Operation, truck 60t, fleet average {AU}| | AusLCI, U
Unit process Australia v00.00.000
Included processes: Fuel production and combustion in vehicle. Remark: This process is for 1 km of vehicle travel scale back to 1 MJ of fuel for simplicity of calculating emission factors. Geography: Refers to an average production in the Australia. Technology: Average Time period: Data collected for 2020 Version: 1.0 Record: Data entry by: Tim Grant Telephone: 0061 408104977; E-mail: tim@lifecycles.com.au; Company: LCS; Country: AU Generator: Data entry by: Tim Grant Telephone: 0061 408104977; E-mail: tim@lifecycles.com.au; Company: LCS; Country: AU
- Sector
- Transport
- Contributor
- —
- Last updated
- 07 Jul 2013
- Reference ID
5637099c-4656-3172-8cfc-98b7ef5b6aba
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Documentation
- Quantitative reference
- Operation, truck 60t, fleet average {AU}| | AusLCI, U
- Sampling procedure
- —
- Creation date
- 07 Jul 2013
- Is copyright protected
- No
- Is infrastructure process
- No
- Tags
- transport
- Sources
-
National greenhouse gas inventory 2002 : with methodology supplements/2004/Austr
National Greenhouse Accounts Factors/2013/Department of Industry Innovation
Product outputs
| Flow | Amount | Unit | Comment |
|---|---|---|---|
| Operation, truck 60t, fleet average {AU}| | AusLCI, U | 0.048591272914089385 | km | Kilometers travelled on 1 MJ of fuel - Fuel use in kg for 1 MJ/ Fuel use in kg for 1km. |
Technical inputs
| Flow | Amount | Unit | Comment |
|---|---|---|---|
| Diesel {RoW}| market for diesel | Cut-off, U | 0.021929824561403508 | kg | Based on 1.MJ (lower heating value) of fuel input to engine |
Outputs to treatment
| Flow | Amount | Unit | Comment |
|---|---|---|---|
| Brake wear emissions, lorry {GLO}| market for brake wear emissions, lorry | Cut-off, U | 0.0002435748 | kg | (2,2,2,4,1,na) Road freight specific non-exhaust emissions. This dataset and the emission factors within it relate to 1kg of brake wear. In order to use the treatment of non-exhaust emissions in a transport dataset the quantity of emissions per km must be calculated. Non-exhaust emissions are considered to be linearly scalable to gross vehicle weight (GVW). For brake wear emissions from lorries the specific quantity is 8.13E-9 kg/kg GVW*km. The GVW of the >32t lorries using an average load factor is 29 960kg. The value calculated must then be devided by the average load to give the non-exhaust emissions per tkm. |
| Road wear emissions, lorry {GLO}| market for road wear emissions, lorry | Cut-off, U | 0.00020972 | kg | (2,2,2,4,1,na) Road freight specific non-exhaust emissions. This dataset and the emission factors within it relate to 1kg of road wear. In order to use the treatment of non-exhaust emissions in a transport dataset the quantity of emissions per km must be calculated. Non-exhaust emissions are considered to be linearly scalable to gross vehicle weight (GVW). For road wear emissions from lorries the specific quantity is 7.0e-9 kg/kg GVW*km. The GVW of the >32t lorries using an average load factor is 29 960kg. The value calculated must then be devided by the average load to give the non-exhaust emissions per tkm. |
| Tyre wear emissions, lorry {GLO}| market for tyre wear emissions, lorry | Cut-off, U | 0.002413278 | kg | (2,2,2,4,1,na) Road freight specific non-exhaust emissions. This dataset and the emission factors within it relate to 1kg of tyre wear. In order to use the treatment of non-exhaust emissions in a transport dataset the quantity of emissions per km must be calculated. Non-exhaust emissions are considered to be linearly scalable to gross vehicle weight (GVW). For tyre wear emissions from lorries the specific quantity is 8.055E-8 kg/kg GVW*km. The GVW of the >32t lorries using an average load factor is 29 960kg. The value calculated must then be devided by the average load to give the non-exhaust emissions per tkm. |
Elementary flow outputs
| Flow | Compartment | Sub-compartment | Amount | Unit | Comment |
|---|---|---|---|---|---|
| Acetaldehyde | Emissions to air | — | 0.002016183000137856 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Acrolein | Emissions to air | — | 0.004145973741794311 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Ammonia | Emissions to air | — | 0.06674354485776805 | g | (2,2,5,4,1,na) Literature value. Derived from HBEFA database (Keller, 2010). |
