Assessing Canada's 2025 passenger vehicle greenhouse gas standards: Technology deployment and costs
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WORKING PAPER 2018-23 Assessing Canada’s 2025 passenger vehicle greenhouse gas standards: Technology deployment and costs Authors: Francisco Posada, Aaron Isenstadt, Ben Sharpe, and John German Date: September 2018 Keywords: Passenger vehicle efficiency technologies, manufacturing costs, consumer benefits, climate benefits, U.S. EPA OMEGA model Background The ICCT analysis uses the U.S. Envi- Results of OMEGA modeling ronmental Protection Agency’s Opti- This paper is part of a series that of the Canadian LDV fleet mization Model for Reducing Emis- reports on an analysis done by the This paper presents the core results of sions of G reenhouse Gases from ICCT of Canada-specific technol- Automobiles (OMEGA) version 1.4.56, the ICCT analysis: the projected tech- ogy pathways, costs, and benefits updated most recently to support the nology deployment in the Canadian of Canada’s 2025 passenger vehicle technical assessment for the midterm vehicle fleet, with associated per-vehi- greenhouse gas standards, as final- review (U.S. Environmental Protection cle costs, by car and truck class and ized in 2014 (Regulations Amending Agency [EPA], National Highway Traf- by vehicle type. (See Appendix I for a the Passenger Automobile and Light fic Safety Administration [NHTSA], brief description of the technologies.) Truck Greenhouse Gas Emission Reg- and California Air Resources Board ulations, 2014). The analysis compares [CARB], 2016). The model evaluates Two scenarios were studied: main- the standards presently in force to the relative costs and effectiveness taining GHG 2025 targets for MY following the Trump Administration’s (CO2 emission reduction) of vehicle 2021–2025 vehicles, and freezing GHG proposal to roll back the 2025 U.S. technologies and applies them to a standards at 2020 targets, beginning fuel economy and greenhouse gas defined baseline vehicle fleet to meet with MY 2021. In the first, technology emissions standards. a specified CO2 emissions target. projections and costs were calculated for a Canadian LDV fleet that follows Such a comparison is relevant For a detailed discussion of the Cana- the GHG 2025 standards. The second because Canada’s passenger vehicle dian baseline vehicle fleet defined presents a Canadian LDV fleet that fuel efficiency regulation is structured for this project, a description of the harmonizes with the U.S. MY 2021– in such a way as to tie Canada’s stan- OMEGA model and the inputs to the 2025 targets frozen at 2020 levels. dards directly to the U.S. regulation. If C anada-specific analysis , and an Canada maintains its regulatory sta- evaluation of consumer benefits and The analysis shown here illustrates the tus quo, its light-duty vehicle (LDV) social/environmental benefits of the projected least-cost technology path- greenhouse gas standards will auto- two regulatory alternatives, see the way toward compliance. Manufactur- matically retreat to whatever level is other papers in this series (Posada, ers may choose other compliance the final outcome of the U.S. rulemak- Isenstadt, Sharpe, & German, 2018a, pathways—including shifting their ing process initiated in August 2018. 2018b, 2018c). product mix to vehicles of larger or © INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION, 2018 WWW.THEICCT.ORG
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS smaller size than those currently sold, Canada fleet average technology penetration or promoting SUV sales over compact 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% cars—depending on marketing strate- Turbo-downsizing gies, fuel price variations, local condi- Non-hybrid Atkinson tions and consumer preferences, and further technology development. Gasoline direct injection Stop-start TECHNOLOGY DEPLOYMENT Cylinder deactivation Mild hybrid Figures 1, 2, and 3 show the Canadian fleet-wide shift in technology market Full hybrid adoption rates from the baseline (CY Battery Electric 2016) for a selected group of technol- >6-speed ogies under the scenarios considered. Figure 1 compares the technology ICCT: CY16 baseline EPA: CY16 baseline ICCT: MY20 EPA: MY20 projections using EPA’s technology- to MY25 to MY25 cost curves as defined in the midterm Figure 1. Comparison of projected Canadian LDV fleet average changes in technology review evaluation and the projections penetration under EPA cost-effectiveness assumptions (brown lines), and under ICCT’s using ICCT’s updated technology- cost-effectiveness assumptions (blue lines). Baseline (CY 2016) data shown as line start cost curves. points; MY 2025 values shown as line arrowheads; MY 2020 values shown as dots. As the figure illustrates, most tech- Can & US fleet average technology penetration-EPA OMEGA Input nologies progress in the same direction 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% under both ICCT and EPA technology Turbo-downsizing