer is placed on the tank, which contains metal particles of a soft magnetic material, a rotating electromagnetic field generator, connected to a three-phase current variator, a nozzle for supplying liquid to be treated and a valve for its discharge into the tank . A receiver is installed in the lower part of the bioreactor, which is equipped with an automatic level indicator, connected to a control block, coupled with a pump, equipped with a methane-liquid ejector, which, by means of a biomethane suction pipe , communicates with the upper part of the bioreactor. The ejector is connected to a sprayer and a vacuum cleaner, located at the bottom of the body. In the lower part of the receiver is connected a spigot with a regulation valve and a recirculation pipe, connected to a pump, which is coupled to the control block and connected to a liquid ejector, connected to an electrogenerator with a hydrogen diaphragm and a perforated distributor, located above the vacuum cleaner. A hose is mounted in the upper part of the receiver, connected by a siphon to an absorption chamber, filled with activated carbon for the purification of biomethane from sulphurous compounds, connected to the body and equipped with a vibration actuation device and a discharge nozzle methane with a valve.
Rezultatul tehnic al invenţiei constă în următoarele. The technical result of the invention consists in the following.
La alimentarea cu curent alternativ a generatorului, care poate fi un stator standard de electromotor, se formează un câmp electromagnetic rotativ, sub acţiunea căruia particulele metalice, cilindrice sau de altă formă, confecţionate dintr-un material magnetic moale, cum ar fi oţelul cu conţinut mic de carbon, care se află în interiorul corpului magnetic al agitatorului electromagnetic şi cantitatea cărora variază între 2,6 şi 5,5% vol., încep a se roti haotic şi a se ciocni, formând un strat magnetic fluidizat. Raportul optim dintre lungimea acestor particule şi diametrul lor (l/d), pentru diametrul de l,5 mm, se află în limitele 5...6. Totodată, conform datelor cunoscute, particulele se rotesc în jurul axelor lor cu o viteză unghiulară variabilă, deplasându-se haotic în volumul stratului cu o viteza unghiulară (φ), care are valorile probabile medii: When supplying alternating current to the generator, which can be a standard electric motor stator, a rotating electromagnetic field is formed, under the action of which metallic particles, cylindrical or otherwise, made of a soft magnetic material, such as steel containing little carbon, which is inside the magnetic body of the electromagnetic stirrer and the amount of which varies between 2.6 and 5.5% vol., start to rotate chaotically and collide, forming a fluidized magnetic layer. The optimal ratio between the length of these particles and their diameter (l/d), for the diameter of 1.5 mm, is within 5...6. At the same time, according to the known data, the particles rotate around their axes with a variable angular velocity, moving chaotically in the volume of the layer with an angular velocity (φ), which has the average probable values:
φ = 0,415·102B-0,45(l/d)- 0,52d-0,28C-0,25[l(R-r)] 0,03. φ = 0.415·102B-0.45(l/d)- 0.52d-0.28C-0.25[l(R-r)] 0.03.
Afară de aceasta, are loc o rotaţie circulară de translaţie rotativă a întregului strat global în direcţia rotirii câmpului cu valorile cele mai probabile ale vitezei mişcării de translaţie (ω): Apart from this, there is a circular translational rotation of the entire global layer in the direction of the rotation of the field with the most probable values of the speed of the translational movement (ω):
ω = 0,327·10-2B0,82(l/d)- 0,13d-0,28C0,25[l/(R-r)]- 0,83, ω = 0.327·10-2B0.82(l/d)- 0.13d-0.28C0.25[l/(R-r)]- 0.83,
unde 1/d este criteriul parametric de similitudine (l - lungimea, d - diametrul particulelor); where 1/d is the parametric similarity criterion (l - length, d - particle diameter);
B - intensitatea câmpului electromagnetic, T1; B - electromagnetic field intensity, T1;
R-r = ΔR - distanţa dintre electrozi; R-r = ΔR - the distance between the electrodes;
C - concentraţia particulelor în volumul agitatorului electromagnetic. C - concentration of particles in the volume of the electromagnetic stirrer.