| Arsenic, ion | Emissions to air | — | 0.00000023916849015317285 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Benzaldehyde | Emissions to air | — | 0.0032090371991247268 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Benzene | Emissions to air | — | 0.00016396498905908098 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Butane | Emissions to air | — | 0.00035135448577680524 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Cadmium (II) | Emissions to air | — | 0.000020807636761487965 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Carbon dioxide, fossil | Emissions to air | — | 69.2 | g | Source DCCEE 2012, ; Uncertainty matrix scores (1,1,1,2,1,1) |
| Carbon monoxide | Emissions to air | — | 0.341877572 | g | From NGGI 2004; Uncertainty matrix scores (1,1,1,2,1,1) |
| Chromium (III) | Emissions to air | — | 0.00007175054704595185 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Chromium (VI) | Emissions to air | — | 0.00000014350087527352298 | g | (2,2,5,4,1,na) Estimated value. Fuel dependant emissions - heavy metal in fuel. Estimated using the underlying assumption that 0.2% of the emitted Cr is emitted as Cr(IV). Fuel dependant emissions - heavy metal in fuel. Literature value for Cr. EMEP/EEA (2013) Tab. 3-100. |
| Copper, ion | Emissions to air | — | 0.00005070371991247265 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Dinitrogen monoxide | Emissions to air | — | 0.001612903 | g | Source DCCEE 2012, ; Uncertainty matrix scores (1,1,1,2,1,1) |
| Ethane | Emissions to air | — | 0.00007027067833698031 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Formaldehyde | Emissions to air | — | 0.019675798687089716 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Heptane | Emissions to air | — | 0.000702706783369803 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Lead (II) | Emissions to air | — | 0.00012460656455142233 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Mercury (II) | Emissions to air | — | 0.000012675908096280089 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Methane | Emissions to air | — | 0.002380952 | g | Source DCCEE 2012, ; Uncertainty matrix scores (1,1,1,2,1,1) |
| NMVOC, non-methane volatile organic compounds | Emissions to air | — | 0.061169705 | g | From NGGI 2004; Uncertainty matrix scores (1,1,1,2,1,1) |
| Nickel (II) | Emissions to air | — | 0.00002104680525164114 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Nitrogen oxides | Emissions to air | — | 0.276104647 | g | From NGGI 2004; Uncertainty matrix scores (1,1,1,2,1,1) |
| PAH, polycyclic aromatic hydrocarbons | Emissions to air | — | 0.00018702954048140045 | g | (2,2,5,4,1,na) Literature value. PAH's per kg fuel use provided by the EMEP/EEA (2013) guidebook. |
| Particulates, < 2.5 um | Emissions to air | — | 0.18435448577680527 | g | (2,2,5,4,1,na) Literature value. Derived from HBEFA database (Keller, 2010). |
| Pentane | Emissions to air | — | 0.00014054157549234136 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Propane | Emissions to air | — | 0.00023423632385120353 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Selenium (IV) | Emissions to air | — | 0.00000023916849015317285 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| Styrene | Emissions to air | — | 0.0013117199124726478 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Sulfur oxides | Emissions to air | — | 0.12437545 | g | From NGGI 2004; Uncertainty matrix scores (1,1,1,2,1,1) |
| Toluene | Emissions to air | — | 0.00002342363238512035 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| Transport energy | Non material emissions | — | 1.0 | MJ | — |
| Zinc (II) | Emissions to air | — | 0.004156739606126915 | g | (2,2,5,4,1,na) Literature value. Fuel dependant emissions - heavy metal in fuel. Literature value. EMEP/EEA (2013) Tab. 3-100. |
| m-Xylene | Emissions to air | — | 0.0022955142231947485 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
| o-Xylene | Emissions to air | — | 0.0009369431072210067 | g | (2,2,5,4,1,na) Literature value. The NMVOC split is provided by the EMEP/EEA (2013) guidebook. All elementary NMVOC exchanges available in the ecoinvent database and quantified in the EMEP/EEA guidebook are provided. Total NMVOC's derived from HBEFA database (Keller, 2010).. |
Parameters
| Name | Value | Formula | Description |
|---|---|---|---|
| d_diesel | 0.842 | — | kg/l ADO physical density |
| D_fuel | 0.842 | D_diesel | — |
| ed_fuel | 45.6 | ED_diesel | — |
| ED_diesel | 45.6 | — | MJ/kg LHV |
| kmperMJ | 0.0457 | — | km per MJ |
| Fuelperkm | 0.451312 | fuel_use*D_fuel | — |
| fuel_use | 0.536 | — | (2,1,3,1,1,na) Litres per km fuel use. ABS Motor vehicle survey 2020. http://www.freightmetrics.com.au/Calculators/TruckOperatingCostCalculator/tabid/104/Default.aspx |