assumptions, although to varying lev- els of penetration. Notable exceptions Non-hybrid Atkinson are turbo-downsizing, stop-start, and Gasoline direct injection mild hybrids. These three technolo- Stop-start gies are expected to increase in mar- ket share under EPA assumptions, but Cylinder deactivation decrease or remain stagnant under Mild hybrid ICCT assumptions. This is due, in part, Full hybrid to ICCT assigning greater cost-effec- Battery Electric tiveness of non-hybrid (naturally aspi- rated), Atkinson-cycle engines with >6-speed cooled exhaust gas recirculation (EGR). Can: CY16 baseline US: MY15 baseline Can: MY20 US: MY20 to MY25 to MY25 The OMEGA model does not consider performance factors that consumers Figure 2. Comparison of estimated technology adoption rates in Canada (blue) and the weigh when purchasing a new vehi- U.S. (brown) under EPA cost-effectiveness inputs. Baseline (CY 2016 or MY 2015) data are cle. Since turbocharged engines have shown as line start points; MY 2025 values are line arrowheads; MY 2020 values are dots. higher torque at lower engine speeds suggesting that there is ample room United States under EPA cost assump- than naturally aspirated engines, con- in Canada’s baseline fleet for down- tions. Figure 3 shows the same com- sumers who favor forced induction sizing engines. parison under ICCT cost assump- may be willing to pay more for turbo- charged engines. This consumer pref- tions. As noted in our description of The differing projections from ICCT erence is not factored into the OMEGA the baseline fleet used in this project and EPA inputs indicate that there are model, which projects that naturally (Posada et al., 2018a), the Canadian many possible ways in which automak- aspirated engines will be the least baseline fleet is comprised of MY ers can both meet GHG standards and expensive path to compliance under 2016 and MY 2017 vehicles, whereas consumer performance expectations. ICCT’s technology assumptions. Only the U.S. baseline fleet is comprised 27% of 6-cylinder engines and 4% of Figure 2 compares the C anadian of MY 2015 vehicles. Consequently, 8-cylinder engines are turbocharged, market projections with those of the some of the Canadian baseline 2 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION WORKING PAPER 2018-23
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS vehicles already have more efficient Can & US fleet average technology penetration-ICCT OMEGA Input technology than their counterparts 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% in the U.S. baseline. This difference Turbo-downsizing may have a small impact in the final Non-hybrid Atkinson projections, most likely toward lower costs for Canada. Gasoline direct injection Stop-start The trends in Figures 2 and 3 mir- ror one another: the U.S. estimated Cylinder deactivation technology update and related cost- Mild hybrid effectiveness work just as well in Can- Full hybrid ada. In general, technology adoption Battery Electric rates increase as CO2 targets become more challenging for manufacturers >6-speed to meet. Can: CY16 baseline US: MY15 baseline Can: MY20 US: MY20 The model estimates that almost all to MY25 to MY25 vehicles (> 97%) are going to receive l e a s t- c o s t t e c h n o l o g y o p t i o n s , Figure 3. Comparison of estimated technology adoption rates in Canada (blue) and the such as low-rolling resistance tires, U.S. (brown) under ICCT cost-effectiveness inputs. Baseline (CY 2016 or MY 2015) data improvements to engine friction, are shown as line start points; MY 2025 values are arrowheads; MY2020 values are dots. electrification of accessories, and (15%–20% market share) and a much more predominant in the model run aerodynamic improvements. lesser role for full-hybrid and bat- using ICCT inputs (Figure 3), as this Across all projections, the 2020 target tery-electric technologies. The ICCT relatively new technology is open- would require only modest improve- update of those pathways (Figure 3) ing up a low-cost option to achieve ments in technology with respect to results in little hybridization of any higher efficiency.1 Lutsey et al. (2017) the Canadian CY 2016 baseline. This kind, due primarily to the lower costs discuss how the costs and benefits of would be achieved with least-cost and higher benefits forecasted for Atkinson-cycle engines are estimated. technology options, as listed above, conventional technologies. and with improvements in transmis- Stop-start systems sions. A small increase in GDI adoption Turbocharged and downsized GDI engines and high-compression As shown in Figures 2 and 3, stop-start is also projected. When compared to Atkinson-cycle engines already enjoys greater market share in GHG 2025 targets, this unambitious Canada’s baseline than in the United technology shift would be reflected A look at the projected fleet wide States. The U.S. baseline has about as small increases in cost and as small, market share (Figures 2 and 3) shows 9.8% of models with stop-start. The