Un atare caracter al mişcării haotice a particulelor metalice şi al ciocnirilor între ele conduce la faptul că particulele mecanice solide, cum ar fi particulele mari de crupe de grâu sau porumb, conţinute în borhotul de la producerea alcoolului şi reprezentând celuloza, sunt supuse unei acţiuni mecanice şi magnetohidrodinamice intensive, în urma căreia are loc nu numai mărunţirea lor, dar şi omogenizarea prin dezagregarea parţială a legăturilor intermoleculare până la starea gelatinoasă sau solubilă în apă. Such a character of the chaotic movement of metal particles and the collisions between them leads to the fact that solid mechanical particles, such as large particles of wheat or corn groats, contained in the borhot from the production of alcohol and representing cellulose, are subjected to mechanical action and intensive magnetohydrodynamics, as a result of which not only their shredding takes place, but also their homogenization through the partial disaggregation of the intermolecular bonds until they become gelatinous or soluble in water.
La aceasta contribuie şi acţiunea câmpului magnetic, care înlesneşte ruperea legăturilor polimerice ale compuşilor macromoleculari şi creşterea masei organice acceptabile în calitate de hrană a microflorei în procesele biochimice de fermentare anaerobă, precum şi, respectiv, creşterea producţiei de biometan. The action of the magnetic field also contributes to this, which facilitates the breaking of the polymer bonds of the macromolecular compounds and the increase of the organic mass acceptable as food for the microflora in the biochemical processes of anaerobic fermentation, as well as, respectively, the increase in biomethane production.
Concomitent, se asigură posibilitatea amestecării uniforme a microorganismelor biologic active stimulatoare, introduse în mod special în lichidul supus tratării, cum ar fi compuşii seriei triterpenice, acţiunea cărora accelerează desfăşurarea proceselor de fermentare anaerobă, ceea ce majorează producţia de biogaz. At the same time, the possibility of uniform mixing of stimulating biologically active microorganisms, specially introduced into the treated liquid, such as compounds of the triterpene series, whose action accelerates the development of anaerobic fermentation processes, which increases biogas production, is ensured.
Condiţiile de vidare a bioreactorului cu ajutorul sistemului de ejectoare asigură evacuarea în flux continuu a biogazului, contribuie la majorarea producţiei lui, deoarece în lipsa acesteia microbulele de gaze degajate (CH4, CO2 etc.) sunt adsorbite de microorganisme, ceea ce conduce la inhibarea desfăşurării procesului biochimic. The vacuum conditions of the bioreactor with the help of the ejector system ensure the discharge of biogas in a continuous flow, contribute to increasing its production, because without it the microbubbles of released gases (CH4, CO2, etc.) are adsorbed by microorganisms, which leads to the inhibition of the development biochemical process.
Ejectarea este asigurată prin funcţionarea pompei care evacuează o parte din lichidul tratat în partea inferioară a bioreactorului, aspirând biogazul cu formarea unei faze gaz-lichid. Totodată se creează condiţii, datorită cărora bioxidul de carbon conţinut în biogaz, solubilitatea căruia în mediul acvatic este mai mare decât a metanului, se dizolvă în receiver. În urma pulverizării fazei gaz-lichid, biometanul se degajă într-o formă mai concentrată şi, ulterior, este îndreptat spre purificarea avansată, iar CO2 saturează faza lichidă şi este evacuat în partea inferioară a receiverului, unde cantitatea lui este controlată cu ajutorul unui indicator automat de nivel. The ejection is ensured by the operation of the pump that evacuates part of the treated liquid in the lower part of the bioreactor, sucking the biogas with the formation of a gas-liquid phase. At the same time, conditions are created, thanks to which the carbon dioxide contained in the biogas, whose solubility in the aquatic environment is higher than that of methane, dissolves in the receiver. After spraying the gas-liquid phase, biomethane is released in a more concentrated form and, subsequently, it is directed to the advanced purification, and CO2 saturates the liquid phase and is discharged into the lower part of the receiver, where its quantity is controlled with the help of an indicator automatic level.
