CS201953B1 - Method of treating the hydrolysers of the agricultural refuse - Google Patents
Method of treating the hydrolysers of the agricultural refuse Download PDFInfo
- Publication number
- CS201953B1 CS201953B1 CS792290A CS229079A CS201953B1 CS 201953 B1 CS201953 B1 CS 201953B1 CS 792290 A CS792290 A CS 792290A CS 229079 A CS229079 A CS 229079A CS 201953 B1 CS201953 B1 CS 201953B1
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- Czechoslovakia
- Prior art keywords
- yeast
- culture
- medium
- bacterial contamination
- hydrolyzate
- Prior art date
Links
- 238000000034 method Methods 0.000 title claims description 8
- 240000004808 Saccharomyces cerevisiae Species 0.000 claims description 22
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 16
- 230000001580 bacterial effect Effects 0.000 claims description 13
- 238000011109 contamination Methods 0.000 claims description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 8
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 8
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 8
- 239000002609 medium Substances 0.000 claims description 8
- 229910052757 nitrogen Inorganic materials 0.000 claims description 8
- 229910052698 phosphorus Inorganic materials 0.000 claims description 8
- 239000011574 phosphorus Substances 0.000 claims description 8
- 239000002253 acid Substances 0.000 claims description 7
- 239000003112 inhibitor Substances 0.000 claims description 7
- 239000002244 precipitate Substances 0.000 claims description 7
- 238000000855 fermentation Methods 0.000 claims description 5
- 230000004151 fermentation Effects 0.000 claims description 5
- 230000036284 oxygen consumption Effects 0.000 claims description 5
- 210000005253 yeast cell Anatomy 0.000 claims description 5
- 241000894006 Bacteria Species 0.000 claims description 4
- 239000002028 Biomass Substances 0.000 claims description 4
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 4
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 4
- 239000002154 agricultural waste Substances 0.000 claims description 4
- HYBBIBNJHNGZAN-UHFFFAOYSA-N furfural Chemical compound O=CC1=CC=CO1 HYBBIBNJHNGZAN-UHFFFAOYSA-N 0.000 claims description 4
- 239000001963 growth medium Substances 0.000 claims description 4
- 239000004571 lime Substances 0.000 claims description 4
- 239000000463 material Substances 0.000 claims description 4
- 208000035143 Bacterial infection Diseases 0.000 claims description 3
- 238000005273 aeration Methods 0.000 claims description 3
- 208000022362 bacterial infectious disease Diseases 0.000 claims description 3
- 238000005119 centrifugation Methods 0.000 claims description 3
- 239000003610 charcoal Substances 0.000 claims description 3
- 238000012258 culturing Methods 0.000 claims description 3
- 150000004676 glycans Chemical class 0.000 claims description 3
- 230000000813 microbial effect Effects 0.000 claims description 3
- 229920001282 polysaccharide Polymers 0.000 claims description 3
- 239000005017 polysaccharide Substances 0.000 claims description 3
- 239000010902 straw Substances 0.000 claims description 3
- 239000006228 supernatant Substances 0.000 claims description 3
- 241000282887 Suidae Species 0.000 claims description 2
- 238000010564 aerobic fermentation Methods 0.000 claims description 2
- 239000010828 animal waste Substances 0.000 claims description 2
- 239000002054 inoculum Substances 0.000 claims description 2
- 230000029058 respiratory gaseous exchange Effects 0.000 claims description 2
- 238000004062 sedimentation Methods 0.000 claims description 2
- 238000004519 manufacturing process Methods 0.000 claims 2
- 238000006386 neutralization reaction Methods 0.000 claims 2
- 208000002874 Acne Vulgaris Diseases 0.000 claims 1
- 108010009736 Protein Hydrolysates Proteins 0.000 claims 1
- 206010000496 acne Diseases 0.000 claims 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims 1
- 210000004027 cell Anatomy 0.000 claims 1
- 238000004042 decolorization Methods 0.000 claims 1
- 210000003608 fece Anatomy 0.000 claims 1
- 230000003472 neutralizing effect Effects 0.000 claims 1
- 229910052760 oxygen Inorganic materials 0.000 claims 1
- 239000001301 oxygen Substances 0.000 claims 1
- 150000003839 salts Chemical class 0.000 claims 1
- 239000007787 solid Substances 0.000 claims 1
- 244000005700 microbiome Species 0.000 description 4
- 238000005903 acid hydrolysis reaction Methods 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000004821 distillation Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 230000003466 anti-cipated effect Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000003966 growth inhibitor Substances 0.000 description 1
- 238000011081 inoculation Methods 0.000 description 1
- 150000002972 pentoses Chemical group 0.000 description 1
- 230000000737 periodic effect Effects 0.000 description 1
- 230000035755 proliferation Effects 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
Landscapes
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
Description
Vynález ša týká sposobu spracovania hydrolyzátorov poinohospodárskych odpadov na krmné bielkoviny kvasinkovitých mikroorganizmov bez odstraňovania inhibítorov.The invention relates to a process for processing hydrolysers of agricultural waste into feed proteins of yeast microorganisms without removing inhibitors.