fleet-wide benefits of avoided CO2. that the large majority of naturally Canadian baseline, which is slightly aspirated engines are projected to be The OMEGA model also projects that newer, has around 16% of models with replaced by high-compression, Atkin- for the average vehicle, most of the stop-start. Thus, the greater market son-cycle engines or by turbocharged efficiency gains are expected to be and downsized GDI engines to com- share in Canada is due to the more realized by improvements to conven- ply with 2025 targets. recent and advanced Canadian base- tional technologies, with very little line fleet, as well as some consumer market uptake required for more High-compression Atkinson-cycle preference for vehicles that happen to advanced powertrains, such as those engines (e.g., Mazda’s Skyactiv or Toy- in full hybrids and electric vehicles. ota’s Dynamic Force gasoline engines) 1 The actual future product mix may be In the 2025 time frame, EPA’s tech- are projected to gain a large market affected by possible consumer preferences for the performance of turbocharged nology pathways (Figure 2) lead share across Canada’s fleet. Note engines, which the OMEGA model does not to some 48 volt mild-hybridization that this type of engine technology is account for. WORKING PAPER 2018-23 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION 3
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS have stop-start. Using EPA inputs, the Table 1. Level of mass reduction/lightweighting in the OMEGA model’s GHG 2025 stop-start market share is expected projections for Canada and the United States, using both ICCT and EPA technology cost- to increase nearly 75% by 2025 and benefit inputs. Baseline masses shown for reference. make up 28% of the overall fleet. Using Canada US ICCT inputs, however, stop-start mar- Cars 6.1% 6.0% ket share is expected to decrease EPA Inputs Trucks 9.0% 10.2% about 10% by 2025. Again, the ranges of cost-effectiveness of various tech- Fleet 7.6% 8.0% nologies leads to different projected Cars 6.4% 6.4% outcomes by 2025. But these differ- ICCT Inputs Trucks 10.2% 11.5% ences signal a wide variety of paths Fleet 8.4% 8.8% manufacturers can choose from in Cars 1,480 (-2.6%) 1,520 order to comply with the standards. Baseline Mass (kg) Trucks 2,010 (-0.8%) 2,026 Fleet 1,757 (+1.2%) 1,736 Cylinder deactivation Cylinder deactivation promises to be a to the electrical system. Combined, estimated to provide a 5%–7% reduc- very cost-effective technology in gen- these effects can dramatically reduce tion in CO2 emissions. And reducing eral, but especially for large engines urban driving fuel consumption. EPA mass with design optimization and that automakers cannot or will not inputs predict that mild hybrids will some material substitution can lead downsize. At low engine loads, deac- occupy 17% of the market by 2025. to net cost savings. Lightweighting tivating cylinders allows the engine to ICCT inputs, on the other hand, show results are tabulated in Table 1. The run as though it were a much smaller fleet-wide compliance without the use results of the OMEGA modeling are engine, saving fuel. EPA’s technology of any mild hybrids. The difference in included for comparison. inputs assumed that these engines projected outcomes is due to ICCT’s would have a fixed bank of cylinders assumptions that improvements in Under both ICCT and EPA assumptions, that would be deactivated. But with conventional combustion technolo- the Canadian fleet requires slightly more recent technology that allows gies—like those discussed above—will less lightweighting than the U.S. fleet. for dynamic cylinder deactivation, the be more cost-effective than those Part of this slight difference is due to number and timing of cylinders deac- used in EPA’s assumptions. the Canadian baseline vehicles’ lower tivated is flexible and variable. This masses (curb weights). The average dynamic control extends the engine’s Electric vehicles Canadian car in the CY 2016 baseline operating range and further increases is 2.6% lighter than the U.S. car in its Regardless of the technology cost its effectiveness. The market share of MY 2015 baseline. The average truck assumptions, Figures 2 and 3 illustrate cylinder deactivation is expected to is 0.8% lighter in Canada than in the that battery-electric vehicles play little, grow from about 11% in 2016 to around United States. The estimated fleet-wide if any, role in meeting the GHG 2025 47% by 2025. average weight reduction in Canada is standards in Canada, as well as in the 7.5%–8.5% in 2025. United States. The standards simply do 48V mild hybrids not require widespread uptake of EVs. The 48V mild hybrid offers roughly Should national-level and local-level COST PER VEHICLE governments desire broad adoption half of the benefits of a full hybrid at When using the ICCT cost-benefit of electric vehicles, additional strate- only a third of the cost. These vehicles estimates, meeting the 2025 stan- gies and incentives would be required