| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Pre 2010 Fleet | |||||
| Diesel hybrid vehicle: 1350 – <1600 cc | km | 0.1823256532 | 0.1795097807 | 0.0002690936 | 0.0025467788 |
| Diesel hybrid vehicle: 1600 – <2000 cc | km | 0.1932439545 | 0.1902594577 | 0.0002852079 | 0.0026992889 |
| Diesel hybrid vehicle: 2000 – <3000 cc | km | 0.237569648 | 0.2339005767 | 0.000350628 | 0.0033184434 |
| Diesel hybrid vehicle: <1350 cc | km | 0.1894659048 | 0.1865397569 | 0.0002796319 | 0.002646516 |
| Diesel hybrid vehicle: ≥3000 cc | km | 0.2635284404 | 0.2594584565 | 0.0003889404 | 0.0036810435 |
| Diesel vehicle: 1350 – <1600 cc | km | 0.2033911669 | 0.2002499546 | 0.0003001841 | 0.0028410282 |
| Diesel vehicle: 1600 – <2000 cc | km | 0.2155709453 | 0.2122416261 | 0.0003181602 | 0.003011159 |
| Diesel vehicle: 2000 – <3000 cc | km | 0.265017934 | 0.2609249461 | 0.0003911388 | 0.0037018492 |
| Diesel vehicle: <1350 cc | km | 0.2113563878 | 0.2080921591 | 0.0003119399 | 0.0029522888 |
| Diesel vehicle: ≥3000 cc | km | 0.2939759494 | 0.2894357283 | 0.0004338778 | 0.0041063433 |
| Motorcycle: <60cc, petrol | km | 0.0662625199 | 0.0634818973 | 0.0008440524 | 0.0019365703 |
| Motorcycle: ≥ 60cc, petrol | km | 0.1325250399 | 0.1269637945 | 0.0016881047 | 0.0038731407 |
| Petrol hybrid vehicle: 1350 – <1600 cc | km | 0.1542578336 | 0.147784599 | 0.0019649372 | 0.0045082974 |
| Petrol hybrid vehicle: 1600 – <2000 cc | km | 0.1736903139 | 0.16640162 | 0.0022124682 | 0.0050762257 |
| Petrol hybrid vehicle: 2000 – <3000 cc | km | 0.1929224594 | 0.1848267128 | 0.0024574474 | 0.0056382992 |
| Petrol hybrid vehicle: <1350 cc | km | 0.1490491275 | 0.1427944697 | 0.0018985886 | 0.0043560691 |
| Petrol hybrid vehicle: ≥3000 cc | km | 0.2307857458 | 0.2211011144 | 0.0029397501 | 0.0067448813 |
| Petrol vehicle: 1350 – <1600 cc | km | 0.1953932558 | 0.1871938254 | 0.0024889204 | 0.00571051 |
| Petrol vehicle: 1600 – <2000 cc | km | 0.2200077309 | 0.2107753853 | 0.0028024597 | 0.0064298859 |
| Petrol vehicle: 2000 – <3000 cc | km | 0.2443684485 | 0.2341138362 | 0.0031127667 | 0.0071418456 |
| Petrol vehicle: <1350 cc | km | 0.1887955615 | 0.180872995 | 0.0024048789 | 0.0055176876 |
| Petrol vehicle: ≥3000 cc | km | 0.2923286113 | 0.2800614116 | 0.0037236835 | 0.0085435163 |
7 Travel emission factors
This travel emissions section provides detail on how to calculate emissions associated with both business travel and staff commuting.
Business travel emissions result from travel associated with (and generally paid for by) the entity. We provide factors for private and rental vehicles, taxis, public transport, air travel, helicopters and accommodation. Business travel emissions are indirect (Scope 3/Category 6: Business travel) if the entity does not directly own or control the vehicles used for travel. If the entity owns or has an operating lease for the vehicle(s) these emissions are direct (Scope 1/Category 1: Purchased goods and services GHG Protocol) and should be accounted for in transport fuels (see Section 3.3).
Staff commuting emissions result from employees travelling between their homes and their worksites. Emissions from staff commuting may arise from the use of private and rental vehicles, taxis, public transport, and air travel. Other emissions associated with working from home can be accounted for in indirect business-related emission factors (see Section 6).
Staff commuting emissions are indirect (Scope 3/Category 7: Employee commuting Section 6.2.3).
7.1 Overview of changes since previous update
| Domain | Emission factors | Size of change | Explanation for change |
|---|---|---|---|
| Travel | All electric and PHEV passenger vehicles, electric motorcycles | 39.10% | The change in all-electric and PHEV passenger vehicles, as well as electric motorcycles, is driven by the increase in the latest annual electricity factor, which is used to derive these emissions factors. |
| Business travel - Hotel Stays | -56.7% to +32.1% | The Cornell Hotel Sustainability Benchmarking Index has introduced a new hotel type classification, replacing the previous “All Hotels” group into separate “Resort” and “Non-Resort” categories, with the latter used to calculate the MEG 2025 emissions factors. This had a significant impact, with the factors decreasing for 40 out of the 48 countries provided. 26 of these countries decreased by over 20%. | |
| Domestic air travel | n/a | These factors have not been updated from the previous edition. The information required to update these factors was not available in time for this publication. | |
| International air travel | No change | The International air travel emission factors are sourced from the UK Greenhouse Gas Reporting: Conversion Factors 2022, published by the UK Department for Energy Security and Net Zero (DESNZ). These factors have remained unchanged in the 2023 and 2024 DESNZ editions, meaning they still reflect air travel data influenced by the COVID-19 pandemic. As a result, we continue to use the 2022 edition factors, which are based on pre-COVID air travel data which provides a more representative period for emissions reporting. |
7.2 Passenger vehicles
This section covers emissions from private vehicles for which mileage is claimed, rental vehicles and taxi travel.
Travel, including rental vehicles, staff mileage and taxi travel are indirect (Scope 3) emissions. This is a change in guidance, to align better with leading practice. As with direct (Scope 1) emissions from transport fuels, the most accurate way to calculate emissions is based on fuel consumption data. Fuel-use data are preferable because factors such as individual vehicle fuel efficiency and driving efficiency mean that kilometre-based estimates of emissions are less accurate. However, this information may not be easily available.
The 2024 fleet statistics (Table 7.3, Table 7.4, Table 7.5 and Table 7.6) were taken from the Te Manatū Waka Ministry of Transport Vehicle Fleet Emissions Model. This provides energy (fuel and electricity) use per km travelled by vehicle.
Fuel-use based emission factors are provided in Section 3.3.
If the only information known is kilometres travelled, use the emission factors in this section. Factors such as individual vehicle fuel efficiency and driving efficiency mean that kilometre based estimates of carbon dioxide equivalent emissions are less accurate than calculating emissions based on fuel-use data.
If the vehicle size and engine type are known, use the factors in Table 7.3, Table 7.4, Table 7.5 and Table 7.6. Table 7.7 lists default private car emission factors and Table 7.8 lists the default rental car emission factors based on distance travelled. Table 7.9 lists emission factors for taxi travel based on dollars spent and kilometres travelled.
Table 7.2 details engine sizes and typical corresponding vehicles.
| Engine size | Vehicle size | Example vehicles | Comparative electric vehicles |
|---|---|---|---|
| <1350 cc | Very small | Fiat 500 | Peugeot iOn |
| 1350-<1600 cc | Small | Suzuki Swift | Renault Zoe |
| 1600-<2000 cc | Medium | Toyota Corolla | Nissan Leaf |
| 2000-<3000 cc | Large | Toyota RAV4 | Hyundai Ioniq |
| >3000 cc | Very large | Ford Ranger | Nissan e-NV200 |
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| 2010–2015 Fleet | |||||
| Diesel hybrid vehicle: 1350 – <1600 cc | km | 0.1615804965 | 0.1590850163 | 0.0002384759 | 0.0022570043 |
| Diesel hybrid vehicle: 1600 – <2000 cc | km | 0.1712565049 | 0.1686115865 | 0.0002527567 | 0.0023921617 |
| Diesel hybrid vehicle: 2000 – <3000 cc | km | 0.2105387861 | 0.2072871845 | 0.0003107333 | 0.0029408683 |
| Diesel hybrid vehicle: <1350 cc | km | 0.1679083247 | 0.1653151162 | 0.0002478151 | 0.0023453933 |
| Diesel hybrid vehicle: ≥3000 cc | km | 0.2335439666 | 0.2299370686 | 0.0003446865 | 0.0032622115 |
| Diesel vehicle: 1350 – <1600 cc | km | 0.1805474809 | 0.1777590709 | 0.0002664692 | 0.0025219408 |
| Diesel vehicle: 1600 – <2000 cc | km | 0.1913592991 | 0.1884039093 | 0.0002824263 | 0.0026729635 |
| Diesel vehicle: 2000 – <3000 cc | km | 0.2352332395 | 0.2316002521 | 0.0003471797 | 0.0032858077 |
| Diesel vehicle: <1350 cc | km | 0.1876180957 | 0.1847204857 | 0.0002769047 | 0.0026207053 |
| Diesel vehicle: ≥3000 cc | km | 0.2609367369 | 0.2569067797 | 0.0003851154 | 0.0036448418 |
| Electric vehicle: 1350 – <1600 cc | km | 0.0210148273 | 0.0204080078 | 0.0005674308 | 0.0000393887 |
| Electric vehicle: 1600 – <2000 cc | km | 0.0236621497 | 0.0229788867 | 0.0006389123 | 0.0000443506 |
| Electric vehicle: 2000 – <3000 cc | km | 0.0262821801 | 0.0255232617 | 0.0007096569 | 0.0000492614 |
| Electric vehicle: <1350 cc | km | 0.0203052357 | 0.0197189063 | 0.0005482708 | 0.0000380587 |
| Electric vehicle: ≥3000 cc | km | 0.031440365 | 0.0305325 | 0.0008489354 | 0.0000589296 |
| Motorcycle: <60cc, electricity | km | 0.0049924743 | 0.0048483128 | 0.000134804 | 0.0000093575 |
