Overview
The European heavy-duty vehicle CO2 standards cover delivery trucks belonging to one of four vehicle groups, registered from the second half of 2019 onwards. The four vehicle groups include all rigid and tractor trucks with either 4×2 or 6×2 axle configurations that exceed 16 metric tonnes of maximum weight. Manufacturers are required to reduce the average CO2 emissions from new vehicle fleets by 15% in 2025 and by 30% in 2030, relative to a fixed baseline. The baseline is determined from the certified CO2 emissions of vehicles registered in the second half of 2019 and the first half of 2020. A recent policy update details the European heavy-duty vehicle CO2 standards.
Standard type
Fleet average CO2 emission limits
Regulating Body
European Union (European Commission, Parliament, Council, and Member States)
Current Standard
Applicability
Rigid and tractor trucks of categories N2 and N3, with an axle configuration of either 4×2 or 6×2, and a technically permissible maximum laden mass exceeding 16 tonnes.
History
The current CO2 emission standards for new heavy-duty vehicles are the first of their kind in the European Union. The CO2 standards proposal for heavy-duty vehicles was put forward by the European Commission in May 2018 as part of the third and final package of a series of regulatory proposals, called Europe on the Move. The regulation was formally adopted on 20 June 2019, with the regulation in the Official Journal of the European Union as Regulation (EU) 2019/1242.
The CO2 standards for heavy-duty vehicles rest on the base of two other important regulations: The CO2 certification regulation, adopted in December 2017 as Regulation (EU) 2017/2400, and the CO2 monitoring and reporting regulation, adopted in June 2018 as Regulation (EU) 2018/956.
Technical Standards
Scope
To regulate the CO2 emissions of heavy-duty trucks, the European Commission introduced a new segmentation for N2 and N3 freight vehicles. Regulation (EU) 2017/2400 defines the vehicle groups as the following:
Axle type | Chassis configuration | Maximum weight | Vehicle group |
---|---|---|---|
4×2 | Rigid | >3.5 – <7.5 tonnes | 0 |
Rigid/Tractor | 7.5 – 10 tonnes | 1 | |
Rigid/Tractor | >10 – 12 tonnes | 2 | |
Rigid/Tractor | >12 – 16 tonnes | 3 | |
Rigid | >16 tonnes | 4 | |
Tractor | >16 tonnes | 5 | |
4×4 | Rigid | 7.5 – 16 tonnes | 6 |
Rigid | >16 tonnes | 7 | |
Tractor | >16 tonnes | 8 | |
6×2 | Rigid | all weights | 9 |
Tractor | all weights | 10 | |
6×4 | Rigid | all weights | 11 |
Tractor | all weights | 12 | |
6×6 | Rigid | all weights | 13 |
Tractor | all weights | 14 | |
8×2 | Rigid | all weights | 15 |
8×4 | Rigid | all weights | 16 |
8×6/8 | Rigid | all weights | 17 |
The current CO2 emission standards for new heavy-duty vehicles apply to vehicle groups 4, 5, 9, and 10. This corresponds to all rigid and tractor trucks with a 4×2 axle configuration that exceed 16 metric tonnes of technically permissible maximum laden mass, and all rigid and tractor trucks with a 6×2 axle configuration. Vehicles not used for the delivery of goods, referred to as vocational vehicles, are excluded from the scope of the CO2 standards.
For the CO2 standards categorization, regulated vehicle groups are divided into sub-groups to account for their different use profiles, such as urban delivery (UD), regional delivery (RD), or long-haul (LH). The sub-group segmentation is based on the cabin type and by engine power:
Group description | Vehicle group | Vehicle sub-group | Cabin type | Engine power |
---|---|---|---|---|
Rigid, 4×2 axle, GVW > 16 tonnes |
4 | 4-UD | All | < 170 kW |
4-RD | Day cab | ≥ 170 kW | ||
Sleeper cab | ≥ 170 kW and < 265 kW |
|||
4-LH | Sleeper cab | ≥ 265 kW | ||
Tractor, 4×2 axle, GVW > 16 tonnes |
5 | 5-RD | Day cab | All |
Sleeper cab | < 265 kW | |||
5-LH | Sleeper cab | ≥ 265 kW | ||
Rigid, 6×2 axle | 9 | 9-RD | Day cab | All |
9-LH | Sleeper cab | |||
Tractor, 6×2 axle | 10 | 10-RD | Day cab | All |
10-LH | Sleeper cab |
Targets and implementation timeline
The CO2 standards set binding CO2 targets from 2025 onwards. The reduction targets are defined relative to a fixed baseline. The implementation timeline is divided into three periods, each with different regulatory stringencies:
Reporting periods | Mandated reduction | Notes |
---|---|---|
2019-2024 | No reduction mandated | Manufacturers can accumulate early credits in this period |
2025-2029 | Fleet average reduction of 15% from the baseline | – |
2030-onwards | Fleet average reduction of 30% from the baseline | The reduction target from 2030 onwards will be subject to review in 2022. |
For any given year, the reporting period includes vehicles registered from July 1 to June 30 of the following year.