permit acceleration assist and turbo dards costs, on average, $865 (2015 beyond the CO2 standards. lag reduction, both of which could CAD, $651 USD) more per vehicle prove attractive to the Canadian fleet, than meeting the 2020 standards. which, as of CY 2016, is more than Lightweighting The costs are higher when using EPA 25% turbocharged. Mild hybrids also Though not shown in the preced- cost-benefit estimates , at $1 , 368 enable more robust stop-start, regen- ing figures, lightweighting, or weight ($1,029 USD) more per vehicle for erative braking, engine downspeed- reduction, is an extremely cost-effec- meeting the 2020 standards. Table ing, sailing, and shifting the burden tive technology for reducing CO2 emis- 2 summarizes the results. The sum- of some accessories from the engine sions. Every 10% reduction in weight is maries include direct manufacturing 4 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION WORKING PAPER 2018-23
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS costs, or the added costs incurred by Table 2. Estimated total costs for the Canadian fleet to meet the 2025 standards manufacturers to meet the standards, compared to the costs of meeting the 2020 standards (2015 CAD). as well as indirect costs, including Costs to meet 2025 Costs to meet 2020 Difference overhead, marketing, distribution, standards in 2025 standards in 2025 (2025 vs 2020) warranty, and profit. Cars $1,542 $331 $1,211 EPA inputs Trucks $1,972 $461 $1,511 Figure 4 compares the total costs incurred by individual manufacturers Fleet $1,766 $399 $1,368 on a fleet-wide basis for the Cana- Cars $1,045 $260 $784 dian fleet, under both ICCT’s assump- ICCT inputs Trucks $1,308 $369 $938 tions and EPA’s more conservative Fleet $1,183 $318 $865 assumptions. The story is much the same under The average compliance costs shown In general, the total costs for Cana- ICCT technology cost-effectiveness in Figures 5 and 6 are, in Canada, dian manufacturers are quite similar to inputs, plotted in Figure 6. Six differ- within 2% of the average costs in the those incurred by the same manufac- ent manufacturers experience slightly United States. The slight differences turers in the United States, as shown higher compliance costs per vehicle in stem largely from the differences in in Figures 5 and 6. Figure 5 shows that Canada than in the United States, but baseline fleet technology penetra- six automakers have slightly higher the majority see a cost decrease. The tion and relative share of cars and costs of compliance in Canada than in full fleet is estimated to cost about $8 trucks, which have different compli- the United States. Most see a decrease more per vehicle in Canada than in the ance costs. The difference in manu- in fleet-average costs, while the entire United States. As expected, the over- facturer car-truck split between the GHG emissions program is estimated all program cost is much lower under two countries also suggests com- to cost $28 less per vehicle in Canada the ICCT technology assumptions pliance costs will dif fer for each than in the United States. than under those from the EPA. manufacturer. $3,000 Cost to meet 2025 standards incremental to 2020 (2015 CAD) Canada Combined - EPA Canada Combined - ICCT $2,500 $2,000 $1,500 $1,368 $1,000 $865 $500 $0 BMW Ford Honda JLR Mercedes Nissan Tesla Volkswagen Fleet FCA GM Hyundai/ Mazda Mitsubishi Subaru Toyota Volvo Kia Figure 4. Comparison of manufacturer fleet-average total costs to meet the 2025 standards in Canada under ICCT (dark) and EPA (light) technology inputs compared to meeting the 2020 standards. WORKING PAPER 2018-23 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION 5
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS $3,000 Cost to meet 2025 standards incremental to 2020 (2015 CAD) US Combined - EPA Canada Combined - EPA $2,500 $2,000 $1,500 $1,396 $1,368 $1,000 $500 $0 BMW Ford Honda JLR Mercedes Nissan Tesla Volkswagen Fleet FCA GM Hyundai/ Mazda Mitsubishi Subaru Toyota Volvo Kia Figure 5. Comparison of manufacturer total costs to meet the 2025 standards in the United States (yellow) and in Canada (blue) under EPA’s technology cost-effectiveness inputs when compared to meeting the 2020 standards. $1,400 Cost to meet 2025 standards incremental to 2020 (2015 CAD) US Combined - ICCT Canada Combined - ICCT $1,200 $1,000 $857 $865 $800 $600 $400 $200 $0 BMW Ford Honda JLR Mercedes Nissan Tesla Volkswagen Fleet FCA GM Hyundai/ Mazda Mitsubishi Subaru Toyota Volvo Kia Figure 6. Comparison of manufacturer total costs to meet the 2025 standards in the United States (yellow) and in Canada (blue) under ICCT’s technology cost-effectiveness inputs when compared to meeting the 2020 standards. 6 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION WORKING PAPER 2018-23
