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2772-68-1

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2772-68-1 Usage

Check Digit Verification of cas no

The CAS Registry Mumber 2772-68-1 includes 7 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 4 digits, 2,7,7 and 2 respectively; the second part has 2 digits, 6 and 8 respectively.
Calculate Digit Verification of CAS Registry Number 2772-68:
(6*2)+(5*7)+(4*7)+(3*2)+(2*6)+(1*8)=101
101 % 10 = 1
So 2772-68-1 is a valid CAS Registry Number.

2772-68-1SDS

SAFETY DATA SHEETS

According to Globally Harmonized System of Classification and Labelling of Chemicals (GHS) - Sixth revised edition

Version: 1.0

Creation Date: Aug 16, 2017

Revision Date: Aug 16, 2017

1.Identification

1.1 GHS Product identifier

Product name [14-C]-methane

1.2 Other means of identification

Product number -
Other names Methan-C14

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only.
Uses advised against no data available

1.4 Supplier's details

1.5 Emergency phone number

Emergency phone number -
Service hours Monday to Friday, 9am-5pm (Standard time zone: UTC/GMT +8 hours).

More Details:2772-68-1 SDS

2772-68-1Upstream product

2772-68-1Downstream Products

2772-68-1Relevant articles and documents

Turnover of propionate in methanogenic paddy soil

Krylova, Nailia I.,Janssen, Peter H.,Conrad, Ralf

, p. 107 - 117 (1997)

Samples from planted Italian paddy soil exhibited most probable numbers (MPN) of about 107 anaerobic propionate utilizers. In anoxic soil slurries that were either unamended or amended with rice straw production of CH4 was measured together with concentrations of H2, acetate and propionate. After a lag phase, during which ferric iron was depleted, CH4 was produced at a constant rate which was slightly higher in the straw-amended than in the unamended soil. Propionate concentrations were relatively low at about 5-15 μM. However, in the straw-amended soil propionate transiently accumulated to about 35 μM just after onset of methanogenesis. During the period of propionate accumulation H2 partial pressures were elevated and the Gibbs free energy (ΔG) of propionate consumption to acetate, bicarbonate and H2 was endergonic or higher than -3 kJ mol-1 propionate. Propionate concentrations decreased again when the ΔG decreased to more negative values. In unamended paddy soil, propionate did not accumulate transiently and ΔG was always -1 propionate. Propionate radiolabelled in the C-1 or C-2 position was utilized with turnover times of 30-60 min. Propionate turnover rates approximately accounted for the rates of H2/CO2- dependent methanogenesis that were measured in experiments with [14C]bicarbonate. The only radioactive product of [1-14C]propionate was 14CO2. However, [2-14C]propionate was converted to radioactive acetate. CO2 and CH4. This observation indicates that propionate was consumed via a randomizing pathway to CO2 and acetate, the latter being then further degraded by acetotrophic methanogens to CO2 and CH4. Turnover of [1- 14C]propionate was almost completely inhibited by high H2 concentrations, chloroform or molybdate. The MPN of bacteria that utilized propionate either in syntrophy with methanogens or by reduction of sulfate was identical. All these observations suggest thai propionate was consumed by a syntrophic randomizing pathway, probably by bacteria that have also the capacity to reduce sulfate.

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Yang,Wolf

, p. 4488,4489 (1960)

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