TY - JOUR
T1 - Mitigating the environmental impacts of milk production via anaerobic
digestion of manure: Case study of a dairy farm in the Po Valley
AU - Battini, F.
AU - Agostini, A.
AU - Boulamanti, A. K.
AU - Giuntoli, J.
AU - Amaducci, Stefano
PY - 2014
Y1 - 2014
N2 - This work analyzes the environmental impacts ofmilk production inan intensivedairyfarmsituated in theNorthern
Italy region of the Po Valley. Three manure management scenarios are compared: in Scenario 1 the animal slurry is
stored in an open tank and then used as fertilizer. In scenario 2 the manure is processed in an anaerobic digestion
plant and the biogas produced is combusted in an internal combustion engine to produce heat (required by the digester)
and electricity (exported). Scenario 3 is similar to scenario 2 but the digestate is stored in a gas-tight tank.
In scenario 1 the GHG emissions are estimated to be equal to 1.21 kg CO2 eq. kg−1 Fat and Protein Corrected Milk
(FPCM) without allocation of the environmental burden to the by-product meat.With mass allocation, the GHG
emissions associated to the milk are reduced to 1.18 kg CO2 eq. kg−1 FPCM. Using an economic allocation approach
the GHG emissions allocated to the milk are 1.13 kg CO2 eq. kg−1 FPCM. In scenarios 2 and 3, without allocation,
theGHGemissions are reduced respectively to 0.92 (−23.7%) and 0.77 (−36.5%) kg CO2 eq. kg−1 FPCM.
If land use change due to soybean production is accounted for, an additionalemission of 0.53 kg CO2 eq. should be
added, raising the GHG emissions to 1.74, 1.45 and 1.30 kg CO2 eq kg−1 FPCMin scenarios 1, 2 and 3, respectively.
Primary energy from non-renewable resources decreases by 36.2% and 40.6% in scenarios 2 and 3, respectively,
with the valorization of the manure in the biogas plant.
The other environmental impact mitigated is marine eutrophication that decreases by 8.1% in both scenarios 2
and 3, mostly because of the lower field emissions.
There is, however, a trade-off between non-renewable energy and GHG savings and other environmental impacts:
acidification (+6.1% and +5.5% in scenarios 2 and 3, respectively), particulate matter emissions (+1.4% and
+0.7%) and photochemical ozone formation potential (+41.6% and+42.3%) increase with the adoption of a biogas
plant.The causeof the increase ismostlyemissions fromtheCHPengine.These impacts canbe tackledbyimproving
biogas combustion technologies to reducemethane andNOx emissions. Freshwater eutrophication slightly increases
(+0.8% in both scenarios 2 and 3) because of the additional infrastructures needed.
In conclusion, on-farm manure anaerobic digestion with the production of electricity is an effective technology to
significantly reduce global environmental impacts of dairy farms (GHG emissions and non-renewable energy consumption),
however local impacts may increase as a consequence (especially photochemical ozone formation).
AB - This work analyzes the environmental impacts ofmilk production inan intensivedairyfarmsituated in theNorthern
Italy region of the Po Valley. Three manure management scenarios are compared: in Scenario 1 the animal slurry is
stored in an open tank and then used as fertilizer. In scenario 2 the manure is processed in an anaerobic digestion
plant and the biogas produced is combusted in an internal combustion engine to produce heat (required by the digester)
and electricity (exported). Scenario 3 is similar to scenario 2 but the digestate is stored in a gas-tight tank.
In scenario 1 the GHG emissions are estimated to be equal to 1.21 kg CO2 eq. kg−1 Fat and Protein Corrected Milk
(FPCM) without allocation of the environmental burden to the by-product meat.With mass allocation, the GHG
emissions associated to the milk are reduced to 1.18 kg CO2 eq. kg−1 FPCM. Using an economic allocation approach
the GHG emissions allocated to the milk are 1.13 kg CO2 eq. kg−1 FPCM. In scenarios 2 and 3, without allocation,
theGHGemissions are reduced respectively to 0.92 (−23.7%) and 0.77 (−36.5%) kg CO2 eq. kg−1 FPCM.
If land use change due to soybean production is accounted for, an additionalemission of 0.53 kg CO2 eq. should be
added, raising the GHG emissions to 1.74, 1.45 and 1.30 kg CO2 eq kg−1 FPCMin scenarios 1, 2 and 3, respectively.
Primary energy from non-renewable resources decreases by 36.2% and 40.6% in scenarios 2 and 3, respectively,
with the valorization of the manure in the biogas plant.
The other environmental impact mitigated is marine eutrophication that decreases by 8.1% in both scenarios 2
and 3, mostly because of the lower field emissions.
There is, however, a trade-off between non-renewable energy and GHG savings and other environmental impacts:
acidification (+6.1% and +5.5% in scenarios 2 and 3, respectively), particulate matter emissions (+1.4% and
+0.7%) and photochemical ozone formation potential (+41.6% and+42.3%) increase with the adoption of a biogas
plant.The causeof the increase ismostlyemissions fromtheCHPengine.These impacts canbe tackledbyimproving
biogas combustion technologies to reducemethane andNOx emissions. Freshwater eutrophication slightly increases
(+0.8% in both scenarios 2 and 3) because of the additional infrastructures needed.
In conclusion, on-farm manure anaerobic digestion with the production of electricity is an effective technology to
significantly reduce global environmental impacts of dairy farms (GHG emissions and non-renewable energy consumption),
however local impacts may increase as a consequence (especially photochemical ozone formation).
KW - Biogas
KW - Dairy farm
KW - Greenhouse gas
KW - Life cycle assessment
KW - Biogas
KW - Dairy farm
KW - Greenhouse gas
KW - Life cycle assessment
UR - http://hdl.handle.net/10807/54595
U2 - 10.1016/j.scitotenv.2014.02.038
DO - 10.1016/j.scitotenv.2014.02.038
M3 - Article
SN - 0048-9697
SP - 196
EP - 208
JO - Science of the Total Environment
JF - Science of the Total Environment
ER -