| Motorcycle: <60cc, petrol | km | 0.0587366048 | 0.0562717976 | 0.0007481872 | 0.00171662 |
| Motorcycle: ≥ 60cc, electricity | km | 0.0099849487 | 0.0096966255 | 0.0002696081 | 0.0000187151 |
| Motorcycle: ≥ 60cc, petrol | km | 0.1174732097 | 0.1125435953 | 0.0014963744 | 0.00343324 |
| PHEV (Diesel) – Diesel consumption: 1350 – <1600 cc | km | 0.0845604598 | 0.0832544918 | 0.0001248024 | 0.0011811656 |
| PHEV (Diesel) – Diesel consumption: 1600 – <2000 cc | km | 0.0896242376 | 0.0882400636 | 0.000132276 | 0.001251898 |
| PHEV (Diesel) – Diesel consumption: 2000 – <3000 cc | km | 0.1101819647 | 0.1084802932 | 0.0001626171 | 0.0015390544 |
| PHEV (Diesel) – Diesel consumption: <1350 cc | km | 0.0878720233 | 0.0865149108 | 0.0001296899 | 0.0012274225 |
| PHEV (Diesel) – Diesel consumption: ≥3000 cc | km | 0.1222213425 | 0.1203337326 | 0.0001803859 | 0.001707224 |
| PHEV (Diesel) – Electricity consumption: 1350 – <1600 cc | km | 0.0101392239 | 0.0098464459 | 0.0002737737 | 0.0000190042 |
| PHEV (Diesel) – Electricity consumption: 1600 – <2000 cc | km | 0.0111094484 | 0.0107886545 | 0.0002999712 | 0.0000208228 |
| PHEV (Diesel) – Electricity consumption: 2000 – <3000 cc | km | 0.012574282 | 0.0122111898 | 0.0003395238 | 0.0000235683 |
| PHEV (Diesel) – Electricity consumption: <1350 cc | km | 0.0105565583 | 0.0102517295 | 0.0002850424 | 0.0000197865 |
| PHEV (Diesel) – Electricity consumption: ≥3000 cc | km | 0.0148720932 | 0.01444265 | 0.0004015681 | 0.0000278752 |
| PHEV (Petrol) – Electricity consumption: 1350 – <1600 cc | km | 0.0100170677 | 0.0097278171 | 0.0002704753 | 0.0000187753 |
| PHEV (Petrol) – Electricity consumption: 1600 – <2000 cc | km | 0.011278958 | 0.0109532693 | 0.0003045482 | 0.0000211405 |
| PHEV (Petrol) – Electricity consumption: 2000 – <3000 cc | km | 0.0125278392 | 0.0121660881 | 0.0003382698 | 0.0000234813 |
| PHEV (Petrol) – Electricity consumption: <1350 cc | km | 0.009678829 | 0.0093993453 | 0.0002613424 | 0.0000181413 |
| PHEV (Petrol) – Electricity consumption: ≥3000 cc | km | 0.014986574 | 0.014553825 | 0.0004046592 | 0.0000280898 |
| PHEV (Petrol) – Petrol consumption: 1350 – <1600 cc | km | 0.0715429404 | 0.0685407316 | 0.0009113144 | 0.0020908945 |
| PHEV (Petrol) – Petrol consumption: 1600 – <2000 cc | km | 0.0805554927 | 0.0771750835 | 0.0010261163 | 0.0023542929 |
| PHEV (Petrol) – Petrol consumption: 2000 – <3000 cc | km | 0.089475132 | 0.0857204214 | 0.0011397347 | 0.0026149758 |
| PHEV (Petrol) – Petrol consumption: <1350 cc | km | 0.0691272048 | 0.0662263692 | 0.0008805427 | 0.0020202928 |
| PHEV (Petrol) – Petrol consumption: ≥3000 cc | km | 0.1070356719 | 0.1025440556 | 0.001363421 | 0.0031281953 |
| Petrol hybrid vehicle: 1350 – <1600 cc | km | 0.1367062556 | 0.1309695508 | 0.0017413651 | 0.0039953397 |
| Petrol hybrid vehicle: 1600 – <2000 cc | km | 0.153927693 | 0.1474683124 | 0.0019607318 | 0.0044986488 |
| Petrol hybrid vehicle: 2000 – <3000 cc | km | 0.1709715898 | 0.1637969837 | 0.0021778371 | 0.004996769 |
| Petrol hybrid vehicle: <1350 cc | km | 0.1320902002 | 0.1265472023 | 0.0016825657 | 0.0038604322 |
| Petrol hybrid vehicle: ≥3000 cc | km | 0.2045267616 | 0.1959440552 | 0.002605263 | 0.0059774433 |
| Petrol vehicle: 1350 – <1600 cc | km | 0.1731612571 | 0.1658947643 | 0.0022057291 | 0.0050607637 |
| Petrol vehicle: 1600 – <2000 cc | km | 0.1949750778 | 0.1867931957 | 0.0024835936 | 0.0056982884 |
| Petrol vehicle: 2000 – <3000 cc | km | 0.2165640137 | 0.2074761793 | 0.0027585936 | 0.0063292408 |
| Petrol vehicle: <1350 cc | km | 0.1673142536 | 0.1602931229 | 0.0021312499 | 0.0048898807 |
| Petrol vehicle: ≥3000 cc | km | 0.2590672313 | 0.2481958032 | 0.0032999999 | 0.0075714282 |
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| 2015–2020 Fleet | |||||
| Diesel hybrid vehicle: 1350 – <1600 cc | km | 0.1523914328 | 0.1500378702 | 0.0002249138 | 0.0021286488 |
| Diesel hybrid vehicle: 1600 – <2000 cc | km | 0.1615171678 | 0.1590226656 | 0.0002383825 | 0.0022561197 |
| Diesel hybrid vehicle: 2000 – <3000 cc | km | 0.1985654702 | 0.1954987869 | 0.0002930619 | 0.0027736214 |
| Diesel hybrid vehicle: <1350 cc | km | 0.1583593982 | 0.1559136652 | 0.0002337219 | 0.0022120111 |
| Diesel hybrid vehicle: ≥3000 cc | km | 0.2202623489 | 0.2168605748 | 0.0003250842 | 0.0030766899 |
| Diesel vehicle: 1350 – <1600 cc | km | 0.1717168568 | 0.1690648287 | 0.0002534361 | 0.002398592 |
| Diesel vehicle: 1600 – <2000 cc | km | 0.1819998662 | 0.1791890252 | 0.0002686128 | 0.0025422282 |
| Diesel vehicle: 2000 – <3000 cc | km | 0.2236339702 | 0.2201801242 | 0.0003300604 | 0.0031237857 |
| Diesel vehicle: <1350 cc | km | 0.178441646 | 0.1756857589 | 0.0002633612 | 0.0024925259 |
| Diesel vehicle: ≥3000 cc | km | 0.2480700371 | 0.2442387957 | 0.0003661255 | 0.0034651159 |
| Electric vehicle: 1350 – <1600 cc | km | 0.0201048461 | 0.019524303 | 0.00054286 | 0.0000376831 |
| Electric vehicle: 1600 – <2000 cc | km | 0.0226375345 | 0.021983858 | 0.0006112462 | 0.0000424302 |
| Electric vehicle: 2000 – <3000 cc | km | 0.0251441127 | 0.0244180569 | 0.0006789275 | 0.0000471283 |
| Electric vehicle: <1350 cc | km | 0.0194259811 | 0.0188650408 | 0.0005245296 | 0.0000364107 |
| Electric vehicle: ≥3000 cc | km | 0.0300789385 | 0.0292103858 | 0.0008121749 | 0.0000563778 |
| Motorcycle: <60cc, electricity | km | 0.0050919711 | 0.0049449365 | 0.0001374906 | 0.000009544 |
| Motorcycle: <60cc, petrol | km | 0.0557618645 | 0.0534218886 | 0.0007102949 | 0.001629681 |
| Motorcycle: ≥ 60cc, electricity | km | 0.0098108435 | 0.0095275477 | 0.000264907 | 0.0000183887 |
| Motorcycle: ≥ 60cc, petrol | km | 0.1074379479 | 0.1029294506 | 0.0013685452 | 0.0031399522 |
| PHEV (Diesel) – Diesel consumption: 1350 – <1600 cc | km | 0.0797515165 | 0.0785198188 | 0.0001177049 | 0.0011139929 |
| PHEV (Diesel) – Diesel consumption: 1600 – <2000 cc | km | 0.0845273178 | 0.0832218617 | 0.0001247535 | 0.0011807027 |
| PHEV (Diesel) – Diesel consumption: 2000 – <3000 cc | km | 0.1039159294 | 0.1023110318 | 0.0001533691 | 0.0014515286 |
| PHEV (Diesel) – Diesel consumption: <1350 cc | km | 0.0828747517 | 0.0815948181 | 0.0001223145 | 0.0011576191 |
| PHEV (Diesel) – Diesel consumption: ≥3000 cc | km | 0.1152706292 | 0.1134903675 | 0.0001701274 | 0.0016101344 |
| PHEV (Diesel) – Electricity consumption: 1350 – <1600 cc | km | 0.0097001765 | 0.0094200764 | 0.0002619188 | 0.0000181813 |
| PHEV (Diesel) – Electricity consumption: 1600 – <2000 cc | km | 0.0106283886 | 0.0103214856 | 0.0002869819 | 0.0000199211 |
| PHEV (Diesel) – Electricity consumption: 2000 – <3000 cc | km | 0.0120297921 | 0.0116824225 | 0.0003248218 | 0.0000225478 |
| PHEV (Diesel) – Electricity consumption: <1350 cc | km | 0.0100994396 | 0.0098078105 | 0.0002726995 | 0.0000189297 |
| PHEV (Diesel) – Electricity consumption: ≥3000 cc | km | 0.0142281038 | 0.0138172563 | 0.0003841794 | 0.0000266681 |
| PHEV (Petrol) – Electricity consumption: 1350 – <1600 cc | km | 0.00958331 | 0.0093065844 | 0.0002587633 | 0.0000179623 |
| PHEV (Petrol) – Electricity consumption: 1600 – <2000 cc | km | 0.0107905581 | 0.0104789723 | 0.0002913607 | 0.0000202251 |
| PHEV (Petrol) – Electricity consumption: 2000 – <3000 cc | km | 0.0119853604 | 0.0116392738 | 0.0003236221 | 0.0000224645 |
| PHEV (Petrol) – Electricity consumption: <1350 cc | km | 0.0092597177 | 0.0089923361 | 0.0002500258 | 0.0000173558 |
| PHEV (Petrol) – Electricity consumption: ≥3000 cc | km | 0.0143376274 | 0.0139236172 | 0.0003871367 | 0.0000268734 |
| PHEV (Petrol) – Petrol consumption: 1350 – <1600 cc | km | 0.0674743019 | 0.0646428283 | 0.000859488 | 0.0019719855 |
| PHEV (Petrol) – Petrol consumption: 1600 – <2000 cc | km | 0.0759743113 | 0.0727861456 | 0.0009677612 | 0.0022204045 |
| PHEV (Petrol) – Petrol consumption: 2000 – <3000 cc | km | 0.0843866918 | 0.0808455112 | 0.0010749182 | 0.0024662624 |
| PHEV (Petrol) – Petrol consumption: <1350 cc | km | 0.0651959488 | 0.0624600834 | 0.0008304664 | 0.001905399 |
| PHEV (Petrol) – Petrol consumption: ≥3000 cc | km | 0.1009485659 | 0.0967123873 | 0.0012858834 | 0.0029502953 |
| Petrol hybrid vehicle: 1350 – <1600 cc | km | 0.128931787 | 0.123521328 | 0.0016423338 | 0.0037681252 |
| Petrol hybrid vehicle: 1600 – <2000 cc | km | 0.1451738433 | 0.1390818069 | 0.0018492252 | 0.0042428111 |
| Petrol hybrid vehicle: 2000 – <3000 cc | km | 0.1612484557 | 0.1544818686 | 0.0020539837 | 0.0047126034 |
| Petrol hybrid vehicle: <1350 cc | km | 0.1245782462 | 0.1193504779 | 0.0015868784 | 0.0036408898 |
| Petrol hybrid vehicle: ≥3000 cc | km | 0.1928953489 | 0.18480074 | 0.002457102 | 0.0056375068 |
| Petrol vehicle: 1350 – <1600 cc | km | 0.1633135969 | 0.1564603487 | 0.0020802895 | 0.0047729586 |
| Petrol vehicle: 1600 – <2000 cc | km | 0.1838868682 | 0.1761702888 | 0.002342352 | 0.0053742274 |
| Petrol vehicle: 2000 – <3000 cc | km | 0.2042480439 | 0.1956770336 | 0.0026017127 | 0.0059692976 |