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS SUMMARY OF TECHNOLOGY Table 3. Technologies and costs (2015 CAD) needed to meet the 2025 GHG standards for DEPLOYMENT AND COST PER the Canadian fleet. VEHICLE DISCUSSION Area Technology EPA inputs ICCT inputs Table 3 summarizes the costs and High compression ratio Atkinson/Miller 23.9% 61.8% technologies required to meet the Advanced Turbocharged and downsized 39.3% 15.1% 2025 standards in Canada by MY combustion Cylinder deactivation 46.1% 48.3% 2025. Both EPA and ICCT inputs lead Non-hybrid and non-electric 80.8% 97.8% to the straightforward conclusion that improvements to conventional pow- Mild hybrid 17.2% 0.0% Hybrid ertrains make up the vast majority of Full hybrid 1.2% 1.2% technology required to meet the GHG Plug-in hybrid electric 0.3% 0.3% Electric standards in 2025. Such improve- Battery electric 0.5% 0.7% ments—termed “advanced combus- Incremental technology cost from 2020 standards $1,368 $865 tion” in Table 3—include Atkinson- Incremental technology cost from Baseline (CY2016) $1,766 $1,183 cycle and Miller-cycle engines, cylinder deactivation, turbo-downsizing, and combustion engines (81% under EPA Unit costs decrease as manufacturers a suite of technologies that allow cost assumptions and 98% under ICCT refine their production processes, use more precise control over engine and cost assumptions). less expensive materials, and simplify transmission operation. Furthermore, or improve component parts. When automakers have recently announced Although the GHG 2025 standards the standards of the combined mar- plans for additional advanced com- by themselves will not significantly ket first splits in MY 2021, it is pos- bustion efficiency technologies that increase the number of zero-emission sible that the rate at which unit costs were not incorporated into either vehicles (ZEVs), ZEVs can help Canada decrease will slow due to less produc- EPA’s or ICCT’s inputs to the OMEGA achieve this goal. The ZEV standard in tion volume. model. 2 Although electrification and Québec serves as an example of man- full hybridization are not necessary datory requirements for automakers The ICCT made use of the individual to comply with Canada’s 2025 GHG to sell or lease a minimum number of technology cost reduction-by-learn- standards, the popularity of plug-in ZEVs per year. ing curves developed by EPA and hybrids and fully electric vehicles will estimated the cost impact assuming likely grow as battery technology potential volume sales reductions improves and costs decline. Many Technology cost impact driven by a bifurcated North Ameri- automakers have publicly committed and sensitivity analysis of a can market. Those technology cost- to offering fully electric vehicles. Such bifurcated market learning curves were developed by commitments serve as further indica- EPA for the 2012 and the 2016 regu- tion that manufacturers have many A bifurcated LDV market in North America would occur if Canada main- latory impact assessment analysis possible pathways in which to improve (EPA, NHTSA, CARB, 2016), and were the efficiency of their fleets and meet tained its 2025 targets, along with California and the Section 177 states, adopted for all the technology cost future GHG emissions standards. analysis included in the OMEGA model. while the remainder of the U.S. mar- ket kept GHG targets at 2020 levels For instance, the EPA estimates that Note that engines can have several out to 2025. Under this scenario, in 2020, non-hybrid, Atkinson-cycle advanced combustion technologies, approximately 40% of the combined engines and cylinder deactivation will as well as some level of hybridization Canadian-U.S. market would be sub- fall to about 90% of their cost the year or electrification. Very little hybridiza- ject to 2025 targets by MY 2025, and they were first introduced—a 10% cost tion is required to meet GHG 2025 standards. They can be met with the remaining 60% would be covered reduction by learning. By 2025, the a fleet that is comprised mainly of under 2020 targets until MY 2025. cost of those two technologies will non-electric vehicles with advanced have fallen to about 85% of their origi- The cost impacts of such a market were nal costs—a 15% reduction by learning 2 For example, Mazda will introduce a gasoline estimated by looking at the changes (see Appendix II). Similarly, EPA esti- compression ignition engine in 2019, FCA’s in production volumes and adoption mates that by 2020, stop-start costs 2019 RAM pickup has a 48v hybrid system rates for key fuel-efficiency technolo- will fall to about 75% of their original standard on the base V6 engine, and Infiniti’s 2019 QX50 has a variable compression ratio, gies. The cost of producing technolo- value and, by 2025, drop to about turbocharged engine. gies decreases as volume increases. 64% of their original value. WORKING PAPER 2018-23 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION 7