Pe măsura atingerii nivelului prestabilit de lichid în vasul receiverului, semnalul căruia este transmis blocului de comandă, acesta, la rândul său, pune în funcţiune pompa de recirculare şi ejectorul gaz-lichid trage hidrogenul de electroliză din electrogeneratorul cu diafragmă de hidrogen. În acest timp are loc amestecarea H2 cu CO2 conţinut în lichidul, care intră din nou în procesul metanogen. Astfel, recircularea lichidului supus tratării intensifică procesul schimbului şi transportului de masă în bioreactorul care conţine o încărcătură pentru fixarea microflorei şi, concomitent, conduce la interacţiunea biochimică a ambelor gaze în condiţiile metanogene şi transformarea lor cu forma biometanului conform reacţiei generale: CO2+4H2→CH4+2H2O. As soon as the preset level of liquid in the receiver vessel is reached, the signal of which is transmitted to the control block, which, in turn, starts the recirculation pump and the gas-liquid ejector pulls the electrolysis hydrogen from the hydrogen diaphragm electrogenerator. During this time, H2 mixes with CO2 contained in the liquid, which enters the methanogenic process again. Thus, the recirculation of the treated liquid intensifies the mass exchange and transport process in the bioreactor that contains a load for fixing the microflora and, at the same time, leads to the biochemical interaction of both gases under methanogenic conditions and their transformation into the form of biomethane according to the general reaction: CO2+4H2→ CH4+2H2O.
Hidrogenul din componenţa biogazului, ca şi CO2, se degajă la faza acetogenă a procesului biochimic al fermentării anaerobe. Însă cauza cantităţii ridicate de CO2 în componenţa biogazului, care se formează în condiţii standard de fermentare anaerobă a deşeurilor organice lichide, este cantitatea insuficientă de H2, de aceea introducerea suplimentară a hidrogenului electrolizat asigură un raport balansat al gazelor, apropiat de cel stoichiometric, şi o producţie majorată a biometanului în procesul biochimic sumar. Hydrogen from the biogas composition, like CO2, is released during the acetogenic phase of the biochemical process of anaerobic fermentation. But the cause of the high amount of CO2 in the composition of biogas, which is formed under standard conditions of anaerobic fermentation of liquid organic waste, is the insufficient amount of H2, therefore the additional introduction of electrolyzed hydrogen ensures a balanced ratio of gases, close to the stoichiometric one, and an increased production of biomethane in the summary biochemical process.
Intensificarea proceselor de schimb de masă în bioreactor favorizează amplificarea acţiunii microadaosurilor biologic active şi dezvoltarea efectului sinergetic al structurii chimice triterpenice, de exemplu, care conduce la majorarea capacităţii procesului biochimic al fermentării anaerobe a deşeurilor lichide organice şi creşterea producţiei de biometan până la valori maxime. The intensification of mass exchange processes in the bioreactor favors the amplification of the action of biologically active microadditions and the development of the synergistic effect of the triterpenic chemical structure, for example, which leads to the increase in the capacity of the biochemical process of anaerobic fermentation of organic liquid waste and the increase of biomethane production to maximum values.
Biogazul admis din receiver conţine, de asemenea, un şir de impurităţi, dintre care cele mai agresive sunt compuşii sulfuroşi, care sunt supuşi purificării avansate într-o cameră de absorbţie umplută cu cărbune activat în calitate de catalizator al proceselor redox. Datorită acestuia, hidrogenul sulfurat, sulful, carbonul sau mercaptanii sunt oxidaţi de oxigen până la sulf elementar conform reacţiilor: The biogas admitted from the receiver also contains a series of impurities, the most aggressive of which are sulfur compounds, which undergo advanced purification in an absorption chamber filled with activated carbon as a catalyst for redox processes. Thanks to it, hydrogen sulfide, sulfur, carbon or mercaptans are oxidized by oxygen to elemental sulfur according to the reactions:
2H2S+O2=2H2O+2S+Q, 2H2S+O2=2H2O+2S+Q,
CS2+O2=CO2+2S+Q. CS2+O2=CO2+2S+Q.