| Petrol vehicle: <1350 cc | km | 0.1577991118 | 0.151177272 | 0.002010046 | 0.0046117938 |
| Petrol vehicle: ≥3000 cc | km | 0.2443341086 | 0.2340809374 | 0.0031123293 | 0.007140842 |
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Post 2020 Fleet | |||||
| Diesel hybrid vehicle: 1350 – <1600 cc | km | 0.1444720988 | 0.1422408439 | 0.0002132257 | 0.0020180292 |
| Diesel hybrid vehicle: 1600 – <2000 cc | km | 0.1531235962 | 0.1507587259 | 0.0002259944 | 0.0021388758 |
| Diesel hybrid vehicle: 2000 – <3000 cc | km | 0.1882466075 | 0.1853392907 | 0.0002778323 | 0.0026294845 |
| Diesel hybrid vehicle: <1350 cc | km | 0.1501299266 | 0.1478112911 | 0.0002215761 | 0.0020970594 |
| Diesel hybrid vehicle: ≥3000 cc | km | 0.2088159632 | 0.2055909693 | 0.0003081905 | 0.0029168034 |
| Diesel vehicle: 1350 – <1600 cc | km | 0.1642241802 | 0.1616878704 | 0.0002423777 | 0.0022939321 |
| Diesel vehicle: 1600 – <2000 cc | km | 0.1740585017 | 0.1713703087 | 0.0002568922 | 0.0024313008 |
| Diesel vehicle: 2000 – <3000 cc | km | 0.2138213793 | 0.2105190807 | 0.000315578 | 0.0029867205 |
| Diesel vehicle: <1350 cc | km | 0.1706555405 | 0.1680199035 | 0.0002518697 | 0.0023837673 |
| Diesel vehicle: ≥3000 cc | km | 0.2371852426 | 0.2335221081 | 0.0003500606 | 0.0033130739 |
| Electric vehicle: 1350 – <1600 cc | km | 0.0193672425 | 0.0188079983 | 0.0005229436 | 0.0000363006 |
| Electric vehicle: 1600 – <2000 cc | km | 0.021807012 | 0.0211773176 | 0.0005888209 | 0.0000408735 |
| Electric vehicle: 2000 – <3000 cc | km | 0.0242216293 | 0.0235222109 | 0.0006540191 | 0.0000453993 |
| Electric vehicle: <1350 cc | km | 0.0187132837 | 0.0181729231 | 0.0005052858 | 0.0000350748 |
| Electric vehicle: ≥3000 cc | km | 0.028975407 | 0.0281387196 | 0.000782378 | 0.0000543094 |
| Motorcycle: <60cc, electricity | km | 0.0048625099 | 0.0047221012 | 0.0001312948 | 0.0000091139 |
| Motorcycle: <60cc, petrol | km | 0.0532490495 | 0.0510145206 | 0.0006782867 | 0.0015562422 |
| Motorcycle: ≥ 60cc, electricity | km | 0.0096935254 | 0.0094136173 | 0.0002617392 | 0.0000181689 |
| Motorcycle: ≥ 60cc, petrol | km | 0.1061532049 | 0.1016986202 | 0.0013521801 | 0.0031024046 |
| PHEV (Diesel) – Diesel consumption: 1350 – <1600 cc | km | 0.0756070651 | 0.074439375 | 0.0001115881 | 0.0010561019 |
| PHEV (Diesel) – Diesel consumption: 1600 – <2000 cc | km | 0.080134682 | 0.0788970666 | 0.0001182704 | 0.001119345 |
| PHEV (Diesel) – Diesel consumption: 2000 – <3000 cc | km | 0.0985157246 | 0.0969942288 | 0.0001453989 | 0.0013760969 |
| PHEV (Diesel) – Diesel consumption: <1350 cc | km | 0.0785679949 | 0.0773545757 | 0.0001159582 | 0.0010974611 |
| PHEV (Diesel) – Diesel consumption: ≥3000 cc | km | 0.1092803541 | 0.1075926073 | 0.0001612864 | 0.0015264604 |
| PHEV (Diesel) – Electricity consumption: 1350 – <1600 cc | km | 0.0093442979 | 0.0090744741 | 0.0002523096 | 0.0000175143 |
| PHEV (Diesel) – Electricity consumption: 1600 – <2000 cc | km | 0.0102384559 | 0.0099428125 | 0.0002764531 | 0.0000191902 |
| PHEV (Diesel) – Electricity consumption: 2000 – <3000 cc | km | 0.0115884449 | 0.0112538195 | 0.0003129048 | 0.0000217206 |
| PHEV (Diesel) – Electricity consumption: <1350 cc | km | 0.0097289129 | 0.009447983 | 0.0002626947 | 0.0000182352 |
| PHEV (Diesel) – Electricity consumption: ≥3000 cc | km | 0.0137061053 | 0.0133103308 | 0.0003700847 | 0.0000256897 |
| PHEV (Petrol) – Electricity consumption: 1350 – <1600 cc | km | 0.0092317189 | 0.0089651459 | 0.0002492698 | 0.0000173033 |
| PHEV (Petrol) – Electricity consumption: 1600 – <2000 cc | km | 0.0103946757 | 0.0100945214 | 0.0002806713 | 0.000019483 |
| PHEV (Petrol) – Electricity consumption: 2000 – <3000 cc | km | 0.0115456433 | 0.0112122539 | 0.0003117491 | 0.0000216403 |
| PHEV (Petrol) – Electricity consumption: <1350 cc | km | 0.0089199985 | 0.0086624267 | 0.0002408529 | 0.000016719 |
| PHEV (Petrol) – Electricity consumption: ≥3000 cc | km | 0.0138116107 | 0.0134127897 | 0.0003729335 | 0.0000258875 |
| PHEV (Petrol) – Petrol consumption: 1350 – <1600 cc | km | 0.0638126603 | 0.0611348429 | 0.000812846 | 0.0018649714 |
| PHEV (Petrol) – Petrol consumption: 1600 – <2000 cc | km | 0.0718513981 | 0.0688362452 | 0.0009152435 | 0.0020999094 |
| PHEV (Petrol) – Petrol consumption: 2000 – <3000 cc | km | 0.0798072622 | 0.0764582516 | 0.0010165854 | 0.0023324253 |
| PHEV (Petrol) – Petrol consumption: <1350 cc | km | 0.0616579471 | 0.0590705495 | 0.0007853993 | 0.0018019983 |
| PHEV (Petrol) – Petrol consumption: ≥3000 cc | km | 0.0954703697 | 0.0914640766 | 0.0012161021 | 0.002790191 |
| Petrol hybrid vehicle: 1350 – <1600 cc | km | 0.1219350197 | 0.1168181711 | 0.001553209 | 0.0035636396 |
| Petrol hybrid vehicle: 1600 – <2000 cc | km | 0.137295665 | 0.1315342264 | 0.001748873 | 0.0040125657 |
| Petrol hybrid vehicle: 2000 – <3000 cc | km | 0.1524979532 | 0.1460985698 | 0.0019425198 | 0.0044568636 |
| Petrol hybrid vehicle: <1350 cc | km | 0.1178177333 | 0.1128736614 | 0.001500763 | 0.0034433089 |
| Petrol hybrid vehicle: ≥3000 cc | km | 0.1824274581 | 0.1747721209 | 0.002323762 | 0.0053315751 |
| Petrol vehicle: 1350 – <1600 cc | km | 0.154638797 | 0.1481495758 | 0.0019697899 | 0.0045194313 |
| Petrol vehicle: 1600 – <2000 cc | km | 0.1741192688 | 0.1668125744 | 0.0022179322 | 0.0050887623 |
| Petrol vehicle: 2000 – <3000 cc | km | 0.1933989111 | 0.1852831708 | 0.0024635164 | 0.0056522238 |
| Petrol vehicle: <1350 cc | km | 0.1494172272 | 0.1431471226 | 0.0019032775 | 0.0043668271 |
| Petrol vehicle: ≥3000 cc | km | 0.2313557067 | 0.2216471576 | 0.0029470103 | 0.0067615388 |
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Private car default | |||||
| Diesel | km | 0.265017934 | 0.2609249461 | 0.0003911388 | 0.0037018492 |
| Diesel hybrid | km | 0.237569648 | 0.2339005767 | 0.000350628 | 0.0033184434 |
| Electric | km | 0.0262821801 | 0.0255232617 | 0.0007096569 | 0.0000492614 |
| PHEV (Diesel) – Diesel consumption | km | 0.1101819647 | 0.1084802932 | 0.0001626171 | 0.0015390544 |
| PHEV (Diesel) – Electricity consumption | km | 0.012574282 | 0.0122111898 | 0.0003395238 | 0.0000235683 |
| PHEV (Petrol) – Electricity consumption | km | 0.0125278392 | 0.0121660881 | 0.0003382698 | 0.0000234813 |
| PHEV (Petrol) – Petrol consumption | km | 0.089475132 | 0.0857204214 | 0.0011397347 | 0.0026149758 |
| Petrol | km | 0.2443684485 | 0.2341138362 | 0.0031127667 | 0.0071418456 |
| Petrol hybrid | km | 0.1929224594 | 0.1848267128 | 0.0024574474 | 0.0056382992 |
Note: Defaults are based on the average age of the vehicle fleet (pre-2010 for petrol and diesel including hybrids, and 2010–2015 for all plug-in cars) and most common engine size (2000–3000 cc). Source: Te Manatū Waka Ministry of Transport
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Rental car default | |||||
| Diesel | km | 0.1819998662 | 0.1791890252 | 0.0002686128 | 0.0025422282 |
| Diesel hybrid | km | 0.1615171678 | 0.1590226656 | 0.0002383825 | 0.0022561197 |
| Electric | km | 0.0226375345 | 0.021983858 | 0.0006112462 | 0.0000424302 |
| PHEV (Diesel) – Diesel consumption | km | 0.0845273178 | 0.0832218617 | 0.0001247535 | 0.0011807027 |
| PHEV (Diesel) – Electricity consumption | km | 0.0106283886 | 0.0103214856 | 0.0002869819 | 0.0000199211 |
| PHEV (Petrol) – Electricity consumption | km | 0.0107905581 | 0.0104789723 | 0.0002913607 | 0.0000202251 |
| PHEV (Petrol) – Petrol consumption | km | 0.0759743113 | 0.0727861456 | 0.0009677612 | 0.0022204045 |
| Petrol | km | 0.1838868682 | 0.1761702888 | 0.002342352 | 0.0053742274 |
| Petrol hybrid | km | 0.1451738433 | 0.1390818069 | 0.0018492252 | 0.0042428111 |
Note: Defaults assume a 2015−2020 fleet for rental cars and engine size of 1600 – <2000 cc.
We were unable to source more up-to-date data on the New Zealand taxi fleet to produce a representative vehicle type for the taxi (regular) factor. Therefore, this factor is derived from an average of the factors for a petrol, diesel, petrol plug-in hybrid and electric vehicle, for a 2010−2015 fleet and 2000–3000 cc vehicle class.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Taxi Travel | |||||
| Electric | km | 0.0262821801 | 0.0255232617 | 0.0007096569 | 0.0000492614 |
| Electric – dollars spent | $ | 0.0072602708 | 0.0070506248 | 0.0001960378 | 0.0000136081 |
| Petrol hybrid | km | 0.1709715898 | 0.1637969837 | 0.0021778371 | 0.004996769 |
| Petrol hybrid – dollars spent | $ | 0.0472297209 | 0.0452477855 | 0.0006016125 | 0.0013803229 |
| Regular | km | 0.1622627558 | 0.1570991692 | 0.0014983168 | 0.0036652697 |
| Regular – dollars spent | $ | 0.0448239657 | 0.0433975606 | 0.0004138997 | 0.0010125055 |
7.2.1 GHG inventory development
Entities should gather the activity data on passenger vehicle use with as much detail as possible, including age of the vehicle, engine size, fuel type and kilometres travelled. If information is not available, we provide conservative defaults to allow for overestimation rather than underestimation.
