The CO2 aquifer storage potential was estimated as totally 146 Gt- CO2 in Japan.
For a given capacity of a wind power project the CO2 emissions mitigation potential can be estimated as: G C E w i n d = ( 8760 P L F w i n d P w i n d ) C E F e (6).
In this model, the power and energy potential can be estimated as follows: E_{text{p}} = {text{HV}} times W times 0.0011628 (5) P_{text{gp}} = E_{text{p}} / 2 4, (6 where E p energy potential (kWh), P gp power generation potential (kW), HV calorific value of the waste (kcal/kg), W weight of the waste (kg).
For a given capacity of a wind power project the CO2 emissions mitigation potential can be estimated as: GCE wind = (8760 PLF wind P wind ) CEF e where Pwind (in MW) represents the capacity of wind power project, PLFwind (in fraction) the plant load factor of the wind power project, CEFe the CO2 emission factor of electricity.
The effect of intervention was estimated as a potential impact fraction (PIF), following Cobiac et al. [ 20].
We used two measures to characterize dietary acid load: (1) NEAP estimated as the dietary potential renal acid load plus organic acid excretion, the latter as a multiple of estimated body surface area; and (2) estimated NEAP based on protein and K.
Potential microbial respiration, estimated as the laboratory C mineralization potential, was about an order of magnitude lower than measured root respiration in both the soil and shale fractures.
Acute dermal exposures from deposition of spray drift on skin were estimated as where PE is potential exposure (milligrams per kilogram bw), TDE is total dermal exposure (milligrams), AB is dermal absorption rate, and bw is body weight (kilograms).
The results indicated that 66.4% of the observations were estimated as rear-end crash potentials.
Water potential gradient was estimated as the difference between pre-dawn and midday leaf water potential.