Reacţia este accelerată în prezenţa amoniacului în concentraţii de până la 0,39 g/m3, care în mod normal întotdeauna se conţine în biogaz în cantităţi mici. Temperatura optimă a acestui proces este de 20...40°C. În legătură cu efectul caloric mare, aceste reacţii au loc cu o intensitate înaltă a procesului. The reaction is accelerated in the presence of ammonia in concentrations up to 0.39 g/m3, which is normally always contained in biogas in small quantities. The optimal temperature for this process is 20...40°C. In connection with the high caloric effect, these reactions take place with a high intensity of the process.
La acumularea a cca 100% de sulf din masa carbonului, reacţiile de oxido-reducere sunt frânate şi carbonul activat este regenerat. Din carbonul uzat sulful este extras cu soluţie de sulfură de amoniu: At the accumulation of approx. 100% sulfur from the mass of carbon, the redox reactions are stopped and the activated carbon is regenerated. Sulfur is extracted from spent carbon with ammonium sulfide solution:
(NH4)2S+nS= (NH4)2Sn+1 . (NH4)2S+nS= (NH4)2Sn+1 .
Apoi polisulfura de amoniu este descompusă la încălzire cu degajare cu sulf elementar: Ammonium polysulfide is then decomposed on heating with release of elemental sulphur:
(NH4)2Sn+1=2NH3+H2S+nS1, (NH4)2Sn+1=2NH3+H2S+nS1,
care este un produs comercial de calitate bună. which is a good quality commercial product.
Cărbunele activat se încarcă în camera de absorbţie în straturi: primul strat de jos are dimensiuni mari ale particulelor (cca 10 mm), urmează apoi stratul cu dimensiuni de 2...4 mm şi, în sfârşit, stratul superior de 1...2 mm. Gradul necesar de purificare este obţinut la o viteză a biogazului de până la 80 mm/s. The activated carbon is loaded into the absorption chamber in layers: the first bottom layer has large particle sizes (approx. 10 mm), then the layer with sizes of 2...4 mm and, finally, the upper layer of 1... 2 mm. The required degree of purification is obtained at a biogas velocity of up to 80 mm/s.
Datorită regenerării, carbonul activat poate fi utilizat pe termen lung, pe parcursul a doi şi mai mulţi ani. Thanks to the regeneration, the activated carbon can be used in the long term, during two and more years.
Invenţia se explică prin desenul din figură, în care este reprezentată schema reactorului anaerob combinat pentru obţinerea biometanului. The invention is explained by the drawing in the figure, in which the scheme of the combined anaerobic reactor for obtaining biomethane is represented.
Reactorul anaerob combinat pentru obţinerea biometanului este constituit din bioreactorul 2 cu corpul cilindric 1 cu fund conic, unit cu ştuţul 3 de evacuare a nămolului, încărcătura 4 pentru fixarea microflorei, indicatorii de nivel 5 şi 6 pentru înregistrare, dispozitivul 7, compus din flotorul 8 şi supapa 9, rezervorul 10, agitatorul electromagnetic 11 cu ştuţul 12 de alimentare cu lichid supus tratării şi ventilul 13 pentru evacuarea lui în rezervorul 10. În interiorul agitatorului electromagnetic 11 sunt plasate particulele metalice 14 dintr-un material moale, iar în exterior - generatorul 15 de câmp electromagnetic rotativ, conectat la variatorul 16 de curent trifazat. În partea inferioară a bioreactorului 2 este instalat receiverul 17, care este dotat cu indicatorul de nivel automat 18, conectat la blocul de comandă 19, cuplat cu pompa 20, dotată cu ejectorul 21 metan-lichid, care, prin intermediul conductei 24 de aspiraţie a biometanului, comunică cu partea superioară a bioreactorului 2, totodată ejectorul 21 este racordat la pulverizatorul 25 şi la aspiratorul 23 prin conducta 22. În partea inferioară a receiverului 17 este racordat ştuţul 26 cu