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS To assess the impact of Canada’s fleet EC 2012 EPA inputs ICCT inputs $3,000 belonging to a smaller market with a slower production volume rate, the $2,602 ICCT estimated the cumulative pro- Average per vehicle costs (2015 $CAD) $2,500 duction rate of technology adoption $2,222 for 2020 and 2025, and then esti- mated how the slower production $1,969 $1,972 $2,000 would affect the incremental cost $1,766 of the technology. Each technology $1,542 exhibits a particular cost impact for $1,500 $1,308 changes in production rates because $1,183 each technology has different levels $1,045 of complexity and is currently at dif- $1,000 ferent levels of market adoption levels. For example, stop-start costs, which, $500 under the full-learning rate would reach about 64% of original cost by 2025, could fall to 70% of the original $0 cost under a slower learning rate. This Cars Trucks Average LDV corresponds to a 9.2% increase in cost for stop-start in a split market. See Figure 7. Comparison of 2012 Environment Canada (EC) estimated manufacturer total appendix II for further details, along costs (corrected to 2015 CAD) to the updated EPA’s and ICCT’s technology cost- effectiveness inputs. with a sensitivity analysis under higher and lower rates of learning. Even under the (highly unrealistic) estimated by EC staff as $1,856 CAD worst case, in which technology costs for cars, $2,453 CAD for trucks, and Assuming that the learning rates no longer decrease after MY 2020, the $2,095 CAD for the average Canadian decelerate according to the market average 2025 per-vehicle technology LDV (Regulations Amending the Pas- split, under a 60% reduction in learn- cost would only be about 8% higher senger Automobile and Light Truck ing rate (i.e., only 40% of the market than under full-scale learning. See Greenhouse Gas Emission Regula- requires additional technologies) the appendix II for further details. tions, 2012). Figure 7 compares these majority of technologies experience original 2012 costs with the cost values a cost increase of 3% to 5%. Averag- found in this analysis. Note that the ing the percent increases, weighted Comparison to Environment original EC 2012 values, in 2011 CAD, by estimated 2025 market share (fig- Canada’s 2012 technology were corrected for inflation and con- ure 1) leads to an overall cost increase of 4.7%–4.9% , or $41–$67 (based cost assessment verted to 2015 CAD (CPI = 1.0608). 3 on Table 3). The reason costs are I n D e ce m b e r 2 01 2 , Enviro n m e nt Improved technology cost-effective- affected so marginally if the market Canada staff presented the results of ness inputs have significantly reduced splits is that the most important tech- a technical analysis supporting the the estimated cost of compliance with nologies to meet the 2025 targets are proposal for harmonization with EPA’s the MY 2025 standards in Canada. The well-known, broadly applied improve- GHG rule covering MY 2017–2025, and 2016 EPA cost-effectiveness inputs ments to conventional vehicles. consistent with the authority set by bring EC’s 2012 costs down by about the Canadian Environmental Protec- 21% on average. When compared to A sensitivity analysis was applied to tion Act of 1999. The impact assess- the most cost-effective inputs from assess the impact of potential market ment team used the 2012 version of the ICCT analysis, the EC 2012 costs size variations on technology costs. the OMEGA model to estimate the dip more than 47%. The market sizes were defined as cost to comply for vehicles sold in retaining the GHG 2025 targets, and Canada. The total incremental cost, 3 Bank of Canada, Inflation calculator. Accessed were evaluated from 0% to 100% of in 2011 CAD, to comply with the MY on Sep 4th, 2018. https://www.bankofcanada. the total North American market. 2025 targets (from MY 2016) was ca/rates/related/inflation-calculator/ 8 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION WORKING PAPER 2018-23
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS Appendix I Vehicle efficiency technologies Table 4. Technologies projected by the OMEGA model. Source: (EPA, NHTSA, CARB, 2016). Technology Code Description Turbocharging increases the specific power level, allowing a reduced engine size while maintaining performance. The OMEGA model considers three levels of boosting, 18-bar brake mean effective pressure (BMEP), 24-bar BMEP and 27-bar BMEP, as well as four levels of TDS 18 / downsizing, from four cylinders (I4) to smaller I4 or I3, from V6 to I4 and from V8 to V6 and Turbocharging and TDS 24 / I4. Cooled EGR is also used for the 24-bar and 27-bar systems and the 27-bar system uses a downsizing TDS 27 2-stage turbocharger. An 18-bar BMEP is applied with 33 percent downsizing, 24-bar BMEP is applied with 50 percent downsizing and 27-bar BMEP is applied with 56 percent downsizing. In addition to the efficiency benefits, turbocharging improves performance, especially in steep and high-altitude conditions. Gasoline direct injection injects fuel at high pressure directly into the combustion chamber. This provides evaporative cooling of the air/fuel charge within the cylinder, which allows for Gasoline direct injection DI higher compression ratios and increased