Baseline
The baseline emissions are defined for each vehicle sub-group based on data resulting from the monitoring and reporting regulation (Regulation (EU) 2018/956) from July 1, 2019 to June 30, 2020 and are equal for all manufacturers. The baseline CO2 emissions for each sub-group will be made publicly available by the European Commission by April 30, 2021.
Metric
The CO2 standards follow a tank-to-wheel approach, addressing only the tailpipe CO2 emissions of regulated vehicle groups. For each manufacturer, the CO2 emissions are regulated on a fleet-wide basis through a metric dubbed average specific CO2 emissions, expressed in grams of CO2 per tonne-km (gCO2/t-km).
The average specific CO2 emissions of a manufacturer are a function of the certified CO2 emissions of each new heavy-duty vehicle over a combination of drive cycles and payloads, the number of vehicles registered in each sub-group, the mileage and payload weighting (MPW) factors, and the zero- and low-emission vehicle factor.
The CO2 certification procedure, Regulation (EU) 2017/2400, is the starting point for the determination of average specific CO2 emissions of a manufacturer. Depending on the vehicle group, the certification procedure provides the CO2 emissions over a set of different driving cycles, also called mission profiles, at both reference and low payloads. The reference and low payloads depend on the vehicle group and the mission profile. The CO2 standards regulation also establishes a set of weighting factors for the cycles and payloads to determine the CO2 emissions of each vehicle for the calculation of the average specific emissions of a manufacturer.
The mileage and payload weighting (MPW) factors are used to reflect the difference in freight activity between vehicle sub-groups. The MPW factor is defined as the product of the typical vehicle mileage and average payload in the sub-group, normalized by the freight activity of sub-group 5-LH, which has the highest freight activity:
Vehicle sub-group | Mission profile weighting | Payload weighting | MPW factor |
---|---|---|---|
4-UD | Urban Delivery: 100% | Low: 50% Reference: 50% |
0.099 |
4-RD | Regional Delivery: 90% Long Haul: 10% |
Low: 50% Reference: 50% |
0.154 |
4-LH | Regional Delivery: 10% Long Haul: 90% |
Low: 50% Reference: 50% |
0.453 |
5-RD | Regional Delivery: 90% Long Haul: 10% |
Low: 30% Reference: 70% |
0.498 |
5-LH | Regional Delivery: 10% Long Haul: 90% |
Low: 30% Reference: 70% |
1.000 |
9-RD | Regional Delivery: 90% Long Haul: 10% |
Low: 30% Reference: 70% |
0.286 |
9-LH | Regional Delivery: 10% Long Haul: 90% |
Low: 30% Reference: 70% |
0.901 |
10-RD | Regional Delivery: 90% Long Haul: 10% |
Low: 30% Reference: 70% |
0.434 |
10-LH | Regional Delivery: 10% Long Haul: 90% |
Low: 30% Reference: 70% |
0.922 |
Incentives for zero- and low-emission vehicles
The CO2 standards include incentives for accelerating the development and adoption of zero- and low-emission heavy-duty vehicles (ZEVs and LEVs). A vehicle is considered an LEV if its CO2 emissions are less than half of the baseline CO2 emissions of its respective sub-group.
The zero- and low-emission heavy-duty vehicles (ZLEV) incentives have two well-defined phases. From 2019 to 2024, a super-credit scheme was adopted. From 2025 onwards, a bonus-only benchmark applies.
The incentives are implemented via the ZLEV factor, which multiplies the average specific CO2 emissions of a manufacturer. The ZLEV factor is capped at a minimum of 0.97. That is, the ZLEV incentives can only reduce the average emissions of a manufacturer by a maximum of 3%. The two phases include the following details:
Super-credits phase (2019–2024)
In the super-credits phase, ZLEVs are counted as more than one vehicle in the calculation of the average CO2 emissions of a manufacturer. ZEVs, which are certified with 0 gCO2/km, are double counted in the averaging set. LEVs are counted as up to 2 vehicles, depending on their CO2 emissions. For example, a LEV with CO2 emissions 75% lower than the sub-group’s baseline would count as 1.5 vehicles.
Benchmark phase (2025 onwards)
In the benchmark phase, manufacturers are only rewarded by the sale of ZLEVs after a sales benchmark of 2% has been met. If the benchmark is not achieved, there are no negative consequences. LEVs count towards the benchmark with a value between 0 and 1, depending on their CO2 emissions. For example, a LEV with CO2 emissions 75% lower than the sub-group’s baseline would count as 0.5 in the ZLEV sales share calculation.