ventilul de reglare 27 şi conducta de recirculare 28, unită la pompa 29, care este cuplată cu blocul de comandă 19 şi unită cu ejectorul 30 de lichid, unit cu electrogeneratorul 31 cu diafragmă de hidrogen, care este dotat cu clapeta de reţinere 32 şi cu distribuitorul perforat 33, amplasat deasupra aspiratorului 23. În partea superioară a receiverului 17 este montat furtunul 34, unit prin sifonul 35 cu camera de absorbţie 36, umplută cu cărbune activat 37 pentru purificarea biometanului de compuşi sulfuroşi, racordată la corpul 1 şi dotată cu dispozitivul de acţionare 38 cu vibrare şi ştuţul 39 de evacuare a metanului cu ventilul 40. The combined anaerobic reactor for the production of biomethane consists of the bioreactor 2 with the cylindrical body 1 with a conical bottom, connected to the sludge outlet 3, the charge 4 for fixing the microflora, the level indicators 5 and 6 for registration, the device 7, composed of the float 8 and the valve 9, the tank 10, the electromagnetic stirrer 11 with the nozzle 12 for supplying the liquid to be treated and the valve 13 for its discharge into the tank 10. Inside the electromagnetic stirrer 11 are placed the metal particles 14 of a soft material, and outside - the generator 15 rotating electromagnetic field, connected to the variator 16 of three-phase current. In the lower part of the bioreactor 2, the receiver 17 is installed, which is equipped with the automatic level indicator 18, connected to the control block 19, coupled with the pump 20, equipped with the methane-liquid ejector 21, which, through the suction pipe 24, of biomethane, communicates with the upper part of the bioreactor 2, at the same time the ejector 21 is connected to the sprayer 25 and the vacuum cleaner 23 through the pipe 22. In the lower part of the receiver 17 is connected the nozzle 26 with the regulation valve 27 and the recirculation pipe 28, connected to the pump 29, which is coupled to the control block 19 and connected to the liquid ejector 30, connected to the electrogenerator 31 with hydrogen diaphragm, which is equipped with the retaining flap 32 and the perforated distributor 33, located above the vacuum cleaner 23. In the upper part of the receiver 17 is fitted with the hose 34, connected through the siphon 35 with the absorption chamber 36, filled with activated carbon 37 for the purification of biomethane from sulphurous compounds, connected to the body 1 and equipped with the actuator 38 with vibration and the nozzle 39 for discharging methane with valve 40.
În calitate de electrogenerator cu diafragmă de hidrogen poate fi utilizată oricare din construcţiile cunoscute, însă cea mai bună dintre acestea este electroreactorul cu diafragmă, dotat cu electrozi plaţi sau poroşi în flux continuu, cu suprafaţa modificată cu aliaje Ni-Re, Ni-W sau Ni-Mo, care posedă o supratensiune joasă de degajare a hidrogenului şi un consum redus de energie electrică. Alimentarea lor cu curent electric poate fi realizată de la instalaţiile de cogenerare, care funcţionează cu biogaz în cadrul instalaţiilor de epurare. Any of the known constructions can be used as a hydrogen diaphragm electrogenerator, but the best of these is the diaphragm electroreactor, equipped with flat or porous electrodes in continuous flow, with the surface modified with Ni-Re, Ni-W or Ni-Mo, which has low hydrogen release overvoltage and low power consumption. They can be supplied with electricity from the cogeneration plants, which operate with biogas within the purification plants.
Reactorul anaerob combinat pentru obţinerea biometanului funcţionează în modul următor. The combined anaerobic reactor for obtaining biomethane works in the following way.