If fuel-use data are available, see Section 3.3.
If fuel-use data are not available, collect data on kilometres travelled by vehicle type and multiply this by the emission factor based on distance travelled for each GHG. If the vehicle is electric and the charging point is within the entity’s boundaries, this is a direct (Scope 1) emission source and emissions are zero. If travel is by rideshare apps (eg, Uber, YourRide, Waka Rider, Ola or Share Your Ride) we recommend using the taxi travel emission factors by distance travelled Table 7.9. If this information is not available, use the taxi emission factors per dollars spent.
Because plug-in hybrids operate on both a fossil fuel and electricity, two separate emission factors should be applied, that for the fossil fuel (petrol or diesel) and that for electricity. The plug-in hybrid electric vehicle electricity factor includes both the electricity and the electricity transmission and distribution loss factor.
Applying the equation E = Q x F this means:
- E = emissions from the emissions source in kg CO2-e per year
- Q = distance travelled by vehicle type (km)
- F = emission factors for correlating vehicle type from Table 3.3 and Table 7.3 to Table 7.9
7.2.1.1 PASSENGER VEHICLES: EXAMPLE CALCULATION 1
An entity has 15 petrol vehicles. They use 40,000 litres of regular petrol in the reporting period.
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 40,000 x 0.0303562842 kg CO₂-e per litre | 1,210 kg CO₂-e |
| CO₂ emissions | 40,000 x 2.283122022 kg CO₂-e per litre | 91,300 kg CO₂-e |
| N₂O emissions | 40,000 x 0.0696486174 kg CO₂-e per litre | 2,790 kg CO₂-e |
| Total CO₂-e emissions | 40,000 x 2.383126924 kg CO₂-e per litre | 95,300 kg CO₂-e |
Note: Numbers may not add due to rounding.
7.2.1.2 PASSENGER VEHICLES: EXAMPLE CALCULATION 2
An entity owns three post-2020 petrol plug-in hybrid electric vehicles (PHEVs). They are all between 1600 and 2000 cc and travel a total of 37,800 km in the reporting period. We need to capture both the fossil fuel and electricity-based emissions.
For the petrol-based emissions, use the PHEV (Petrol) − Petrol consumption emission factor:
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 37,800 x 0.0009152435 kg CO₂-e per km | 34.6 kg CO₂-e |
| CO₂ emissions | 37,800 x 0.0688362452 kg CO₂-e per km | 2,600 kg CO₂-e |
| N₂O emissions | 37,800 x 0.0020999094 kg CO₂-e per km | 79.4 kg CO₂-e |
| Total CO₂-e emissions | 37,800 x 0.0718513981 kg CO₂-e per km | 2,720 kg CO₂-e |
Then also use the PHEV (Petrol) − Electricity consumption emission factor:
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 37,800 x 0.0002806713 kg CO₂-e per km | 10.6 kg CO₂-e |
| CO₂ emissions | 37,800 x 0.0100945214 kg CO₂-e per km | 382 kg CO₂-e |
| N₂O emissions | 37,800 x 0.000019483 kg CO₂-e per km | 0.736 kg CO₂-e |
| Total CO₂-e emissions | 37,800 x 0.0103946757 kg CO₂-e per km | 393 kg CO₂-e |
The sum of the above totals is the total emissions:
- 2,720 kg CO₂-e + 393 kg CO₂-e = 3,110 kg CO₂-e
Note: Numbers may not add due to rounding.
7.2.1.3 PASSENGER VEHICLES: EXAMPLE CALCULATION 3
An entity uses petrol rental cars to travel 12,000 km. It also spends $18,000 on hybrid taxi travel.
- Total CO2-e emissions from rental cars = 12,000 km × 0.1838868682 = 2,210 kg CO₂-e
- Total CO2-e emissions from hybrid taxi travel = $18,000 × 0.0472297209 = 850 kg CO₂-e
Note: Numbers may not add due to rounding.
7.2.2 Emission factor derivation methodology
The 2024 fleet statistics were taken from the Te Manatū Waka Ministry of Transport Vehicle Fleet Emissions Model. This provides energy (fuel and electricity) use per 100 km travelled by vehicle.
We split the fleet into four categories and develop average emission factors for these.
- The pre-2010 fleet is based on the average fuel consumption data from 1970 to 2010. We assume there are no electric vehicles or plug-in hybrid vehicles.
- The 2010–2015 fleet is based on the average fuel consumption data from vehicles produced between 2010 and 2015.
- The 2015−2020 fleet is based on the average fuel consumption data from vehicles produced between 2015 and 2020.
- The post-2020 fleet is based on the average fuel consumption data from vehicles produced from 2021 onwards.
Note that some guidance documents, such as those published by the UK Department for Energy Security and Net Zero (formerly published by the Department of Business, Energy and Industrial Strategy), apply an uplift factor to passenger vehicles. This accounts for the real-world effects on fuel consumption, such as the use of air conditioning, vehicle payload, gradient and weather. We do not apply an uplift factor here, because the Vehicle Fleet Emissions Model is based on real-world driving and fuel use.
For each category, default vehicles are based on the 2000–3000 cc engine size, as it is the most common size for light passenger vehicles in New Zealand based on Motor Vehicle Register open data.
| CC | Unit | Pre 2010 Fleet | 2010-2015 Fleet | 2015-2020 Fleet | Post 2020 Fleet |
|---|---|---|---|---|---|
| Diesel hybrid vehicle | |||||
| 1350 - <1600 cc | Litres | 6.801469 | 6.027592 | 5.684804 | 5.389381 |
| 1600 - <2000 cc | Litres | 7.208765 | 6.388546 | 6.02523 | 5.712116 |
| 2000 - <3000 cc | Litres | 8.862288 | 7.85393 | 7.407278 | 7.022344 |
| <1350 cc | Litres | 7.067828 | 6.263645 | 5.907433 | 5.600441 |
| >=3000 cc | Litres | 9.830654 | 8.712115 | 8.216658 | 7.789662 |
| Diesel vehicle | |||||
| 1350 - <1600 cc | Litres | 7.587296 | 6.735136 | 6.405719 | 6.126212 |
| 1600 - <2000 cc | Litres | 8.04165 | 7.138459 | 6.789316 | 6.493071 |
| 2000 - <3000 cc | Litres | 9.886218 | 8.775131 | 8.342433 | 7.976384 |
| <1350 cc | Litres | 7.88443 | 6.998898 | 6.65658 | 6.366127 |
| >=3000 cc | Litres | 10.966467 | 9.733973 | 9.253995 | 8.847949 |
| Electric vehicle | |||||
| 1350 - <1600 cc | kWh | 21.751352 | 19.313457 | 18.477148 | 17.799261 |
| 1600 - <2000 cc | kWh | 24.491458 | 21.74645 | 20.804788 | 20.041506 |
| 2000 - <3000 cc | kWh | 27.203315 | 24.154362 | 23.108433 | 22.260634 |
| <1350 cc | kWh | 21.016891 | 18.661314 | 17.853244 | 17.198247 |
| >=3000 cc | kWh | 32.542283 | 28.894938 | 27.643733 | 26.629544 |
| Motorcycle | |||||
| <60cc, electricity | Litres | 5.137236 | 4.588281 | 4.508276 | 4.454366 |
| <60cc, petrol | Litres | 2.780486 | 2.464686 | 2.339861 | 2.234419 |
| >=60cc, electricity | Litres | 10.274472 | 9.176562 | 9.016553 | 8.908733 |
| >=60cc, petrol | Litres | 5.560973 | 4.929373 | 4.679723 | 4.468839 |
| PHEV (Diesel) - Diesel consumption | |||||
| 1350 - <1600 cc | Litres | 3.559435 | 3.15444 | 2.975047 | 2.820443 |
| 1600 - <2000 cc | Litres | 3.772587 | 3.343339 | 3.153204 | 2.989341 |
| 2000 - <3000 cc | Litres | 4.637931 | 4.110224 | 3.876476 | 3.675027 |
| <1350 cc | Litres | 3.69883 | 3.277974 | 3.091556 | 2.930897 |
| >=3000 cc | Litres | 5.144709 | 4.55934 | 4.300051 | 4.07659 |
| PHEV (Diesel) - Electricity consumption | |||||
| 1350 - <1600 cc | kWh | 10.494582 | 9.318347 | 8.914845 | 8.587779 |
| 1600 - <2000 cc | kWh | 11.498811 | 10.210022 | 9.767909 | 9.409545 |
| 2000 - <3000 cc | kWh | 13.014984 | 11.556262 | 11.055854 | 10.650239 |
| <1350 cc | kWh | 10.926543 | 9.701894 | 9.281784 | 8.941255 |
| >=3000 cc | kWh | 15.393328 | 13.668041 | 13.07619 | 12.596452 |
| PHEV (Petrol) - Electricity consumption | |||||
| 1350 - <1600 cc | kWh | 10.368145 | 9.206081 | 8.80744 | 8.484314 |
| 1600 - <2000 cc | kWh | 11.674262 | 10.365808 | 9.916949 | 9.553118 |
| 2000 - <3000 cc | kWh | 12.966913 | 11.513579 | 11.01502 | 10.610902 |
| <1350 cc | kWh | 10.018051 | 8.895226 | 8.510046 | 8.197831 |
| >=3000 cc | kWh | 15.511822 | 13.773254 | 13.176846 | 12.693416 |
| PHEV (Petrol) - Petrol consumption | |||||
| 1350 - <1600 cc | Litres | 3.387493 | 3.002062 | 2.831335 | 2.677686 |
| 1600 - <2000 cc | Litres | 3.81423 | 3.380243 | 3.188009 | 3.015005 |
| 2000 - <3000 cc | Litres | 4.236566 | 3.754527 | 3.541007 | 3.348846 |
| <1350 cc | Litres | 3.27311 | 2.900693 | 2.735731 | 2.587271 |
| >=3000 cc | Litres | 5.068042 | 4.491396 | 4.235971 | 4.006097 |
| Petrol hybrid vehicle | |||||
| 1350 - <1600 cc | Litres | 6.472917 | 5.736424 | 5.410194 | 5.116598 |
| 1600 - <2000 cc | Litres | 7.288337 | 6.459064 | 6.091738 | 5.761156 |
| 2000 - <3000 cc | Litres | 8.09535 | 7.174254 | 6.766255 | 6.39907 |
| <1350 cc | Litres | 6.254351 | 5.542726 | 5.227512 | 4.94383 |
| >=3000 cc | Litres | 9.684157 | 8.582286 | 8.094212 | 7.654962 |
| Petrol vehicle | |||||
| 1350 - <1600 cc | Litres | 8.199029 | 7.266137 | 6.852912 | 6.488903 |
| 1600 - <2000 cc | Litres | 9.231893 | 8.181481 | 7.716201 | 7.306336 |
| 2000 - <3000 cc | Litres | 10.25411 | 9.087389 | 8.57059 | 8.115342 |
| <1350 cc | Litres | 7.922178 | 7.020787 | 6.621515 | 6.269797 |
| >=3000 cc | Litres | 12.266598 | 10.870895 | 10.252669 | 9.708073 |
| Source: Te Manatū Waka Ministry of Transport Vehicle Fleet Emissions Model | |||||
Vehicle emissions per kilometre are calculated by combining real-world fuel consumption with fuel-specific emission factors expressed in carbon dioxide equivalent (CO₂-e):
\[ \begin{aligned} \text{emissions per km}~(\mathrm{kg~CO_2\text{-}e~km^{-1}}) &= \frac{ \text{fuel consumption}~(\mathrm{L~per~100~km}) \times \text{fuel emission factor}~(\mathrm{kg~CO_2\text{-}e~L^{-1}}) }{ 100 } \end{aligned} \]
Dividing by 100 gives a factor for litres (or kWh) per fuel per km. Use this with the fuel emission factors to calculate emissions per km.
