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Can an Electronic Nose Assess the Biomethanation Process?

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E-nose was able to:

1. Detect overload of the system

2. Suggest disturbed digestion and

recovery time of the batches to

return to a stable digestion

Gilles ADAM* and Jacques NICOLAS

Environmental Sciences and Management Department, University of Liège Avenue de Longwy 185, 6700 Arlon, Belgium

*Gilles.Adam@doct.ulg.ac.be

Conclusions

Material and methods

Objective

E-nose Concept

Also called gas sensor array, an e-nose employs various

complementary gas sensors, in order to improve selectivity. Anaerobic digestion technology is a trendy solution for a more sustainable world. It produces biogas, a mixture of methane and carbon dioxide used in combined heat and power unit to produce renewable

energy.

This technology is now adapted in farm plants in Belgium. Because of the diversity of substrates and sensitivity of the anaerobic digestion

process to overload, most of the reactors are under-loaded to avoid

process disturbance, resulting in lower gas yield.

E-nose technology offers the possibility of a new robust, simple,

sensitive and low cost tool for biogas production monitoring in order

to optimize the process and increase gas yield in small scale agricultural plants.

System of anaerobic batches

Future trends

Electronic nose demonstrated its potential in biomethanation process monitoring. The tool was able to discriminate

overload situations. Nowadays, anaerobic digestion control is only able using high-tech analysis, such as VFA

determination by GC-MS or HPLC. Results of these analyses are expensive and available one week after sampling.

E-nose allows to avoid this delay by on-line control but it needs to be tested in conditions closer to the real situation.

Batches Biogas collection

Insulated box

Temperature regulated at 38 ± 1°C Three load strategies :

1. Control : 1 g sucrose batch-1.day-1 2. Slow load increase : 1 to 5 g

sucrose batch-1.day-1

3. Punctual overloads : 1 g sucrose batch-1.day-1 and one punctual

overload a week of 3, 9 and 12 g sucrose batch-1.

Experiment duration : 3 weeks Sample in

-3 -2 -1 0 1 2 3 FACTOR 1 (62%) -3 -2 -1 0 1 2 3 F A C T O R 2 ( 3 3 % ) Control

Slow load increase Puntual overload Overload area Stable digestion

Measured variables

Daily analyses : Chemical analysis

-COV composition and concentration (GC-MS1)

-[CH4] and [CO2] (IR2 sensors) -[H2S], [CO] (EC3 gas sensors)

Principal component analysis of the e-nose normalized data (6 variables, 83 observations) Twelve anaerobic batches of 1.5 L in are put in an insulated

thermostatic bath. Batches were inoculated with sludge (5% TS)

from the wastewater treatment station of Schifflange (Luxembourg).

Results and discussion

95% of the variance explained

Two groups of data detected:

-overload area

> 4 g sucrose.day-1

-stable digestion

< 4 g sucrose.day-1 Intermediate situation observed in the punctual overload data set:

-Days following the overload

  

 Recovery process detected

Can an electronic nose assess the biomethanation process?

Gas footprint Gas sensor array Biogas S3 S2 S1 S4 S5 Good process Disturbed process Unstable process Data base Pattern recognition Good process Response 1 2 3 4 5 6 7 8 9 10 11 13 14 1 2 3 4 5 6 7 8 9 10 11 12 13 14 -3 -2 -1 0 1 2 3 Factor 1 (62%) -3 -2 -1 0 1 2 3 F a c to r 2 ( 3 3 % ) 1 2 3 4 5 6 7 8 9 10 11 13 14 1 2 3 4 5 6 7 8 9 10 11 12 13 14 Batch 1 Batch 2

Numbers represents the days numbers after inoculating the batches

Overload schedule: day 4, 9 and 13( respectively 3, 9 and 12 g sucrose batch-1

Stable digestion area

Area of digestion in recovery process

Overload area

Electronic nose analysis

6 TGS sensors (tin oxide sensors) Sensors chamber regulated at 50°C

Dilution rate of biogas : 25x in air (10% RH at 37°C). Biogas input of 9 minutes.

1Gas chromatography – Mass Spectrometry (GC-MS)

2Infrared (IR)

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