Înainte de începutul funcţionării şi pentru acţionarea reactivului, în deşeurile lichide, cum ar fi borhotul de alcool şi divin, sunt introduse microcantităţi de adaosuri biologic active naturale din grupul compuşilor triterpenici ai procesului de metanogeneză prin ştuţul 12 în agitatorul electromagnetic 11 şi se conectează sursa la curent alternativ de la variatorul 16 la generatorul 15 şi, în urma apariţiei câmpului electromagnetic rotativ, particulele metalice 14 încep o rotire haotică intensă, agitând lichidul cu adaosuri şi omogenizând particulele mecanice 14 conţinute în el. Apoi se deschide ventilul 13 şi amestecul omogenizat trece în rezervorul 10 şi, prin dispozitivul 7 cu flotor 8 deschis şi supapa 9, se revarsă în bioreactorul 2, care prealabil este umplut cu încărcătura 4 pentru fixarea microflorei. Pentru iniţierea fermentării metanogene împreună cu lichidul supus tratării poate fi introdusă microflora activă din instalaţiile analoage ale bioreactoarelor anaerobe în funcţiune. Din momentul atingerii nivelului prestabilit al lichidului în bioreactorul 2, indicat de indicatorul de nivel 5, flotorul 8 cu supapa 9 se ridică la suprafaţă şi închide revărsarea lichidului din rezervorul 10, iar în bioreactorul 2 se desfăşoară procesul de fermentare metanică. Before the start of operation and for the operation of the reagent, microquantities of natural biologically active additions from the group of triterpene compounds of the methanogenesis process are introduced into the liquid waste, such as alcohol and divine borth, through the nozzle 12 in the electromagnetic stirrer 11 and the source is connected to alternating current from the variator 16 to the generator 15 and, following the appearance of the rotating electromagnetic field, the metal particles 14 begin an intense chaotic rotation, agitating the liquid with additions and homogenizing the mechanical particles 14 contained in it. Then the valve 13 is opened and the homogenized mixture passes into the tank 10 and, through the device 7 with open float 8 and the valve 9, it is poured into the bioreactor 2, which is previously filled with the charge 4 for fixing the microflora. In order to initiate the methanogenic fermentation, active microflora can be introduced from the analogous installations of the anaerobic bioreactors in operation together with the treated liquid. From the moment of reaching the predetermined level of liquid in bioreactor 2, indicated by level indicator 5, the float 8 with valve 9 rises to the surface and closes the liquid overflow from tank 10, and in bioreactor 2 the methane fermentation process takes place.
După aceasta se pune în funcţiune pompa 20 şi lichidul supus tratării trece prin aspiratorul 23, conducta 22 şi ejectorul 21, creând vid, datorită căruia biogazul este aspirat în el cu formarea unui amestec gaz-lichid, care este refulat sub presiune în pulverizatorul 25, montat în receiverul 17, umplându-l până la nivelul stabilit, care este controlat de indicatorul de nivel automat 18. After that, the pump 20 is put into operation and the liquid to be treated passes through the aspirator 23, the pipe 22 and the ejector 21, creating a vacuum, thanks to which the biogas is sucked into it with the formation of a gas-liquid mixture, which is pumped under pressure into the sprayer 25, mounted in the receiver 17, filling it to the set level, which is controlled by the automatic level indicator 18.
Vacuumarea pernei de gaz, realizată de ejectorul 21 de deasupra suprafeţei lichidului supus tratării din bioreactorul 2, amplifică degajarea gazului din el, ceea ce reduce posibilitatea inhibării de către biogaz a activităţii microorganismelor şi o intensifică, conducând la majorarea eficienţei globale a procesului de degajare a biogazului. The vacuuming of the gas cushion, carried out by the ejector 21 above the surface of the liquid to be treated in the bioreactor 2, amplifies the release of gas from it, which reduces the possibility of inhibiting the activity of microorganisms by biogas and intensifies it, leading to an increase in the overall efficiency of the release process biogas.
Pe parcursul pulverizării amestecului gaz-lichid, metanul slab solubil în mediul apos şi alţi componenţi gazoşi se acumulează în zona superioară a receiverului 17 şi, prin furtunul 34 şi sifonul 35, se evacuează în camera de absorbţie 36, umplută cu cărbunele activat 37, unde se purifică de compuşi agresivi cu conţinut de sulfuri şi se elimină prin ştuţul 39 cu ventilul 40 deschis pentru a fi ulterior utilizaţi. Pentru evitarea aglutinării cărbunelui activat 37 şi reducerea rezistenţei hidraulice a fluxului gazos, poate fi conectat periodic sau permanent dispozitivul de acţionare 38 cu vibrare pentru fluidizarea umpluturii de cărbune. During the spraying of the gas-liquid mixture, the poorly soluble methane and other gaseous components accumulate in the upper area of the receiver 17 and, through the hose 34 and siphon 35, are evacuated into the absorption chamber 36, filled with the activated carbon 37, where it is purified from aggressive compounds containing sulphides and is removed through the nozzle 39 with the valve 40 open to be used later. In order to avoid agglutination of the activated carbon 37 and to reduce the hydraulic resistance of the gas flow, the vibration actuator 38 can be periodically or permanently connected to fluidize the carbon filling.