Multiply the values for fuel consumption by the emission conversion factors in Table 3.3.
New Zealand Transport Agency vehicle registration data is unchanged from the 2022 guidance, where the average year of manufacture for the taxi fleet was 2012, and 2015 for the rental fleet1. We assumed a 2010–2015 fleet for taxis and post-2015 fleet for rental cars.
The taxi (regular) factor is derived from an average of the factors for a petrol, diesel, petrol plug-in hybrid and electric vehicle, for a 2000–3000 cc vehicle class. These workings are in Table 7.11.
| Vehicle | CC | Unit | CO₂/unit (kg CO₂-e) | CH₄/unit (kg CO₂-e) | N₂O/unit (kg CO₂-e) | Total kg CO₂-e/unit |
|---|---|---|---|---|---|---|
| Electric | 2000 - <3000 cc | km | 0.025523 | 0.00071 | 0.000049 | 0.026282 |
| Diesel | 2000 - <3000 cc | km | 0.2316 | 0.000347 | 0.003286 | 0.235233 |
| Petrol | 2000 - <3000 cc | km | 0.207476 | 0.002759 | 0.006329 | 0.216564 |
| Petrol hybrid | 2000 - <3000 cc | km | 0.163797 | 0.002178 | 0.004997 | 0.170972 |
| Taxi (regular) | Average | km | 0.157099 | 0.001498 | 0.003665 | 0.162263 |
TaxiCharge NZ Ltd advised that the current average price per kilometre in a taxi is $3.62. North Island’s average rate = $3.4, while South Island’s average = $3.99.
The calculation to develop the emission factors for taxi based by $ spend is:
\[ \begin{aligned} \text{emissions per \$ spend} &= \frac{ \text{emissions per km} }{ \text{average price per km} } \end{aligned} \]
The private car default is based on the average age of light passenger vehicles in the New Zealand fleet, back-calculated to the year of manufacture, with the fuel consumption factors in Table 7.12 applied.
According to Te Manatū Waka Ministry of Transport’s The New Zealand 2024 Vehicle Fleet: Data Spreadsheet2, the average age of light passenger vehicles in 2024 was 15.2 years. This corresponds to a 2009 year of manufacture.
| Engine type | Unit | Units per 100 km for a 2000–3000 cc engine |
|---|---|---|
| Petrol | Litres | 10.25411 |
| Diesel | Litres | 9.886218 |
| Petrol hybrid | Litres | 6.766255 |
| Diesel hybrid | Litres | 7.407278 |
| PHEV (Petrol) - Petrol consumption | Litres | 3.541007 |
| PHEV (Petrol) - Electricity consumption | kWh | 11.01502 |
| PHEV (Diesel) - Diesel consumption | Litres | 3.876476 |
| PHEV (Diesel) - Electricity consumption | kWh | 11.055854 |
| Electric | kWh | 23.108433 |
The default emission factor for rental cars is the same as for vehicles in the post-2015 1600–2000 cc category.
7.2.3 Assumptions, limitations and uncertainties
Emission factors from fuel are multiplied by real-world consumption rates for vehicles with different engine sizes. The uncertainties embodied in these figures carry through to the emission factors. For petrol vehicles, we multiplied the real-world consumption by ‘regular petrol’ emission factors from the fuel emission source category. This may overestimate emissions for some and underestimate emissions for others.
According to Te Manatū Waka Ministry of Transport’s The New Zealand 2024 Vehicle Fleet: Data Spreadsheet, the most common size of light passenger vehicle is between 2000 cc and 3000 cc. Therefore, the default emission factors (for vehicles of unknown engine size) are the same as for a <3000 cc vehicle.
The Vehicle Fleet Emissions Model contains uncertainties about the fuel consumption figures provided. Emission factors represent the average fuel consumption of vehicles operating in the real world under different driving conditions, across all vehicle types in that classification.
We assume there are no electric cars or hybrids in the pre-2010 fleet.
7.3 Public transport passenger travel
The emission factors for public transport for passenger travel on buses, trains and a ferry were provided by Auckland Transport. The unit used for these emission sources are passenger kilometres (pkm).
The national average for the bus factor is unchanged from the previous edition.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) | Uncertainties |
|---|---|---|---|---|---|---|
| Bus | ||||||
| Average Bus | pkm | 0.1545879756 | 0.1521743592 | 0.0002806001 | 0.0021330164 | Unknown |
| Diesel Bus | pkm | 0.1700575897 | 0.1674311876 | 0.0002509872 | 0.0023754149 | Unknown |
| Electric Bus | pkm | 0.020624096 | 0.0200535933 | 0.00053611 | 0.0000343928 | Unknown |
| Hydrogen Bus | pkm | 0.0371185712 | 0.0361255988 | 0.0009278171 | 0.0000651553 | Unknown |
| National Average for Bus | pkm | 0.155 | 0.153 | 0.000125 | 0.002125 | Unkown |
| Ferry | ||||||
| Ferry Average | pkm | 0.3462605439 | 0.3409128294 | 0.0005110444 | 0.0048366701 | Unknown |
| Rail | ||||||
| Metropolitan Average | pkm | 0.0268170819 | 0.0261757766 | 0.0005104428 | 0.0001308624 | Unknown |
| Metropolitan Diesel | pkm | 0.274856378 | 0.2706114432 | 0.0004056593 | 0.0038392755 | Unknown |
| Metropolitan Electric | pkm | 0.0202225932 | 0.0196770957 | 0.0005132286 | 0.0000322688 | Unknown |
7.3.1 GHG inventory development
To calculate public transport passenger emissions, collect data on the type of transport and distance travelled, and multiply this by the emission factors for each gas. Entities could conduct a staff travel survey to quantify these emissions.3
Applying the equation E = Q x F this means:
- E = emissions from the emissions source in kg CO2-e per year
- Q = distance travelled, by vehicle type (km)
- F = emission factors for correlating vehicle type, from Table 7.13.
7.3.1.1 PASSENGER BUS: EXAMPLE CALCULATION
An employee takes a return trip on an electric Wellington bus from the CBD to the airport (9.4 km each way). This happens five times in the reporting year.
Passenger kilometres travelled = 2 trips × 9.4 km x 5 times = 94 pkm
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 94 x 0.00053611 kg CO₂-e per pkm | 0.0504 kg CO₂-e |
| CO₂ emissions | 94 x 0.0200535933 kg CO₂-e per pkm | 1.89 kg CO₂-e |
| N₂O emissions | 94 x 0.0000343928 kg CO₂-e per pkm | 0.00323 kg CO₂-e |
| Total CO₂-e emissions | 94 x 0.020624096 kg CO₂-e per pkm | 1.94 kg CO₂-e |
Note: Numbers may not add due to rounding.
7.3.2 Emission factor derivation methodology
7.3.2.1 National average bus
To calculate the emission factor for national average bus travel we used the New Zealand Transport Agency passenger travel data Table 7.14 to estimate the national average loading capacity of seven people per bus.
| Region | Mode | Breakdown | 2020/21 |
|---|---|---|---|
| New Zealand | Bus | pkm | 534,976,704 |
| New Zealand | Bus | Service km | 122,934,050 |
The passenger loading per bus for the different regions for 2020/21 is shown in Table 7.15.
| Region | Unit | End Use |
|---|---|---|
| National average | Passenger/bus | 7 |
| Auckland | Passenger/bus | 7 |
| Bay of Plenty | Passenger/bus | 3 |
| Canterbury | Passenger/bus | Missing data |
| Gisborne | Passenger/bus | 8 |
| Hawkes Bay | Passenger/bus | 1 |
| Manawatū-Whanganui | Passenger/bus | 5 |
| Marlborough-Nelson-Tasman | Passenger/bus | 6 |
| Northland | Passenger/bus | 8 |
| Otago | Passenger/bus | Missing data |
| Southland | Passenger/bus | 3 |
| Taranaki | Passenger/bus | 12 |
| Waikato | Passenger/bus | 4 |
| Wellington | Passenger/bus | 20 |
We then divided the per kilometre emission factor for diesel buses in Table 7.14 by the national passenger/bus loading rate to give the emissions per gas, see Table 7.22.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Public Transport Vehicle | |||||
| Diesel bus: ≥ 12000 kg | km | 1.081684768 | 1.06497902 | 0.0015964537 | 0.0151092939 |
7.3.2.2 Auckland buses
To calculate the emissions from Auckland buses we used the most recent data available, which were from the year 2024. This information was from Auckland Transport.
Data for the electric and hydrogen buses are in Table 7.17. The distance travelled by electric and hydrogen buses for each 2023 quarter was multiplied by an estimated average bus power rating of 1.08 kWh and 5.76 kWh per kilometre respectively.4 The resultant energy consumption was multiplied by its respective quarterly electricity emission factor (including the transmission and distribution loss factor of electricity) to produce quarterly emissions totals. These totals were then divided by the quarterly totals for passenger kilometres travelled. The final emission factor is weighted based on the quarterly emissions totals and quarterly passenger kilometres travelled.
| Bus type | 2023/24 Quarter | Distance (km) | Fuel consumption rate (kWh/km) | Electricity consumption | pkm |
|---|---|---|---|---|---|
| Electric | Q1 | 1,816,925.055 | 1.083652 | 1,968,915.085638 | 8,769,389.589 |
| Electric | Q2 | 2,214,166.563 | 1.083652 | 2,399,386.774931 | 12,071,135.61 |
| Electric | Q3 | 2,011,190.4 | 1.083652 | 2,179,431.181134 | 13,121,883.46 |
| Electric | Q4 | 2,152,556.505 | 1.083652 | 2,332,622.891473 | 12,454,403.58 |
| Hydrogen | Q1 | 1,089.389 | 5.761427 | 6,276.434671 | 20,565.56657 |
| Hydrogen | Q2 | 1,226.141 | 5.761427 | 7,064.32127 | 20,056.62695 |
| Hydrogen | Q3 | 1,507.266 | 5.761427 | 8,684.002299 | 27,451.51811 |
| Hydrogen | Q4 | 2,045.531 | 5.761427 | 11,785.176543 | 34,286.74539 |
Data for the diesel buses are in Table 7.18. The annual distance travelled was multiplied by an estimated fuel efficiency of 0.457 litres per kilometre travelled.5The resultant energy consumption was multiplied by the diesel emission factor, to produce an annual emissions total. This total was then divided by the annual passenger kilometres travelled, to produce the final emission factor.
| Distance (km) | Fuel consumption rate (l/km) | Fuel consumption (litres) | pkm |
|---|---|---|---|
| 55,858,421.04 | 0.457388 | 25,548,975.392733 | 402,737,937 |
7.3.2.3 Auckland trains
To calculate the emissions from Auckland trains we used the most recent data available, which were from the year 2023/24 for electric trains. Diesel trains stopped operating in the region in August 2022. This information was from Auckland Transport.
Data for the electric and diesel trains are in Table 7.19. The diesel fuel used by diesel trains was multiplied by the diesel emission factor in Table 3.3 to produce an annual emissions total. This total was then divided by the annual passenger kilometres travelled, to produce the final emission factor.
The electricity used by electric trains for each year quarter, was multiplied by the respective quarterly electricity emission factors (including the transmission and distribution loss factor of electricity) to produce quarterly emissions totals. These totals were then divided by the quarterly totals for passenger kilometres travelled. The final emission factor is weighted based on the quarterly emissions totals and quarterly passenger kilometres travelled.
