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23/05/2017 EmiLi 2017
Gaseous emissions of 3 solid manure
heap treatments :
control, covered, covered&compacted
at storage
Lorinquer, E., Charpiot, A., Robin, P., Lecomte, M.
1
Partners
Financial support
CONTEXT
223/05/2017 EmiLi
Livestock manure : ~ 65% NH3 national emissions (CITEPA, 2014)
Cattle ~ 50%
FR 4,2 t milk / ha
• High diversity production
system (feeding, housing,
manure management)
• 80 % of french livestock
manure are solid manure
with 69 million tons/year
• Few references concerning
farm yard manure gaz
emissions
PROJECT OBJECTIVES
323/05/2017 EmiLi
1. Measure gas emissions of solid manure at storage in 3 different management
ways
Compacted and coveredControl = field storage Covered
2. Lab emissions measurements
3. Simplified (spotted) method to measure
gas emissions coupled with a model
Focus on this part
MATERIAL & METHODS
Product studied :
- Solid manure from deep litter dairy
barn
- ~ 70 dairy cows fed mainly at winter
time with maize and grass silage
- ~5tons of solid manure per heaps
423/05/2017 EmiLi
3 weeks accumulation Storage : 11 weeksStorage : 11 weeks
21/01/13 13/02/13 24/04/13
Spreading
Sequence of events :
Heaps characteristics
• Weight, manure sampling,
heaps shape & volume at the
start and end of storage
MATERIAL & METHODS
Climate parameters :
- Humidity, rainfall, temperatures
- Inside heaps temperatures (at 3 different heights -
thermocouple & central data acquisition – Campbell)
- Weighting and sampling all leachates from heap every week
Gas emissions :
- Method : Wind tunnel
- Frequency : Covered during first 5 days after starting storage and once a
week for 24h during all storage period
- Ventilation : Mechanical exhaust air (FANCOM)
- Concentration gas : H2O, CO2, NH3, CH4, N2O with INNOVA 1412
RESULTS
623/05/2017 EmiLi
leachate
Rainfall
Gas
Control Coveref
Cov.
Comp.
Ntot_leach(%i) 0,7 0,6 0,7
Control Coveref
Cov.
Comp.
%i %i %i
N-NH3 12 7 4
N-N2O 0,1 0,08 0,2
N-N2 24 28 4
C-CH4 0,4 0,3 3
C-CO2 41 26 27
2.1 Mass losses
Mass losses are less
important for control heap
due to higher exposure with
rainfall (not cover)
2.2 Leachates losses
N loss related to
leaching <1% initial
total N
2.3 Gas losses
1- N gases
NH3 : <12% initial total nitrogen – effect
compaction on NH3 emissions
N2O : < 0,2% initial total nitrogen
N2 : major emission
2- C gases
CH4: times 10 when compacted
RESULTS
723/05/2017 EmiLi
2.3 Gas losses : kinetics emissions
NH3 CH4
Almost all emissions occured following the first month after storage
Light differences between different treatment regarding NH3 emissions, but still <6%
of initial total nitrogen
Week month
Cont
.
Cov.. C&C.
CONCLUSION
• NH3 losses < 12 % initial N
• Solid manure from deep litter system : heterogeneous
manure, sampling and characterization is hard
• Need to look at the french diversity of solid manure
• Look at transfer pollutants on the whole manure
management chain
23/05/2017 EmiLi 8
23/05/2017 EmiLi 2017
Thanks for your
attention !
elise.lorinquer@idele.fr
9

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EMAFUM-stockage fumier et émissions _EmiLi2017_24/05/17

  • 1. 23/05/2017 EmiLi 2017 Gaseous emissions of 3 solid manure heap treatments : control, covered, covered&compacted at storage Lorinquer, E., Charpiot, A., Robin, P., Lecomte, M. 1 Partners Financial support
  • 2. CONTEXT 223/05/2017 EmiLi Livestock manure : ~ 65% NH3 national emissions (CITEPA, 2014) Cattle ~ 50% FR 4,2 t milk / ha • High diversity production system (feeding, housing, manure management) • 80 % of french livestock manure are solid manure with 69 million tons/year • Few references concerning farm yard manure gaz emissions
  • 3. PROJECT OBJECTIVES 323/05/2017 EmiLi 1. Measure gas emissions of solid manure at storage in 3 different management ways Compacted and coveredControl = field storage Covered 2. Lab emissions measurements 3. Simplified (spotted) method to measure gas emissions coupled with a model Focus on this part
  • 4. MATERIAL & METHODS Product studied : - Solid manure from deep litter dairy barn - ~ 70 dairy cows fed mainly at winter time with maize and grass silage - ~5tons of solid manure per heaps 423/05/2017 EmiLi 3 weeks accumulation Storage : 11 weeksStorage : 11 weeks 21/01/13 13/02/13 24/04/13 Spreading Sequence of events : Heaps characteristics • Weight, manure sampling, heaps shape & volume at the start and end of storage
  • 5. MATERIAL & METHODS Climate parameters : - Humidity, rainfall, temperatures - Inside heaps temperatures (at 3 different heights - thermocouple & central data acquisition – Campbell) - Weighting and sampling all leachates from heap every week Gas emissions : - Method : Wind tunnel - Frequency : Covered during first 5 days after starting storage and once a week for 24h during all storage period - Ventilation : Mechanical exhaust air (FANCOM) - Concentration gas : H2O, CO2, NH3, CH4, N2O with INNOVA 1412
  • 6. RESULTS 623/05/2017 EmiLi leachate Rainfall Gas Control Coveref Cov. Comp. Ntot_leach(%i) 0,7 0,6 0,7 Control Coveref Cov. Comp. %i %i %i N-NH3 12 7 4 N-N2O 0,1 0,08 0,2 N-N2 24 28 4 C-CH4 0,4 0,3 3 C-CO2 41 26 27 2.1 Mass losses Mass losses are less important for control heap due to higher exposure with rainfall (not cover) 2.2 Leachates losses N loss related to leaching <1% initial total N 2.3 Gas losses 1- N gases NH3 : <12% initial total nitrogen – effect compaction on NH3 emissions N2O : < 0,2% initial total nitrogen N2 : major emission 2- C gases CH4: times 10 when compacted
  • 7. RESULTS 723/05/2017 EmiLi 2.3 Gas losses : kinetics emissions NH3 CH4 Almost all emissions occured following the first month after storage Light differences between different treatment regarding NH3 emissions, but still <6% of initial total nitrogen Week month Cont . Cov.. C&C.
  • 8. CONCLUSION • NH3 losses < 12 % initial N • Solid manure from deep litter system : heterogeneous manure, sampling and characterization is hard • Need to look at the french diversity of solid manure • Look at transfer pollutants on the whole manure management chain 23/05/2017 EmiLi 8
  • 9. 23/05/2017 EmiLi 2017 Thanks for your attention ! elise.lorinquer@idele.fr 9