Concomitent cu acest proces, lichidul supus tratării şi saturat cu bioxid de carbon (CO2), care se acumulează în partea inferioară a receiverului 17, la semnalul indicatorului de nivel automat 18, prin intermediul blocului de comandă 19, cuplează pompa 29, care prin conducta de recirculare 28 aspiră lichidul în ejectorul 30 de lichid, unde datorită efectului de vidare, prin clapeta de reţinere 32, aspiră hidrogenul generat în electrogeneratorul 31 cu diafragmă de hidrogen şi saturează cu el lichidul, care este apoi refulat prin distribuitorul perforat 33 din nou în bioreactorul 2, asigurând regimul de recirculare. Datorită faptului că în faza gazelor de fermentare se conţin până la 30% vol. de CO2, care posedă o solubilitate superioară în apă, acesta rămâne parţial în componenţa lichidului îmbogăţit cu el. De aceea, în procesul biochimic metanogen, CO2 şi alte produse intermediare ale fermentării reacţionează cu hidrogenul introdus, contribuind prin aceasta la majorarea eficienţei de producere a metanului şi, în general, a conţinutului de biometan în componenţa biogazului. Simultaneously with this process, the liquid subjected to treatment and saturated with carbon dioxide (CO2), which accumulates in the lower part of the receiver 17, at the signal of the automatic level indicator 18, through the control block 19, engages the pump 29, which through the pipe recirculation valve 28 sucks the liquid into the liquid ejector 30, where due to the vacuum effect, through the check valve 32, it sucks the hydrogen generated in the electrogenerator 31 with hydrogen diaphragm and saturates the liquid with it, which is then discharged through the perforated distributor 33 back into bioreactor 2, ensuring the recirculation regime. Due to the fact that the fermentation gas phase contains up to 30% by volume of CO2, which has a superior solubility in water, it remains partially in the composition of the liquid enriched with it. That is why, in the methanogenic biochemical process, CO2 and other intermediate products of fermentation react with the introduced hydrogen, thus contributing to the increase of the methane production efficiency and, in general, of the biomethane content in the biogas composition.
Recircularea lichidului supus tratării cu ajutorul pompei 29 prin conducta 28, ejectorul 30 şi distribuitorul perforat 33 din receiverul 17 în bioreactorul 2, conduce la tulburarea conţinutului acestuia, contribuind prin aceasta la crearea unor condiţii favorabile de schimb şi transferul de masă, amplificând degazarea lui şi ridicarea bulelor de gaze CH4 şi CO2 absorbite la suprafaţă, ceea ce conduce la intensificarea dezvoltării activităţii microorganismelor. Un rol important în procesul metanogen i se atribuie influenţei stimulatoare a microadaosurilor de substanţe biologic active în componenţa lichidului supus tratării, care joacă un rol dublu: accelerează productivitatea procesului de metanogeneză şi servesc drept factor suplimentar în majorarea producţiei de biometan în componenţa biogazului. The recirculation of the liquid subjected to treatment with the help of the pump 29 through the pipe 28, the ejector 30 and the perforated distributor 33 from the receiver 17 in the bioreactor 2, leads to the disturbance of its content, thereby contributing to the creation of favorable exchange conditions and mass transfer, amplifying its degassing and the rise of CH4 and CO2 gas bubbles absorbed on the surface, which leads to the intensification of the development of the activity of microorganisms. An important role in the methanogenic process is attributed to the stimulating influence of microadditions of biologically active substances in the composition of the liquid undergoing treatment, which play a double role: they accelerate the productivity of the methanogenesis process and serve as an additional factor in increasing the production of biomethane in the composition of biogas.