The diesel fuel used by diesel trains was multiplied by the diesel emission factor (in Table 3.3) to produce an annual emissions total. This total was then divided by the annual passenger kilometres travelled, to produce the final emission factor.
| Train type | Quarter/Year | Unit | Fuel consumption per unit | pkm |
|---|---|---|---|---|
| Electric | Sep-23 | kWh | 8,271,508 | 39,934,857 |
| Electric | Dec-23 | kWh | 7,447,841 | 38,607,309 |
| Electric | Mar-24 | kWh | 7,598,900 | 40,232,907 |
| Electric | Jun-24 | kWh | 7,717,790 | 44,101,512 |
| Diesel | 2021/22 | Litres | 443,997 | 4,330,313 |
The train average factor is weighted based on the emission factors for electric and diesel trains and the respective passenger kilometres travelled.
7.3.3 Auckland ferry
To calculate the emissions from ferry travel we used the most recent data available, which were from 2024. This information was from Auckland Transport and covers the 30 ferries operating in the Auckland region.
The annual distance travelled by diesel ferries over the 4 quaters was multiplied by an estimated average fuel consumption rate of 4.84 l/km to estimate the diesel used by public transport ferries in Auckland region.6 The diesel used was then multiplied by the diesel emission factor (in Table 3.3) to produce an annual emissions total. This total was then divided by the annual passenger kilometres travelled, to produce the final emission factor.
| Distance | Fuel consumption (litres) | pkm |
|---|---|---|
| 1,462,099 | 8,930,329 | 69,136,84 |
7.3.4 Assumptions, limitations and uncertainties
Limited data are available for areas outside the Auckland region.
These metro commuter rail emission factors are assumed to be appropriate for use on any commuter rail line in New Zealand.
7.4 Public transport vehicles
Public transport vehicle emissions include those from buses. Emissions are calculated for the whole vehicle. This approach is appropriate for transport operators or if a bus is chartered. Table 7.21 details these emission factors.
Buses: We calculated the emissions of different buses using Te Manatū Waka Ministry of Transport Vehicle Fleet Emissions Model data for fuel consumption in litres per 100 kilometres. The guide presents the data in emissions per kilometre.
The change in all-electric and PHEV vehicle emission factors is driven by the increase in the latest annual electricity factor, which is used to derive these emissions factors.
Table 7.21 details the data provided to calculate the emission conversion factors.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Public Transport Vehicle | |||||
| Diesel bus: 7500 – 12000 kg | km | 0.7804570209 | 0.7684034925 | 0.001151873 | 0.0109016554 |
| Diesel bus: < 7500 kg | km | 0.5634573521 | 0.5547552084 | 0.0008316042 | 0.0078705396 |
| Diesel bus: ≥ 12000 kg | km | 1.081684768 | 1.06497902 | 0.0015964537 | 0.0151092939 |
| Diesel hybrid bus: 7500 – 12000 kg | km | 0.5522890998 | 0.5437594407 | 0.000815121 | 0.0077145381 |
| Diesel hybrid bus: < 7500 kg | km | 0.3987296488 | 0.3925715914 | 0.0005884833 | 0.0055695741 |
| Diesel hybrid bus: ≥ 12000 kg | km | 0.7654524092 | 0.7536306149 | 0.0011297278 | 0.0106920665 |
| Electric bus: 7500 – 12000 kg | km | 0.0869461467 | 0.0844355091 | 0.0023476719 | 0.0001629657 |
| Electric bus: < 7500 kg | km | 0.0627714842 | 0.0609589088 | 0.001694921 | 0.0001176544 |
| Electric bus: ≥ 12000 kg | km | 0.1205041662 | 0.1170245147 | 0.0032537871 | 0.0002258644 |
7.4.1 GHG inventory development
To calculate public transport emissions, collect data on the type of transport and distance travelled, and multiply this by the emission factors for each gas.
Applying the equation E = Q x F this means:
- E = emissions from the emissions source in kg CO2-e per year
- Q = distance travelled, by vehicle type (km)
- F = emission factors for correlating vehicle type, from Table 7.21.
7.4.1.1 DIESEL BUS: EXAMPLE CALCULATION
An entity charters a diesel bus (<7,500 kg) to travel 500 km. The emissions would be:
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 500 x 0.0008316042 kg CO₂-e per km | 0.416 kg CO₂-e |
| CO₂ emissions | 500 x 0.5547552084 kg CO₂-e per km | 277 kg CO₂-e |
| N₂O emissions | 500 x 0.0078705396 kg CO₂-e per km | 3.94 kg CO₂-e |
| Total CO₂-e emissions | 500 x 0.5634573521 kg CO₂-e per km | 282 kg CO₂-e |
This result is for the entire bus.
Note: Numbers may not add due to rounding.
7.4.2 Emission factor derivation methodology
The average age of the bus fleet is 16.4 years (according to Te Manatū Waka Ministry of Transport fleet statistics). Therefore, we applied an average fuel consumption factor for a pre-2010 fleet to the bus fleet from the Vehicle Fleet Emissions Model.
| Emission source | Weight class | Unit | Pre-2010 units of energy per 100 km |
|---|---|---|---|
| Diesel bus | <7500 kg | Litre | 21.01919 |
| 7500 - 12000 kg | Litre | 29.114137 | |
| >=12000 kg | Litre | 40.351124 | |
| Diesel hybrid bus | <7500 kg | Litre | 14.874195 |
| 7500 - 12000 kg | Litre | 20.60257 | |
| >=12000 kg | Litre | 28.554405 | |
| Electric bus | <7500 kg | kWh | 57.689474 |
| 7500 - 12000 kg | kWh | 79.906944 | |
| >=12000 kg | kWh | 110.748089 |
Using the information in Table 7.22 and appropriate emission factor, the equation is:
\[ \mathrm{Emissions\ per\ km}\,(\mathrm{kg\ CO_2\text{-}e\ km^{-1}}) = \frac{ \mathrm{Energy\ use}\,(\mathrm{unit\ per\ 100\ km}) \times \mathrm{Emission\ factor}\,(\mathrm{kg\ CO_2\text{-}e\ unit^{-1}}) }{ 100 } \]
Where:
- fuel/energy consumption = units of energy per 100 km travelled (L for diesel/hybrid and kWh for electric)
- emission factor = the emission factor from Table 3.3 or Table 5.2
This allows you to use distance travelled as a unit for calculating emissions. If there are data on the quantity of fuel used, refer to transport fuel emission factors.
7.4.3 Assumptions, limitations and uncertainties
The Vehicle Fleet Emissions Model historical year results have been carefully calibrated to give a total road fuel use that matches MBIE’s road fuel sales figures. The sources used to develop these emission factors will have inbuilt assumptions, limitations and uncertainties. To investigate these, see the documents referenced.
7.5 Air travel
This section covers emission factors for domestic and international air travel for entities seeking to determine the emissions from business travel.
7.5.1 Domestic air travel
This section provides emission factors based on data from 2023. Domestic air travel is a common source of indirect (Scope 3) emissions for many New Zealand entities.
For air travel emission factors, multipliers or other corrections may be applied to account for the radiative forcing of emissions arising from aircraft transport at high altitude (jet aircraft). Radiative forcing helps entities account for the wider climate effects of aviation, including water vapour and indirect GHGs. This is an area of active research and uncertainty, aiming to express the relationship between emissions and the climate warming effects of aviation, but there is yet to be consensus on this aspect.
In this guidance, emission factors with a radiative forcing multiplier refers to the indirect climate change effects (non-CO₂ emissions eg, water vapour, contrails, NOx). Emission factors without a radiative forcing multiplier refers to the direct climate change effects (CO₂, CH₄ and N₂O). If multipliers are applied, entities should disclose the specific factor used including its source and produce comparable reporting. Therefore, avoid reporting with air travel conversion factors in one year and without in another year, as this may skew the interpretation of your reporting.
The decision to apply the Radiative Forcing Index, and to what type of air travel (flight altitude) should be guided by the requirements of your intended use and users.
In terms of the small and medium aircraft, a radiative forcing multiplier may not be required given the lower altitude at which these aircrafts typically fly. However, these emission factors are provided in the tables below for completeness, and for users wanting to take a conservative approach to their reporting.
Table 7.23 provides the emission factors without the radiative forcing multiplier applied. Table 7.24 provides emission factors with a radiative forcing multiplier of 1.7 applied.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Without Radiative Forcing factors | |||||
| Large aircraft | pkm | 0.1042303604 | 0.1034434268 | 0.000020252 | 0.0007666817 |
| Medium aircraft | pkm | 0.1198521492 | 0.1189472719 | 0.0000232873 | 0.00088159 |
| National average | pkm | 0.1146405571 | 0.1137750271 | 0.0000222747 | 0.0008432554 |
| Small aircraft | pkm | 0.3524624434 | 0.3405366516 | 0.0028841629 | 0.009041629 |
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| With Radiative Forcing factors | |||||
| Large aircraft | pkm | 0.1766407592 | 0.1758538256 | 0.000020252 | 0.0007666817 |
| Medium aircraft | pkm | 0.2031152396 | 0.2022103623 | 0.0000232873 | 0.00088159 |
| National average | pkm | 0.1942830761 | 0.193417546 | 0.0000222747 | 0.0008432554 |
| Small aircraft | pkm | 0.5908380995 | 0.5789123077 | 0.0028841629 | 0.009041629 |
We have provided a national average emission factor, and three factors based on the aircraft size: large, medium or small aircraft. A large aircraft in New Zealand would be an Airbus A320neo, A320ceo and A321neo. A medium aircraft has between 50 and 70 seats (ie, regional services on an ATR 72 or de Havilland Q300) and a small aircraft has fewer than 50 seats. If the aircraft type is unknown, we recommend using the national average.
7.5.1.1 GHG inventory development
To calculate emissions for domestic air travel, collect information on passengers flying, their departure and destination airports, flight length, travel class and, if practical, the type of aircraft. Your travel provider may be able to provide this information.
If the type of aircraft is unknown, use the national average emission factors. Calculate distances using online calculators such as www.airmilescalculator.com. Multiply the number of passengers by the distance travelled to obtain the pkm.
Applying the equation E = Q x F this means:
- E = emissions from the emissions source in kg CO2-e per year
- Q = passengers multiplied by distance flown (pkm)
- F = emission factors from Table 7.23 to Table 7.24
DOMESTIC AIR TRAVEL: EXAMPLE CALCULATION
An entity flies an employee on a return flight from Christchurch to Wellington (304 km each way). This happens five times in the reporting year on an aircraft of unknown size. The national average emission factor with radiative forcing is used.
Passenger kilometres travelled = (2 × 304) × 5 = 3,040 pkm
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 3,040 x 0.0000222747 kg CO₂-e per pkm | 0.0677 kg CO₂-e |
| CO₂ emissions | 3,040 x 0.193417546 kg CO₂-e per pkm | 588 kg CO₂-e |
| N₂O emissions | 3,040 x 0.0008432554 kg CO₂-e per pkm | 2.56 kg CO₂-e |
| Total CO₂-e emissions | 3,040 x 0.1942830761 kg CO₂-e per pkm | 591 kg CO₂-e |
Note: Numbers may not add due to rounding.
7.5.1.2 Emission factor derivation methodology
We developed emission factors for aircraft type with data from various data sources. We calculated an average emission factor for domestic air travel using data from the 2016, 2020 and 2023 calendar years.
An average emission factor has also been provided where the aircraft type is unknown (see Table 7.23 and Table 7.24). Entities that own aircraft could calculate emissions based on the fuel consumption data.
