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3. FOOD ChEMISTRy & bIOTEChNOLOGy 3.1. Lectures

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Chem. Listy, 102, s265–s1311 (2008) Food Chemistry & Biotechnology<br />

P04 ThERMOPhILIC bACTERIA APPLICATION<br />

TO whEy bIODEGRADATION<br />

LIBOR BABáK and RADKA BURDYCHOVá<br />

Institute of Food Science and Biotechnology, Faculty of Chemistry,<br />

Brno University of Technology<br />

Purkyňova 118, 612 00 Brno, Czech Republic,<br />

babak@fch.vutbr.cz<br />

Introduction<br />

In former times the whey was thought as valueless waste<br />

of dairy industry rising in cheese, cottage and casein production.<br />

Its application was in feed only. In these days, the whey<br />

meaning inceases simultaneously with new knowledges of<br />

nutrition, with sepative methods development, envirtonment<br />

protection endeavour and rapid progress of food and pharmaceutical<br />

industry. Environmental aspect is purity rivers maintenance<br />

and it means the prohibition of waste-water disposal<br />

(the whey too). It is possible to make the whey „liquidation“<br />

by the help of microbial systems. Several microbial systems<br />

were used for these purposes but they are still pure described.<br />

Testing of new microbial systems for the degradation ot the<br />

whey is in progress. In this work, the testing of degradation of<br />

the whey medium using the mixture of thermophilic bacteria<br />

is described.<br />

Experimental<br />

Experiments were practised with thermophilic aerobic<br />

culture, the mixture of bacteria of the genus Bacilus and the<br />

genus Thermus (sludge from waste treatment plant Bystřice<br />

pod Hostýnem). The whey from cheese production (type<br />

ermine) was used as the medium. Casein (0.1 mol dm –3<br />

H 2 SO 4 ) and α,β-�lactoglobulins (20 min at 85 °C) were taken<br />

out before cultivations. The whey was centrifuged and pH<br />

value was adjusted. All cultivations were practised in the<br />

laboratory fermentor BIOSTAT B (B. Braun Biotech.) with<br />

working volume 2 dm 3 .<br />

Fig. 1. batch cultivation progress in longer time (312 hours)<br />

s581<br />

Cultivation conditions: multiple turbo-stirrer 250 min –1 ,<br />

aeration 10 dm 3 min –1 , pH adjusted on value 6.5, medium<br />

temperature 60 °C, vessel isolation Mirelon. The batch was<br />

selected as the cultivation method. The cultivation time was<br />

66 h (1 st experiments) and 312 h (2 nd experiments). The process<br />

characteristics were determined direct by fermentor system<br />

(dissolved oxygen concentration) or by the help of samples<br />

taking and their analyses (biomass – turbidimeter, COD<br />

– spectrofotometer at 600 nm, lactose – HPLC after microfiltration,<br />

100 % lactose ≈ 46 g.dm –3 . The statistical analyse<br />

was realized in the relevancy level 0.05.<br />

Results<br />

The experimental results are summarized in Fig. 1. & 2.<br />

Fig. 2. batch cultivation progress in shorter time (66 hours)<br />

•<br />

•<br />

•<br />

•<br />

•<br />

•<br />

Hence it follows:<br />

Lactose was not used as primary substrate source<br />

(Fig. 2.), consequently the exponential growth<br />

phase in time 3–43 hours (specific growth rate<br />

µ = 0.05 ± 0.01 h –1 ) is a result of simpler whey compound<br />

utilization probably, for example lactate.<br />

Lactose metabolisation was combined with the 2 nd<br />

growth phase in time 120–260 hours (specific growth<br />

rate µ = 0.010 ± 0.006 h –1 ) (Fig. 1.).<br />

The biomass accrument was very slow. It was probably<br />

an inhibition effect of concentrated substrate, especially<br />

in the 1 st cultivation period (Fig. 1., Fig 2.). Total biomass<br />

concentration after 312 hours: (<strong>3.</strong>3 ± 0.3) g dm –3 at<br />

productivity 0.01 g.dm –3 h –1 .<br />

The oxygen limitation can contibute to slow biomass<br />

growth (primarily in the 1 st growth phase).<br />

Maximum COD elimination was in the 1 st half of every<br />

exponetial growth phase: 15 ± 3 % after the 1 st growth<br />

phase and ± 4 % after the 2 nd growth phase.<br />

The oxygen transfer coefficient was determined too,<br />

k L a = (270 ± 21) h –1 .

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