Spracovaním róznych poinohospodárskych odpadov na báze róznych lignocelulózových a iných polysacharídových materiálov kyslou hydrolýzou sa získá substrát pre biosyntézu mikrobiálnej hmoty pomocou kvasinkovitých mikroorganizmov. Tieto materiály v dósledku rozkladu pentós obsahujú značné množstvo furolu i ďalších inhibítorov rastu mikroorganizmov. Doterajšie postupy na využitie takýchto surovin předpokládali před vlastnou fermentáciou nákladné odstraňovanie inhibítorov adsorbciou alebo destiláciou. Pri kultivácii kvasinkovitých mikroorganizmov sa takto upravený hydrolyzát neutralizoval na pH 4,5 až 5.Treatment of different agricultural wastes based on different lignocellulosic and other polysaccharide materials by acid hydrolysis yields a substrate for microbial mass biosynthesis using yeast microorganisms. These materials, due to the decomposition of the pentoses, contain a considerable amount of furol and other microorganism growth inhibitors. Prior processes for utilizing such raw materials have anticipated costly removal of inhibitors by adsorption or distillation prior to fermentation. When culturing yeast microorganisms, the hydrolyzate thus treated was neutralized to a pH of 4.5 to 5.
Vyššie uvedené nedostatky sú odstránené spósobom spracovania hydrolyzátorov poinohospodárskych odpadov podlá vynálezu, ktorého podstata spočívá v tom, že sa kyslý hydrolyzát lignocelulózových alebo iných polysacharidových materiálov s případným doživením vhodným zdrojom dusíka a fosforu upraví na pH = 6,0 až 7,0, vzniknutá zrazenina sa odstráni a číry supernatant sa podrobí aerobnej fermentácii pomocou kvasiniek pri pH — 6,0 až 7,0. Výhodou tohto postupu je, že nie je nutné pdstraňovať inhibitory adsorbciou alebo destiláciou s výnimkou, keď sa jedná o ich získavanie ako vedlajšieho produktu. Za uvedených podmienok je rást kvasiniek v porovnaní s rýchlosťou pomnoženia bakteriálnej infekcie dostatočné rýchly. Bakteriálna kontaminácia sa sice vyskytuje aj pri pH 5, avšak v menšej miere.The above-mentioned drawbacks are eliminated by the method of processing of agricultural waste hydrolysers according to the invention, which consists in that the acid hydrolyzate of lignocellulosic or other polysaccharide materials is adjusted to pH = 6.0 to 7.0 with a suitable source of nitrogen and phosphorus. is removed and the clear supernatant is subjected to yeast aerobic fermentation at a pH of 6.0 to 7.0. The advantage of this process is that it is not necessary to remove the inhibitors by adsorption or distillation, except when obtaining them as a by-product. Under these conditions, the growth of yeast is fast enough compared to the rate of growth of the bacterial infection. Bacterial contamination occurs at pH 5, but to a lesser extent.
V ďalšom je předmětný sposob fermentačného spracovania kyslých hydrolyzátorov na bakteriálnu hmotu bližšie objasněný v príkladoch prevedenia, hoci na tieto příklady sa neobmedzuje.In the following, the present method of fermentative processing of acid hydrolysers to a bacterial mass is explained in more detail in the examples, although it is not limited thereto.