Continuitatea procesului biochimic de fermentare metanogenă a deşeurilor lichide organice este asigurată prin reglarea evacuării unei părţi de lichid tratat prin ştuţul 26 şi ventilul 27, iar nămolul format în bioreactorul 2 este evacuat periodic prin ştuţul 3, de asemenea, datorită prezenţei dispozitivului 7 cu flotor 8 plasat între rezervorul 10 şi bioreactorul 2, care asigură introducerea automată în flux continuu în bioreactor a unei cantităţi de lichid supus tratării. Menţinerea nivelului prestabilit al lichidului în receiverul 17 se asigură în mod automat cu ajutorul indicatorului de nivel automat 18 şi al blocului de comandă 19, care semnalizează cuplarea şi decuplarea pompelor 20 şi 29. The continuity of the biochemical process of methanogenic fermentation of liquid organic waste is ensured by regulating the evacuation of a part of the treated liquid through the nozzle 26 and the valve 27, and the sludge formed in the bioreactor 2 is periodically evacuated through the nozzle 3, also due to the presence of the device 7 with float 8 placed between the reservoir 10 and the bioreactor 2, which ensures the automatic introduction in continuous flow into the bioreactor of a quantity of liquid subject to treatment. Maintaining the preset level of the liquid in the receiver 17 is ensured automatically with the help of the automatic level indicator 18 and the control block 19, which signals the switching on and off of the pumps 20 and 29.
În acest mod se obţine realizarea obiectivelor propuse de majorare a producţiei de biometan şi a gradului necesar de purificare a acestuia, de asigurare a eficienţei procesului în condiţii de flux continuu, de reducere a cheltuielilor materiale şi de exploatare, respectiv, de ieftinire a procesului. Prin acţiune complexă asupra procesului de fermentare anaerobă a deşeurilor lichide organice prevăzute în bioreactorul anaerob combinat propus se asigură reducerea suprafeţelor de producţie şi a investiţiilor capitale datorită majorării productivităţii proceselor biochimice, conţinutul biometanului poate atinge valori de până la 94...97% vol., ceea ce este similar cu gazul natural şi posedă o capacitate calorică mai mare la utilizarea lui. In this way, the proposed objectives of increasing the production of biomethane and the necessary degree of its purification, ensuring the efficiency of the process in continuous flow conditions, reducing the material and operating expenses, respectively, making the process cheaper, are achieved. Through complex action on the process of anaerobic fermentation of organic liquid waste provided in the proposed combined anaerobic bioreactor, the reduction of production areas and capital investments is ensured due to the increase in the productivity of biochemical processes, the biomethane content can reach values of up to 94...97% vol. , which is similar to natural gas and has a higher calorific capacity when used.
1. MD 3062 G2 2006.05.31 1. MD 3062 G2 2006.05.31
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| MD4204B1 (en) * | 2012-03-29 | 2013-02-28 | Univ De Stat Din Moldova | Installation for anaerobic production of biohydrogen |
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| MD885Z (en) * | 2014-08-11 | 2015-09-30 | Институт Прикладной Физики Академии Наук Молдовы | Reactor and process for producing hydrogen |
| MD4376C1 (en) * | 2014-08-22 | 2016-05-31 | Государственный Университет Молд0 | Combined high-pressure biogas production reactor |
| MD4382C1 (en) * | 2014-08-22 | 2016-06-30 | Государственный Университет Молд0 | Combined biogas-production reactor |
| RU2694965C1 (en) * | 2018-08-20 | 2019-07-18 | федеральное государственное бюджетное образовательное учреждение высшего образования "Кемеровский государственный университет" (КемГУ) | Apparatus for simulating conditions for decomposition of coal dressing slugs and low-quality coals by microbiological action |
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| Publication number | Publication date |
|---|---|
| MD4244B1 (en) | 2013-07-31 |
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| FG4A | Patent for invention issued | ||
| KA4A | Patent for invention lapsed due to non-payment of fees (with right of restoration) | ||
| MM4A | Patent for invention definitely lapsed due to non-payment of fees |