scholarly journals The effect of oxygen on fermentation of sucrose by rumen micro-organisms in vitro

1969 ◽  
Vol 23 (1) ◽  
pp. 67-80 ◽  
Author(s):  
J. W. Czerkawski ◽  
Grace Breckenridge

1. The effect of oxygen on the fermentation of sucrose by mixed rumen micro-organisms in vitro was studied by adding oxygen to the gas phase in three ways: at the beginning of incubation, at two hourly intervals during incubation and continuously.2. The additions of oxygen had no measurable effect on the utilization of sucrose or on the production of carbon dioxide, steam-volatile acids and particulate organic matter by the micro-organisms. The addition of oxygen at the beginning of incubation inhibited methane production and increased the accumulation of hydrogen. Similar but much less pronounced changes occurred when the oxygen was infused continuously.3. In all the experiments there was a net uptake of oxygen by micro-organisms. When large amounts of oxygen were present in the gas phase the rates of uptake were proportional to these amounts. When small amounts of oxygen were added, the rates of uptake were independent of the amount added and had a value of approximately 5 ml/h when 100 ml of strained rumen contents were incubated.

1933 ◽  
Vol 8 (4) ◽  
pp. 375-389 ◽  
Author(s):  
P. H. H. Gray ◽  
N. B. McMaster

Microbiological studies of samples from the separate horizons and from different depths of soils of the Appalachian upland podsol group show that the activity of the micro-organisms is dependent upon the organic-matter relations in the horizons. The organic-matter horizon is biologically the most active, as shown by analyses for carbon dioxide, nitrate nitrogen, numbers of bacteria, and production of ammonia from urea. Evidence is submitted that the reduced activity of the leached layer and the horizons of accumulation is not due to toxic compounds produced by leaching of the organic matter.


1929 ◽  
Vol 19 (4) ◽  
pp. 627-648 ◽  
Author(s):  
V. Subrahmanyan

(1) In absence of decomposing organic matter addition of nitrate led to no loss of nitrogen.(2) On addition of small quantities of fermentable matter such as glucose there was (a) rapid depletion of nitrates and oxygen, but no denitrification, and (b) increase in acidity, carbon dioxide and bacteria. The greater part of the soluble nitrogen was assimilated by microorganisms or otherwise converted and the greater part of the added carbohydrate was transformed into lactic, acetic and butyric acids.(3) The organic acids were formed from a variety of carbohydrates. Lactic acid was the first to be observed and appeared to be formed mainly by direct splitting of the sugar. It decomposed readily, forming acetic and butyric acids. Some acetic acid was formed by direct oxidation of lactic acid, with pyruvic acid as the intermediate product. All the acids were, on standing, converted into other forms by micro-organisms.


1998 ◽  
Vol 1998 ◽  
pp. 60-60
Author(s):  
U.R. Altaf ◽  
R. Mauricio ◽  
F.L. Mould ◽  
T. Smith ◽  
E. Owen ◽  
...  

A previous study (Mauricio et al., 1998) with 12 forage substrates (straw, hay and dried grasses) showed a high correlation between rumen liquor and faeces for total gas production and in vitro organic matter digestibility (OMD). However parameters estimated using faecal inoculum were generally lower man when using rumen liquor. To confirm this observation, a second study was conducted using maize silage and silages made from maize plant fractions.


1973 ◽  
Vol 17 (3) ◽  
pp. 329-332 ◽  
Author(s):  
D. G. Edwards ◽  
I. F. Duthie ◽  
Barbara M. Rogers ◽  
Emyr Owen

SUMMARYThe digestibility of a feed containing hull material prepared mechanically from Throws MS field bean (Viciafaba L) was determined in a 12-day balance trial with sheep. The pelleted feed contained 62 % hulls and 38 % of a concentrate mixture, and was given at a maintenance level. The mean digestibility coefficients of the feed were for dry matter, 66·3; organic matter, 68·2; nitrogen, 65·7; crude fibre, 59·4; and energy, 65·5%.The coefficients for the bean hulls themselves, estimated by assuming coefficients for the concentrates, were dry matter, 59·6; organic matter, 61·0; nitrogen, 58·2; crude fibre, 60·3; and energy, 59·9%. By assuming a value of 2·515 Mcal/kg for the metabolizable energy of the concentrates, the metabolizable energy of the bean hulls was calculated to be between 2·00 and 2·10 Mcal/kg.Digestibility coefficients for the bean hulls determined in vitro were found to agree with those determined in vivo.


2000 ◽  
Vol 27 (4) ◽  
pp. 814-828 ◽  
Author(s):  
L Bibeau ◽  
G Viel ◽  
M Heitz

The problem related to air discharge contaminated with volatile organic solvents (VOS) is the scope of numerous researches. Throughout the last decades, the development of different types of bioreactors to treat atmospheric emissions contaminated with VOS has been observed, such as: the bioscrubber, the percolating filter and the biofilter. These bioreactors are processes that use microorganisms in order to degrade the VOS into carbon dioxide, water, and biomass. This paper presents the results of a study on degradation by biofiltration of xylene contained in air, with a new filtering bed composed of cellulose. We have studied the conversion, the capacity of elimination of xylene with respect to the inlet load and the production of carbon dioxide. An elimination capacity of 75 g·m-3·h-1 for an inlet con centration to the biofilter of 1.7 g·m-3 of xylene has been obtained, which is a value that is superior to values mentioned in the literature. Measurements of temperature, pressure drop, and moisture content have been taken regularly so as to evaluate the influence of these parameters in the degradation process of xylene by microorganisms. Counts of bacteria and yeast/mould present in the filtering bed have been performed in order to follow the evolution of these micro organisms. At last, modeling based on the Ottengraf's model (1986) has been developed with the experimental data.Key words: treatment, air, biofiltration, xylenes, cellulose, volatile organic solvents.