Příklad 1Example 1
Použil sa hydrolyzát získaný kyslou hydrolýzou slamy s HC1, ktorý mal 7 % refraktometrickej sušiny, pH 1,9 a obsah furalu 0,07%. Hydrolyzát sa přiživil s KjHPOj (1 g/1), (NH4/2SO4/I g/1) a zneutoalizoval na hodnotu pH 7,0. Vytvořená zrazenina sa oddělila centrifugáciou, alebo sedimentáciou. Círy supernatant sa inokuloval s 1/20 až 1/10 objemu kultury kvasiniek kmeň A 78 zo zbierky Katedry technickej mikrobiologie a biochémie Chemicko technologické j fakulty Slovenskej vysokej školy technickej v Bratislavě a kultivácia sa viedla za aerácie v ban201953 kách na trepačke pri 28 °C počas 24 až 36 h. Získala.sa dobré sedimentujúca biomasa kvasiniek vo výtažku 2,5 g/100 ml média. V médiu pripravenom rovnakým sposobom s tým rozdielom, ’ že sa zneutralizovalo na hodnotu pH 6 a nižšia kultúra nevyrástla ani po niekolkých dňochkultivácie.A hydrolyzate obtained by acid hydrolysis of straw with HCl, which had a 7% refractometric dry matter, pH 1.9 and a fural content of 0.07%, was used. The hydrolyzate was fed with K 3 HPO 3 (1 g / L), (NH 4 / 2SO 4/1 g / L) and neutralized to pH 7.0. The precipitate formed was separated by centrifugation or sedimentation. The clear supernatant was inoculated with 1/20 to 1/10 yeast culture volume strain A 78 from the Department of Technical Microbiology and Biochemistry of the Faculty of Chemical Technology of the Slovak University of Technology in Bratislava and cultivated under aeration in a ban201953 shaker at 28 ° C. for 24 to 36 hours. A good sedimenting yeast biomass was obtained in a yield of 2.5 g / 100 ml of medium. In a medium prepared in the same way, with the difference that it was neutralized to pH 6 and the lower culture did not grow even after several days of cultivation.
Příklad 2Example 2
Hydrolyzát slamy uvedený v příklade 1 sa zneutralizoval na pH 7, vyčíril odstředěním a přiživil zdrojom dusíka a fosforu. Jeden liter média sa inokuloval s 50 ml kultúry kvasiniek A 78 z vyrastených v predchádzajúcich kultiváciách. Použité inokulum bolo čiastočne infikované pohyblivými baktériami a kokmi. Poměr počtu baktérii ku počtu kvasiniek 1 :100.The straw hydrolyzate of Example 1 was neutralized to pH 7, clarified by centrifugation, and fed with a source of nitrogen and phosphorus. One liter of medium was inoculated with 50 ml of A 78 yeast culture grown in previous cultures. The inoculum used was partially infected with motile bacteria and cocci. 1: 100 ratio of bacteria to yeast count.
Kultivovalo sa neasepticky v laboratórnom fermentore objemu 5 1 za aerácie v priebehu 72 hodin systémom pH státu s registráciou spotřeby kyslíka meranou Clarkovou polarografickou elektrodou. Zníženie pH v priebehu kultivácie pod hodnotu pH 6 predávkovaním kyseliny málo za následok zníženie intenzity respirácie a rastu kvasiniek. Zvýšenie alkaiity kultivačného média na hodnotu pH 8 prídavkom lúhu málo za následok rýchle pomnoženie bakteriálnej kontaminácie. Spatnou úpravou acidity na hodnotu pH 7 a zapojením fermentora do systému pH státu došlo k výraznej aliminácii bakteriálnej kontaminácie.It was cultured non-aseptically in a 5 L laboratory fermentor under aeration for 72 hours with a state pH system with a registered oxygen consumption measured by Clark's polarographic electrode. Lowering the pH during cultivation below pH 6 by overdosing acid little results in a decrease in the intensity of respiration and yeast growth. Increasing the alkalinity of the culture medium to a pH of 8 by adding lye little results in a rapid proliferation of bacterial contamination. By reversing the acidity to pH 7 and incorporating the fermenter into the state pH system, bacterial contamination was significantly eliminated.