thermodynamic efficiency. GDI is generally paired with TDS to further support engine downsizing for improved efficiency. A conventional AT is optimized by adding additional gears, which reduces gear ratio spacing and increases the overall gear ratio spread. This enables the engine to operate more efficiently Automatic transmissions AT6 / AT8 over a broader range of vehicle operating conditions, with options for six and eight gears. In addition to the efficiency benefits, the higher number of gears improves performance, especially in steep and high-altitude conditions. Improvements to MTs include six-speed manual transmissions, offering an additional gear Manual transmission MT ratio, often with a higher overdrive gear ratio, compared to the baseline five-speed manual transmission. DCTs are similar in construction to a manual transmission, but the vehicle’s computer controls Advanced transmissions DCT6 / shifting and launch functions, instead of the driver. A dual-clutch automated shift manual and dual clutch DCT8 transmission uses separate clutches for even-numbered and odd-numbered gears, so the next transmission expected gear is pre-selected, which allows for faster, smoother shifting. Diesel engines have good fuel-efficiency due to reduced pumping losses and a combustion cycle that operates at a high compression ratio, with a very lean air-fuel mixture. This Advanced diesel DSL technology requires the addition of relatively costly emissions control equipment, including NOx after-treatment and diesel particulate filters (DPFs). Also known as idle-stop or 12V micro-hybrid and commonly implemented as a 12-volt, belt- driven integrated starter-generator, this is the most basic hybrid system that facilitates idle- Start-stop system, 12 V SS stop capability. This system replaces a common alternator with an enhanced power starter- alternator, both belt-driven, and a revised accessory drive system. MHEVs provide regenerative braking and acceleration assist capacity, in addition to idle-stop capability. A higher voltage battery is used, 48 V, with increased energy capacity compared to Mild-hybrid electric baseline automotive batteries. The higher voltage allows the use of a smaller, more powerful MHEV vehicle electric motor and reduces the weight of the motor, inverter, and battery wiring harnesses. This system replaces a standard alternator with an enhanced power, higher voltage, higher efficiency, belt-driven starter. The battery capacity is smaller compared to HEV batteries. A full hybrid vehicle has larger capacity electric motors and batteries, enabling higher rates of Hybrid electric vehicle HEV regenerative braking energy and acceleration assist, as well as limited operation on the electric motor alone. An example of a hybrid vehicle is the Toyota Prius. PHEVs are hybrid electric vehicles with the means to charge their battery packs from an Plug-in hybrid electric outside source of electricity (usually the electric grid). These vehicles have larger battery packs PHEV vehicle than non-plug-in hybrid electric vehicles with more energy storage and a greater capability to be discharged. EVs are vehicles with all drive and other systems powered by energy-optimized batteries Electric vehicle EV charged primarily from grid electricity. EVs with 75-mile, 100-mile and 150-mile ranges have been included as potential technologies by the OMEGA model. The second generation of low rolling resistance tires further reduce frictional losses associated Low-rolling resistance with the energy dissipated in the deformation of the tires under load, compared to the now LRRT2 tires common LRRT available on baseline vehicles. LRRTs tend to be stiffer than conventional tires, giving them more resistance to rough roads. WORKING PAPER 2018-23 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION 9
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS Includes continuous improvement in seals, bearings and clutches, super finishing of gearbox High-efficiency gearbox HEG parts, and development in the area of lubrication, all aimed at reducing frictional and other parasitic load in the system for an automatic, DCT or manual type transmission Second-generation improved accessories include high-efficiency alternators, electrically driven (i.e., on-demand) water pumps and cooling systems and alternator regenerative braking. This Improved accessories IACC2 excludes other electrical accessories such as electric oil pumps and electrically driven air conditioner compressors. The second generation of components to reduce engine friction includes low-tension piston rings, roller cam followers, improved material coatings, more optimal thermal management, Engine friction reduction EFR2 piston surface treatments, and other improvements in the design of engine components and subsystems that improve engine operation. Adopted with boost, cooled EGR increases the exhaust-gas recirculation rate used in the Cooled exhaust gas EGR combustion process to increase thermal efficiency and reduce