1998 ◽  
Vol 1998 ◽  
pp. 60-60 ◽  
Author(s):  
U.R. Altaf ◽  
R. Mauricio ◽  
F.L. Mould ◽  
T. Smith ◽  
E. Owen ◽  
...  

A previous study (Mauricioet al., 1998) with 12 forage substrates (straw, hay and dried grasses) showed a high correlation between rumen liquor and faeces for total gas production andin vitroorganic matter digestibility (OMD). However parameters estimated using faecal inoculum were generally lower man when using rumen liquor. To confirm this observation, a second study was conducted using maize silage and silages made from maize plant fractions.


1998 ◽  
Vol 22 ◽  
pp. 89-91 ◽  
Author(s):  
C. Rymer ◽  
A. R. Moss ◽  
E. R. Deaville ◽  
D. I. Givens

When a food is ingested by a ruminant animal, the carbohydrate fraction of the food is fermented by the rumen micro-organisms to produce gas (predominantly carbon dioxide and methane) as well as volatile fatty acids (VFA). The gas production technique simulates this fermentation process and provides an estimate of both the rate and extent of fermentation. Comparing the gas production (GP) profiles of foods enables a comparison to be made of the fermentative characteristics of different foods. However, the technique uses a bicarbonate-based medium system with the rumen liquor. This complicates the GP profile because of the production of ‘indirect’ gas resulting from the reaction between the VFA and the bicarbonate ions.Beuvink and Spoelstra (1992) measured the volume of gas produced from buffered rumen fluid when known amounts of VFA were added and observed that 20·8 ml gas were released per mmol VFA. However, there is variation between laboratories in terms of the composition of the medium that is used. Even when the same medium is used, significant differences have been observed in the GP profile when different types of apparatus were employed (Rymer and Givens, 1997). Media are gassed with carbon dioxide before they are added to the gas production system and it is possible that the concentration of carbon dioxide dissolved in the medium varies between experiments. The objective of this experiment, therefore, was to determine whether the volume of indirect gas produced was affected by the composition of the medium, the addition of carbon dioxide, and the technique employed to measure gas production.


1935 ◽  
Vol 13c (4) ◽  
pp. 251-255 ◽  
Author(s):  
P. H. H. Gray ◽  
C. B. Taylor

Microbiological studies of samples from the separate horizons of two soils from the Laurentian uplands showed that, as in the case of the soils previously studied from the Appalachian uplands, biological activity was dependent upon the organic-matter relations of the horizons. A1 (organic-matter) horizons were the most active, as shown by the evolution of carbon dioxide, nitrification of the soil's own nitrogen, by numbers of micro-organisms (bacteria, actinomyces, and fungi) and by the production of ammonia from urea. Bacterial numbers in the illuvial horizons were, however, higher than in the eluvial (leached) horizons above, a condition that did not obtain with the Appalachian soils. The organic matter of a soil bearing a coniferous (spruce) flora was deficient in nitrifying power. The biological activity at different levels of a virgin clay soil was found to be in sharp contrast with that of the podsol soils.


Author(s):  
Ivan Petric

Laboratory-scale aerobic composting tests with mixture of poultry manure and wheat straw were conducted in closed thermally insulated column reactors with effective volumes of 1 L and 32 L. Two 14-day experiments with two different mixture ratios (manure to straw, 2.77:1 and 5.25:1 on dry weight, respectively) were performed in order to compare the performances of composting process in both reactors as well to obtain the parameter values in the kinetic model and to validate proposed kinetic and reactor model in this work. The maximum temperature of 64.6°C was reached after 2.1 days in the large reactor and 64.5°C after 1.3 days in the small reactor. The temperature in these reactors was maintained above 55°C for 2 days, which should be sufficient to maximize sanitation and to destroy pathogens. The greatest mass of carbon dioxide was generated during the first 3 days. The maximum consumption of oxygen was noticed in the exit gas mixtures from both reactors after the first day of the process (the small reactor 16.0 vol. %, the large reactor 11.7 vol. %). The maximum emission of ammonia was observed from the small reactor after first day and from large reactor after the third day. The organic matter content of the materials decreased in both reactors during the process, but this reduction was greater in the large reactor (47.60%) than in the small reactor (41.36%). The proposed kinetic and reactor model was described by a differential equation set with 12 dynamic state variables: mass of organic matter, mass of oxygen, mass of dissolved carbon dioxide, mass of dissolved ammonia, mass of water in the substrate, molar amount of O2 (gas phase), molar amount of CO2 (gas phase), molar amount of NH3 (gas phase), molar amount of H2O vapour (gas phase), molar amount of N2 (gas phase), temperature of gas phase, temperature of solid-liquid phase. In the proposed kinetic model, four kinetic parameters were calculated. The model was validated by the results of several experimentally measured dynamic state variables (temperature of substrate, conversion of organic matter conversion, concentration of carbon dioxide, concentration of oxygen). Comparisons of experimental and simulation results showed good agreement during the whole duration of the process in a reactor, except for ammonia (good agreement was achieved for the first four days and for the last three days of the process). Different simulation scenarios were performed with the model in order to study the effects of initial moisture content, airflow rates and air temperature on the substrate temperature and organic matter conversion. A sensitivity analysis showed that two of four kinetic parameters had a great influence on all three objective functions (maximum conversion of organic matter, maximum concentration of carbon dioxide and maximum substrate temperature).


Agronomie ◽  
2002 ◽  
Vol 22 (7-8) ◽  
pp. 777-787 ◽  
Author(s):  
Graeme D. Schwenke ◽  
Warwick L. Felton ◽  
David F. Herridge ◽  
Dil F. Khan ◽  
Mark B. Peoples

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