Ak sa analogická fermentácia uškutóčhila neasepticky pri pH 7 na hydrolyzáte z ktorého sa inhibitory odstránili aktívnym uhlím za tepla, nebolo možné uskutočniť produkciu mikrobiálnej hmoty kvasiniek pre masívnu bakteriálnu infekciu. Bakteriálná kontaminácia sa vyskytovala sice aj pri neaseptickej fermentáoii vedenej pri pH 5, avšak v podstatě menšej miere. Odstránenie časti inhibítorov aktívnym uhlím dovolilo znížiť pH pri kultivácii aj pod hodnotu 6, avšak bakteriálna kontaminácia rástla rýchlejšie ako buňky kvasinkovitých Organizmov a semikontinuálna kultivácia neholá možná. Po 24 h. kultivácii poměr počtu baktérií ku počtu kvasiniek dosiahol hodnotu 1:1 až 2:1, Periodickým preočkovaním kultúry priamo z fermentora do fermentora za neaseptických podmienok na hydrolyzáte živočišného odpadu pH 6 až 7 bolo možné udržať kvasinkovitých organizmov bez prerastenia bakteriálnou kontaraináciou viac ako 4 týždne.If an analogous fermentation was made non-aseptically at pH 7 on the hydrolyzate from which the inhibitors were removed by hot charcoal, it was not possible to produce yeast microbial mass for a massive bacterial infection. Bacterial contamination occurred even in non-aseptic fermentation conducted at pH 5, but to a lesser extent. Removal of a portion of the inhibitors with activated carbon allowed the pH to decrease below 6 during culture, but bacterial contamination grew faster than yeast cells and semi-continuous cultivation was not feasible. After 24 h. The periodic inoculation of the culture directly from the fermenter to the fermenter under non-aseptic conditions on animal waste hydrolyzate pH 6-7 allowed the yeast organisms to be maintained without overgrowing with bacterial contamination for more than 4 weeks.
Příklad 3Example 3
Kyslý hydrolyzát exkrěmentov z velkovýkrmně ošípaných s póvodnou sušinou 5,8 % sa zneutralizoval prídavkom vápna na pH 4,5 a odfarbil s' 2 % aktívneho uhlia za tepla. Po tejto úpravě mal vyčírený roztok následovně zloženie: 3,5 % sušiny. 1,54% redukujúcich látok, 1,2 % celkového dusíka, 0,1 % fosforu a 0,02 % furalu. Jeden liter média sa naočkoval kultúrou kvasiniek kmeň A 78. Počas kultivácie sa tvořila zrazenina, ktorá obalovala buňky kvasiniek vytvárajúc amorfně zhluky. Rast kultúry .sledovaný tvorbou biomasy a na základe rýchlosti spotřeby kyslíka bol malý. Rovnaké problémy vznikali aj v tom případe, keď sa na neutralizáciu použila iná zásada vy tvář aj úca neutralizáciou soli, vo vodě rozpustné, napr. NaOH.The acid hydrolyzate of the excrements from the large-fed pigs with an initial dry weight of 5.8% was neutralized by addition of lime to pH 4.5 and decolorized with 2% hot charcoal. After this treatment, the clarified solution had the following composition: 3.5% dry matter. 1.54% reducing agents, 1.2% total nitrogen, 0.1% phosphorus and 0.02% fural. One liter of the medium was inoculated with yeast culture strain A78. During the cultivation, a precipitate was formed which enveloped the yeast cells forming amorphous clumps. The growth of the culture followed by biomass formation and based on the rate of oxygen consumption was low. The same problems arose when a different water-soluble salt-solubilizing principle, e.g. NaOH.
Pri neutralizácii vápnom alebo s Ca/OH/2 ná hodnotu pH 6 až 7' takto připravené kultivačně médium aj v případe bez odfarbovania s aktívnym uhlím vytvárálo iba malé množstvo zrazenín, ktoré sa okrem toho nezrážali na buňkách kvasiniek a kultúra vykazovala intenzívny rast sprevádzaný rýchlou spotřebou kyslíka. Ukázalo sa, že prídavok zdrojov dusíka a fosforu nie je nutný.When neutralized with lime or with a Ca / OH / 2 pH of 6-7, the culture medium thus prepared, even in the case without decolouration with activated charcoal, produced only a small amount of clots which, moreover, did not precipitate on the yeast cells and the culture showed intense growth accompanied by rapid growth. oxygen consumption. It has been shown that the addition of nitrogen and phosphorus sources is not necessary.
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Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CS792290A CS201953B1 (en) | 1979-04-04 | 1979-04-04 | Method of treating the hydrolysers of the agricultural refuse |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CS792290A CS201953B1 (en) | 1979-04-04 | 1979-04-04 | Method of treating the hydrolysers of the agricultural refuse |
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| Publication Number | Publication Date |
|---|---|
| CS201953B1 true CS201953B1 (en) | 1980-12-31 |
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| Application Number | Title | Priority Date | Filing Date |
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| CS792290A CS201953B1 (en) | 1979-04-04 | 1979-04-04 | Method of treating the hydrolysers of the agricultural refuse |
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| CS (1) | CS201953B1 (en) |
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1979
- 1979-04-04 CS CS792290A patent/CS201953B1/en unknown
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