To calculate the emission factor, first calculate average fuel (kg) per flight for each aircraft:
\[ \begin{aligned} \frac{ \text{average total fuel used (kg)} }{ \text{average number of flights} } \end{aligned} \]
Then calculate average fuel (kg) per passenger:
\[ \begin{aligned} \frac{ \text{average total fuel (kg) per flight} }{ \text{average number of seats} \times 0.8 } \end{aligned} \]
Using this, next calculate fuel per passenger per km:
\[ \begin{aligned} \frac{ \text{average fuel (kg) per passenger} }{ \text{average flight distance (km)} } \end{aligned} \]
The density of kerosene (the assumed aviation fuel) is 0.79 kg/l.7
Emission factors for each aircraft were determined by multiplying the fuel (litres) per passenger per kilometre by the kerosene (aviation fuel) emission factor in Table 3.3
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) | Uncertainties |
|---|---|---|---|---|---|---|
| Without radiative forcing factors | ||||||
| Aerospatiale/Alenia ATR 72 | pkm | 0.1135302273 | 0.1126730802 | 0.0000220589 | 0.0008350882 | |
| Airbus A320 | pkm | 0.1105000756 | 0.109665806 | 0.0000214702 | 0.0008127995 | |
| Beechcraft Beech 1900D | pkm | 0.1790597259 | 0.1777078345 | 0.0000347913 | 0.0013171 | |
| British Aerospace Jetstream 32 | pkm | 0.2277260737 | 0.2260067541 | 0.0000442472 | 0.0016750724 | |
| Cessna Light Aircraft | pkm | 0.5298459145 | 0.5258456063 | 0.0001029491 | 0.0038973591 | |
| De Havilland Canada DHC–8–300 Dash 8/8Q | pkm | 0.2200666746 | 0.218405183 | 0.000042759 | 0.0016187326 | |
| FOKKER F50 | pkm | 0.0870854283 | 0.086427938 | 0.0000169207 | 0.0006405696 | |
| Pilatus PC–12 | pkm | 0.1806018705 | 0.1792383361 | 0.000035091 | 0.0013284435 | |
| Saab SF–340 | pkm | 0.0930101527 | 0.092307931 | 0.0000180719 | 0.0006841498 | |
Note: 2016 or 2020 data unless denoted otherwise. Airbus A320, Aerospatiale/Alenia ATR 72, De Havilland Q300 updated using 2023 data.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) | Uncertainties |
|---|---|---|---|---|---|---|
| With radiative forcing factors | ||||||
| Aerospatiale/Alenia ATR 72 | pkm | 0.1924013834 | 0.1915442363 | 0.0000220589 | 0.0008350882 | |
| Airbus A320 | pkm | 0.1872661398 | 0.1864318702 | 0.0000214702 | 0.0008127995 | |
| Beechcraft Beech 1900D | pkm | 0.30345521 | 0.3021033187 | 0.0000347913 | 0.0013171 | |
| British Aerospace Jetstream 32 | pkm | 0.3859308016 | 0.384211482 | 0.0000442472 | 0.0016750724 | |
| Cessna Light Aircraft | pkm | 0.8979378389 | 0.8939375307 | 0.0001029491 | 0.0038973591 | |
| De Havilland Canada DHC–8–300 Dash 8/8Q | pkm | 0.3729503027 | 0.3712888111 | 0.000042759 | 0.0016187326 | |
| FOKKER F50 | pkm | 0.147584985 | 0.1469274947 | 0.0000169207 | 0.0006405696 | |
| Pilatus PC–12 | pkm | 0.3060687057 | 0.3047051713 | 0.000035091 | 0.0013284435 | |
| Saab SF–340 | pkm | 0.1576257044 | 0.1569234827 | 0.0000180719 | 0.0006841498 | |
Note: 2016 or 2020 data unless denoted otherwise. Airbus A320, Aerospatiale/Alenia ATR 72 using 2023 data.
For situations where the aircraft type is unknown, average emission factors are also provided for a domestic average, and for large, medium and small aircraft (see Table 7.23 and Table 7.24).
We then calculated a weighted average emission factor for each size category, using the aircraft types within that size range. The weighted averages are calculated using the annual flight domestic distance travelled and the total number of domestic flights for each aircraft type. This method applies an equal weighting of 50 per cent to both distance travelled and number of flights.
- Large aircraft: A320neo, A320ceo and A321neo
- Medium aircraft: ATR 72 and Q300
- Small aircraft: British Aerospace Jetstream 32, Cessna Light Aircraft.
A national average emission factor was calculated using the same weighted average approach described above, this time considering the contribution each of the five large and medium aircraft types make to the overall distance travelled and number of flights.
7.5.1.3 Assumptions, limitations and uncertainties
We assume the fuel for domestic flights is kerosene (aviation fuel) and all the kerosene is combusted. The domestic emission factors are based on fuel delivery data. Therefore, it is not necessary to apply a distance uplift factor to account for delays/circling and non-direct routes (ie, not along the straight-line/great-circle between destinations). However, this should be considered for international air travel.
7.5.2 International air travel
The International air travel emission factors are sourced from the UK Greenhouse Gas Reporting: Conversion Factors 2022, published by the UK Department for Energy Security and Net Zero (DESNZ). These factors have remained unchanged in the 2023 and 2024 DESNZ editions, meaning they still reflect air travel data influenced by the COVID-19 pandemic. As a result, we continue to use the 2022 edition factors, which are based on pre-COVID air travel data which provides a more representative period for emissions reporting.
Because the DESNZ 2022 emission factors were developed using the GWP values from the AR4, the factors presented here have been converted to AR5 GWP values.
Entities wishing to report their international air travel emissions based on distance travelled per passenger could use the International Civil Aviation Organisation (ICAO) calculator. This calculator considers aircraft types and load factors for specific airline routes but does not apply the radiative forcing multiplier (accounting for the wider climate effect of emissions arising from aircraft transport at altitude) or distance uplift factor to account for delays/circling and non-direct routes (ie, not along the straight-line/great-circle between destinations). If using the ICAO calculator to calculate emissions for international air travel, multiply the output by 1.08 to account for the 8 per cent distance uplift factor (see Section 7.5.2.3) and then by 1.7 to apply a radiative forcing multiplier.
If you prefer not to use the ICAO calculator, we recommend the emission factors in Table 7.27 and Table 7.28. These emission factors follow those published online by the UK Department of Business, Energy and Industrial Strategy conversion factors (Conversion factors 2022: condensed set (for most users)) and include a distance uplift of 8 per cent and a radiative forcing multiplier of 1.7.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Without Radiative Forcing | |||||
| Long–haul (>3700km): Average passenger | pkm | 0.1019748913 | 0.10111 | 0.0000112 | 0.0008536913 |
| Long–haul (>3700km): Business class | pkm | 0.2264776349 | 0.22457 | 0.0000224 | 0.0018852349 |
| Long–haul (>3700km): Economy class | pkm | 0.0781003611 | 0.07744 | 0.0000112 | 0.0006491611 |
| Long–haul (>3700km): First class | pkm | 0.3123779369 | 0.30975 | 0.0000224 | 0.0026055369 |
| Long–haul (>3700km): Premium economy class | pkm | 0.1249516362 | 0.1239 | 0.0000112 | 0.0010404362 |
| Short–haul (<3700km): Average passenger | pkm | 0.0810870389 | 0.0804 | 0.0000112 | 0.0006758389 |
| Short–haul (<3700km): Business class | pkm | 0.1196371732 | 0.11863 | 0.0000112 | 0.0009959732 |
| Short–haul (<3700km): Economy class | pkm | 0.0797581463 | 0.07908 | 0.0000112 | 0.0006669463 |
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| With Radiative Forcing | |||||
| Long–haul (>3700km): Average passenger | pkm | 0.1929848913 | 0.19212 | 0.0000112 | 0.0008536913 |
| Long–haul (>3700km): Business class | pkm | 0.4285876349 | 0.42668 | 0.0000224 | 0.0018852349 |
| Long–haul (>3700km): Economy class | pkm | 0.1477903611 | 0.14713 | 0.0000112 | 0.0006491611 |
| Long–haul (>3700km): First class | pkm | 0.5911479369 | 0.58852 | 0.0000224 | 0.0026055369 |
| Long–haul (>3700km): Premium economy class | pkm | 0.2364616362 | 0.23541 | 0.0000112 | 0.0010404362 |
| Short–haul (<3700km): Average passenger | pkm | 0.1534470389 | 0.15276 | 0.0000112 | 0.0006758389 |
| Short–haul (<3700km): Business class | pkm | 0.2263971732 | 0.22539 | 0.0000112 | 0.0009959732 |
| Short–haul (<3700km): Economy class | pkm | 0.1509381463 | 0.15026 | 0.0000112 | 0.0006669463 |
The emission factors from the UK DESNZ are calculated regarding the indirect and direct climate change effects. For continuity in this guidance, we have categorised the international air travel emission factors by whether a radiative forcing multiplier was applied, as outlined in this section. Further information can be found in paragraphs 8.37 to 8.41 in the 2023 UK DESNZ Methodology Paper for Conversion Factors.
7.5.2.1 GHG inventory development
To calculate emissions for international air travel, collect information on passengers flying, their departure and destination airports, flight length, travel class and, if practical, the type of aircraft. Your travel provider may be able to provide this information. Information on flight distance will be required to determine whether the short- or long-haul factors should be used.
To calculate emissions for international air travel, gather the information on how far each passenger flew for each flight. Multiply this by the factors in Table 7.27 or Table 7.28. Use the specified emission factors for different cabin classes if information is available. If unknown, use the average emission factors.
Applying the equation E = Q x F this means:
- E = emissions from the emissions source in kg CO2-e per year
- Q = passengers multiplied by distance flown (pkm)
- F = appropriate emission factors from Table 7.27 or Table 7.28.
INTERNATIONAL AIR TRAVEL: EXAMPLE CALCULATION
An entity makes five flights from Auckland to Shanghai (9,346 km each way). On the first trip, two people flew return to Shanghai on the same flight in economy class. On the second trip, three people flew return to Shanghai and the cabin classes were not recorded. Long-haul (>3,700 km) emission factors with radiative forcing are used.
For the two people who travel economy class: Passenger kilometres travelled = (2 × 9,346) × 2 = 37,384 pkm
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 37,384 x 0.0000112 kg CO₂-e per pkm | 0.419 kg CO₂-e |
| CO₂ emissions | 37,384 x 0.14713 kg CO₂-e per pkm | 5,500 kg CO₂-e |
| N₂O emissions | 37,384 x 0.0006491611 kg CO₂-e per pkm | 24.3 kg CO₂-e |
| Total CO₂-e emissions | 37,384 x 0.1477903611 kg CO₂-e per pkm | 5,520 kg CO₂-e |
For the three people with unknown (average) travel classes: Passenger kilometres travelled = (3 × 9,346) × 2 = 56,076 pkm
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 56,076 x 0.0000112 kg CO₂-e per pkm | 0.628 kg CO₂-e |
| CO₂ emissions | 56,076 x 0.19212 kg CO₂-e per pkm | 10,800 kg CO₂-e |
| N₂O emissions | 56,076 x 0.0008536913 kg CO₂-e per pkm | 47.9 kg CO₂-e |
| Total CO₂-e emissions | 56,076 x 0.1929848913 kg CO₂-e per pkm | 10,800 kg CO₂-e |
Total CO2-e emissions from international air travel = 5,520 kg CO₂-e + 10,800 kg CO₂-e = 16,300 kg CO₂-e
Note: Numbers may not add due to rounding.
7.5.2.2 Emission factor derivation methodology
The 2023 UK DESNZ Methodology Paper for Conversion Factors publication discusses the methodology in more detail, including changes over time.