Compliance flexibilities
Manufacturers are allowed to accumulate CO2 emissions credits and debts during specific periods of time. The credit-debt accounting, expressed in gCO2/t-km, is proportional to the number of vehicle registrations under the scope of the regulation produced by the manufacturer. Credits and debts are not transferable between manufacturers.
Starting in 2019 and through 2024, manufacturers are allowed to accumulate early-credits. These early-credits are generated once the manufacturer’s average CO2 emissions are below a certain threshold, called the CO2 reduction trajectory, defined as a linear function between the baseline CO2 emissions and the 2025 emissions target. The early-credits can only be used for compliance in 2025 and are not valid thereafter. There are no implications if a manufacturer’s average CO2 emissions are above the CO2 reduction trajectory during this period, meaning no debt is accumulated.
From 2025 to 2029, manufacturers can generate credits if the manufacturer’s average CO2 emissions are below the linear CO2 reduction trajectory between the 2025 and 2030 emissions targets. During this period, manufacturers accumulate debt if their average CO2 emissions are above the respective CO2 target. If the average emissions of a manufacturer lie between the mandatory target and the CO2 reduction trajectory, neither credits nor debts are generated. Emissions credits can only be used for compliance up to 2029 and any emission debts must be resolved by then. From 2025 to 2029, if the accumulated debt exceeds a given threshold, the manufacturer is required to pay a per-vehicle penalty of €4,250 per vehicle for each gCO2/t-km of excess emissions.
Compliance in 2030 and thereafter is evaluated each year without the application of past credits or accumulated debt. Excess CO2 emissions above the target would result in immediate financial penalties. From 2030 onwards, the penalty amounts to €6,800 per vehicle for each gCO2/t-km of excess emissions. Extending the credit-debt scheme to the post-2030 period, including the immediate financial penalties, will be reassessed in the 2022 regulation review:
Reporting periods | Credit/debt system | Penalty |
---|---|---|
2019-2024 | Early credits can be accrued. Debt cannot be accrued. |
None |
2025-2029 | Early credits can be used. Credits can be accrued. Debt can be accrued. |
4,250 Euros per-vehicle for each gCO2/t-km of excess emissions |
2030-onwards | None. To be reviewed by 2022. |
6,800 Euros per-vehicle for each gCO2/t-km of excess emissions |
CO2 certification procedure
Due to the existing diversity of configurations in the heavy-duty sector and the associated testing efforts, carrying out CO2 certifications in the same fashion as passenger and light commercial vehicles is not viable. A simulation-based approach has therefore been selected for the determination of both the CO2 emissions and fuel consumption of HDVs.
The backbone of the CO2 emissions and fuel consumption certification procedure is the Vehicle Energy Consumption Calculation Tool (VECTO), a publicly available, open source, downloadable, and executable software. The CO2 certification regulation establishes the input parameters to the simulation tool and also outlines the details for performance data measurement of vehicle components with significant impacts on the CO2 emissions and fuel consumption of heavy-duty vehicles. The current components to be tested, forming VECTO’s input data, are shown in the table below. They are also detailed here:
Component / subsystem | Parameters required by the certification methodology |
---|---|
Engine | Displacement, idle speed, fuel consumption map, full load torque curve, motoring friction curve, brake-specific fuel consumption over the Worldwide Harmonized Transient and Stationary Cycles (WHTC and WHSC) |
Transmission | Transmission type, gear ratios, torque loss map as a function of torque and speed for each gear, maximum torque and speed per gear |
Torque converter | Torque ratio as a function of the speed ratio and the input torque |
Angle drive | Torque loss map as a function of input torque and speed |
Retarder | Braking torque as a function of the input speed to the retarder |
Axle | Axle ratio and torque loss map as a function of torque and speed |
Aerodynamic drag | Air drag area corrected to zero yaw angle as calculated by the VECTO Air Drag Tool |
Tires | Tire dimensions, rolling resistance coefficient, load applied during the rolling resistance test |
Auxiliaries | Technology used for the following auxiliary components: Cooling fan, steering system, electric system, pneumatic system, air conditioning system, and power take off |
Vehicle | Curb vehicle weight, GVW rating, axle configuration, retarder type, angle drive type, power take off type |
VECTO is currently being expanded to also include vans, buses, and hybrid and electric vehicles. The set of input data required for VECTO certification is, therefore, expected to expand in the future.
Links
Regulatory documents
- HDV CO2 standards, Regulation (EU) 2019/1242
- HDV CO2 certification procedure, Regulation (EU) 2017/2400
- HDV CO2 monitoring and reporting, Regulation (EU) 2018/956
Additional resources
- European Commission’s Regulatory Impact Assessment
- ICCT Policy Update on HDV CO2 standards
- ICCT Policy Update on HDV CO2 certification