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The difference between economic and mass allocations of straw production is presented in Fig. 5 as in our case straw is not used as fodder, but for energy applications.
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When treating fly ash impacts, three allocation procedures were compared: 'no allocation', economic, and mass allocation, with mass allocation giving unreasonably high impacts of fly ash.
The mass allocation factor is the mass ratio of grain to straw, which is 2 3.
A superstructure is presented to define the interactions between mass allocation and heat exchanger networks.
Results vary significantly for Ru/C, depending on whether economic or mass allocation methods are used.
The energy consumptions were reported by mass allocation as 143 MJ/kg-DMC.
This paper presents a mixed-integer linear programming model to design mass allocation and heat exchanger networks simultaneously.
The methodology can be very helpful for sequential or simultaneous models designing mass allocation and heat exchangers networks.
Perfluorotributylamine spectra were collected and averaged contiguously for a period of 48 h with no significant signal loss or peak mass allocation shift.
Life cycle GHGs for Ru/C are estimated at 80.4 kg CO2-e/kg catalyst using economic allocation and 13.7 kg CO2-e/kg catalyst using mass allocation.
Open image in new window Fig. 5 Sensitivity analysis when mass allocation is used in the cultivation stage of straw-based systems (in ecoinvent database), normalized results.
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