7.5.2.3 Assumptions, limitations and uncertainties
The emission factors in Table 7.27 and Table 7.28 are based on UK and European data. The short-haul emission factor applies to international flights of less than 3,700 km. The long-haul factor applies to flights of more than 3,700 km.
The UK DESNZ endorses a great circle distance uplift factor to account for non-direct (ie, not along the straight-line/great-circle between destinations) routes and delays/circling. The 8 percent uplift factor applied by UK DESNZ is based on the analysis of flights arriving and departing from the United Kingdom. This figure is likely to be overstated for international flights to/from New Zealand (initial estimates from Airways New Zealand suggest it is likely to be less than 5 per cent). In the absence of a New Zealand-specific figure for international flights, we recommend an 8 per cent uplift factor. This figure is comparable to an IPCC publication, Aviation and the Global Atmosphere (refer to section 8.2.2.3)8, which suggests for European flights the average flight distance is about 99 per cent to 1010 per cent greater than the actual flight track distance.
The emission factors refer to aviation’s direct GHG emissions including carbon dioxide, methane and nitrous oxide. There is currently uncertainty over the other climate change impacts of aviation (including water vapour and indirect GHGs, among other factors), which the IPCC estimated to be up to two to four times those of carbon dioxide alone. However, the science is currently uncertain and New Zealand’s Greenhouse Gas Inventory 1990−2023 does not use a multiplier.
International travel is divided by class of travel. Emissions vary by class because they are based on the number of people on a flight. Business class passengers use more space and facilities than economy class travellers. If everyone flew business class, fewer people could fit on the flight and therefore emissions per person would be higher.
7.6 Helicopters
This section provides emission factors for some commonly used helicopters in New Zealand. Business activities that require the use of helicopters might include entities involved in tourism, air transport, agricultural operations, or emergency services.
| Emissions Source | Unit | kg CO₂–e/unit | CO₂/unit (kg CO₂–e) | CH₄/unit (kg CO₂–e) | N₂O/unit (kg CO₂–e) |
|---|---|---|---|---|---|
| Helicopter | |||||
| Bell 206B | hours | 320.5909112 | 318.170467 | 0.0622908427 | 2.358153331 |
| Eurocopter AS 350B Squirrel | hours | 465.0289696 | 461.5180258 | 0.0903551703 | 3.420588592 |
| Eurocopter AS 350B3 Squirrel | hours | 481.1247858 | 477.4923194 | 0.0934825889 | 3.538983721 |
| Robinson R22 Beta | hours | 123.9417068 | 122.9771726 | 0.0248225722 | 0.9397116614 |
| Robinson R44 | hours | 179.0278644 | 177.6346408 | 0.0358550177 | 1.357368526 |
7.6.1 GHG inventory development
These emission factors can be used where the amount of fuel used is not known. Obtaining fuel data will provide a more accurate estimate of your carbon emissions. To calculate emissions from operating helicopters when only the number of operating hours is known.
Applying the equation E = Q x F this means:
- E = emissions from the emissions source in kg CO2-e per year
- Q = hours of operating time (hours)
- F = emission factors for correlating helicopter type, from Table 7.29.
7.6.1.1 HELICOPTER USE: EXAMPLE CALCULATION
An agricultural operation used a Eurocopter AS 350B Squirrel to apply topdressing and other spraying activities. They could not obtain data on the amount of fuel used, but had recorded 10 flying hours over a given year.
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| CH₄ emissions | 10 x 0.0903551703 kg CO₂-e per hours | 0.904 kg CO₂-e |
| CO₂ emissions | 10 x 461.5180258 kg CO₂-e per hours | 4,620 kg CO₂-e |
| N₂O emissions | 10 x 3.420588592 kg CO₂-e per hours | 34.2 kg CO₂-e |
| Total CO₂-e emissions | 10 x 465.0289696 kg CO₂-e per hours | 4,650 kg CO₂-e |
Note: Numbers may not add due to rounding.
7.6.2 Emission factor derivation methodology
These emission factors were derived from the Swiss Federal Office of Civil Aviation’s (FOCA) Guidance on the Determination of Helicopter Emissions. This contains air emissions data (non-GHG) for one hour of flying time, including fuel consumption, for a range of helicopter models.This contains air emissions data (non-GHG) for one hour of flying time, including fuel consumption, for a range of helicopter models.
The one-hour emissions values are used, which assume a combination of rotations and cruise per flight-hour.
The fuel consumption (provided in kgs) was converted to litres using assumed densities of 0.804 kg per litre and 0.69 kg per litre, for Jet A1 and aviation gas respectively. Turbine engine helicopters are assumed to use Jet A1 while piston helicopters are assumed to use aviation gas. We then applied the Jet A1 and aviation gas emission factors from Transport fuels section above to determine the emission factor for one hour of operation.
We used the aircraft register on the New Zealand Civil Aviation Authority (CAA) website9 to identify the most commonly registered helicopter models in the country.
7.6.3 Assumptions, limitations and uncertainties
Obtaining the amount of fuel used for helicopter activities would provide a more accurate estimate of carbon emissions, than using this emission factor which is based on operating hours.
A number of factors will influence the accuracy of this emission factor for a given operating hour, such as the cruising speed, the take-off and approach, and the way the helicopter is being used.
Finally, if your entity has a helicopter model that is not provided here, you may wish to choose the model that seems to be the best fit. However, this approach will have limitations, due to variations that include engine operating power, and the size and number of engines.
7.7 Accommodation
Accommodation is an indirect (Scope 3) emissions source associated with business travel. The emission factors for hotel stays have been updated using factors from the 2024 edition of the Cornell Hotel Sustainability Benchmarking Index (CHSB) Index,10 which provides data for the 2022 calendar year.
We obtained the emission factors from the M1 tab of the source spreadsheet, using the median values for all hotels. The factors are in CO2-e and are not available by gas type. For more information on the Cornell methodology, see the Hotel Sustainability Benchmarking Index 2024 guidance document.11
Note these emission factors are based on either AR4 or AR5 GWP values, depending on the country. The reason is some countries submit their emission factors to this study in terms of CO2-e, while other countries break it down into the three main GHG types. In the latter cases, the AR5 GWPs were applied.
The provision of these emission factors can be limited by the availability of data in different countries. If the factor for a certain country is not available in Table 7.30, we recommend using factors from a previous edition of this guidance.
The Cornell Hotel Sustainability Benchmarking Index has introduced a new hotel type classification, replacing the previous “All Hotels” group into separate “Resort” and “Non-Resort” categories, with the latter used to calculate the 2025 emissions factors. This had a significant impact, with the factors decreasing for 40 out of the 48 countries provided. 26 of these countries decreased by over 20%.
| Emissions Source | Unit | kg CO₂–e/unit |
|---|---|---|
| Hotel Stays | ||
| Argentina | Room per night | 15.32536591 |
| Australia | Room per night | 34.11941583 |
| Austria | Room per night | 10.0507584 |
| Bahrain | Room per night | 102.8526699 |
| Belgium | Room per night | 14.552063 |
| Brazil | Room per night | 6.757310062 |
| Canada | Room per night | 10.62474158 |
| Caribbean Region | Room per night | 43.77455914 |
| Chile | Room per night | 31.45942816 |
| China | Room per night | 58.30625072 |
| Colombia | Room per night | 16.27678951 |
| Costa Rica | Room per night | 5.631959026 |
| Czech Republic | Room per night | 20.79396066 |
| Egypt | Room per night | 51.80399693 |
| Finland | Room per night | 10.76387424 |
| France | Room per night | 7.208308927 |
| Germany | Room per night | 13.03291589 |
| Greece | Room per night | 26.14054121 |
| Hong Kong | Room per night | 79.27066469 |
| Hungary | Room per night | 22.22753295 |
| India | Room per night | 48.93327122 |
| Indonesia | Room per night | 52.31393587 |
| Italy | Room per night | 15.33321042 |
| Japan | Room per night | 37.39716278 |
| Jordan | Room per night | 63.32658195 |
| Kazakhstan | Room per night | 73.75667032 |
| Macau | Room per night | 130.3482989 |
| Malaysia | Room per night | 55.17545263 |
| Mexico | Room per night | 18.43939187 |
| Netherlands | Room per night | 15.56062372 |
| New Zealand | Room per night | 10.30784912 |
| Oman | Room per night | 76.39205262 |
| Panama | Room per night | 21.19874686 |
| Peru | Room per night | 16.31695679 |
| Philippines | Room per night | 55.76161689 |
| Poland | Room per night | 29.33200281 |
| Portugal | Room per night | 12.77550297 |
| Qatar | Room per night | 90.61959799 |
| Saudi Arabia | Room per night | 72.51266367 |
| Singapore | Room per night | 23.30541411 |
| South Africa | Room per night | 52.74867755 |
| South Korea | Room per night | 45.61996656 |
| Spain | Room per night | 11.51795365 |
| Switzerland | Room per night | 7.94082916 |
| Thailand | Room per night | 43.879308 |
| Turkey | Room per night | 32.6361285 |
| United Arab Emirates | Room per night | 54.72447283 |
| United Kingdom | Room per night | 10.37875541 |
| United States | Room per night | 14.23988937 |
| Vietnam | Room per night | 76.44083626 |
7.7.1 GHG inventory development
To calculate emissions from accommodation during business trips, collect data on the number of nights and the country stayed in.
Applying the equation E = Q x F this means:
- E = emissions from the emissions source in kg CO2-e per year
- Q = rooms per night
- F = emission factors for the country stayed in from Table 7.30.
7.7.1.1 ACCOMODATION: EXAMPLE CALCULATION
An entity sends six people to a conference in Australia. They book three rooms for four nights. 3 rooms x 4 nights = 12
| Gas | Calculation | Emissions (kg CO₂-e) |
|---|---|---|
| Total CO₂-e emissions | 12 x 34.11941583 kg CO₂-e per Room per night | 409 kg CO₂-e |
Note: Numbers may not add due to rounding.
7.7.2 Assumptions, limitations and uncertainties
The Hotel Sustainability Benchmarking Index 2024 guidance document outlines the limitations of the study. These include:
- it is skewed towards upmarket and chain hotels, meaning the data may not be representative of the entire hotel industry, particularly the economy and midscale segments
- the results do not distinguish a property’s facilities, except for outsourced laundry services, which are taken into consideration. This means it is difficult to compare two hotels because some may contain distinct attributes (such as restaurants, fitness centres and swimming pools) while others do not
- the data have not been independently verified by a third-party provider.
New Zealand Transport Agency: https://nzta.govt.nz/resources/new-zealand-motor-vehicle-register-statistics/new-zealand-vehicle-fleet-open-data-sets.↩︎
Te Manatū Waka Ministry of Transport: https://www.transport.govt.nz/statistics-and-insights/fleet-statistics/sheet/annual-fleet-statistics.↩︎
GHG Protocol Technical Guidance for Calculating Scope 3 Emissions: https://ghgprotocol.org/sites/default/files/standards_supporting/Chapter6.pdf.↩︎
These network average rates for Auckland were based on Auckland Transport’s GHG inventory of 2023/24.↩︎
The average fuel efficiency was based on Auckland Transport’s GHG inventory of 2023/24.↩︎
The average fuel efficiency was based on Auckland Transport’s GHG inventory of 2023/24.↩︎
https://archive.ipcc.ch/ipccreports/sres/aviation/121.htm#8223↩︎
https://www.aviation.govt.nz/aircraft/aircraft-registration/aircraft-register-search/.↩︎
https://ecommons.cornell.edu/items/85eddae3-2b5b-41fb-88ad-75a0b53f8424.↩︎