pumping losses. Levels of recirculation exhaust gas recirculation approach 25% by volume in the highly boosted engines modeled. Reducing the aerodynamic drag of a vehicle reduces fuel consumption. The OMEGA model considers two levels of aerodynamic improvements. The first one considers changes to vehicle shape, which is constrained primarily by design considerations and should have zero Active aerodynamics AERO implementation cost. The second option covers active aerodynamics technologies. One example of active aerodynamic technologies is active grill-shutters. Active grill shutters close off the area behind the front grill under highway driving conditions, reducing the vehicle aerodynamic drag and thus, fuel consumption. An Atkinson-cycle engine trades off decreased power for increased efficiency. Essentially, the intake valve remains open for a longer duration on the intake stroke and closes during the normal compression stroke. This results in an effective compression ratio that is less than the expansion ratio during the power stroke, and increases the geometric compression ratio. High compression ATK This allows more work to be extracted per volume of fuel as compared to a typical Otto-cycle Atkinson-cycle engine engine. However, due to a smaller amount of trapped air mass (a consequence of air being forced out of the cylinder through the intake valve early in the compression stroke), the power density in the Atkinson cycle is lower than that of the Otto cycle. Increasing the compression ratio can partially compensate for this drawback. Vehicle weight reduction, also referred to as lightweighting, reduces the energy needed to overcome inertial forces, thus yielding lower fuel consumption and GHG emissions. Weight reduction WR Lightweighting was modeled in OMEGA assuming per-vehicle changes of 0%, 5%, 10%, 15% and 20%. The maximum, 20%, was applied only to 2025 vehicles. 10 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION WORKING PAPER 2018-23
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS Appendix II Potential Percentage of original direct manufacturing cost 100% technology cost effects of a 90% 4.9% 3.6% bifurcated North American 80% ATK, DEAC 11.3% market: Discussion 9.2% TDS, GDI, 70% transmissions, If Canada, California, and the Section MHEV-Non-batt 60% MHEV-batt 177 U.S. states maintain the GHG stan- SS dards unchanged, approximately 40% 50% of the combined Canadian-U.S. mar- ket would be subject to 2025 targets, 40% while 60% would remain under the 30% 2020 target through MY 2025. 2020 20% 2025 In this situation, it is possible that 2025 reduced learning rate 10% rates of decrease in unit production reduced learning rate costs will slow, due to slowed accu- 0% mulated production volume. Typically, Time from base direct manufacturing cost (illustrative) as cumulative production volumes increase, unit costs decrease as manu- Figure 8. Full learning rates and reduced learning rates of fuel-efficiency technologies facturers learn to improve processes, Table 5. Percent increase in technology cost due to a North American market split use less expensive materials, and sim- plify or improve component parts. Percent OMEGA estimated OMEGA estimated Generally, the newer the technology, change in 2025 penetration, 2025 penetration, the lower the cumulative production, Technology cost in 2025 EPA assumptions ICCT assumptions and the less experience manufactur- Turbo-downsizing 3.6% 39.3% 15.1% ers have with it. Atkinson cycle 4.9% 23.0% 61.8% GDI 3.6% 67.9% 80.8% Through numerous studies contained Stop-start 9.2% 28.3% 14.3% in, and since, the initial 2012 rulemak- Cylinder deactivation 4.9% 46.1% 48.3% ing for the U.S. 2017–2025 greenhouse gas standards, the EPA refined its MHEV* 6.4% 17.2% 0.0% learning curves and where technolo- Transmissions 3.6% 92.8% 92.3% gies lie on these curves (EPA, NHTSA, Mass reduction 5.8% 7.6% MR fleet-wide 8.4% MR fleet-wide CARB, 2016). Weighted average cost change 4.9% 4.7% Figure 8 illustrates this concept with * MHEV costs are a weighted average of battery and non-battery component costs. (EPA, NHTSA, CARB 2016) estimates battery costs to be 36% of total MHEV costs. key f u e l - ef f icie n c y te ch n olo gies required to meet the 2025 targets. The Several technologies are located on their original value by 2020 and drop solid blue curve represents a technol- the curves based on EPA’s assumed to about 64% of their original value ogy that is already fully learned out by rate of learning. For instance, EPA by 2025. manufacturers. The cost in the year it is introduced (100%) does not change estimates that, in 2020, non-hybrid, As the figure shows, manufacturers dramatically over many years, and it Atkinson-cycle engines and cylinder have significant experience with a decreases by about 1.5% annually. The deactivation will fall on the blue curve majority of technologies, and these solid brown curve illustrates a tech- at about 90% of their original cost. By technologies fall on the blue line. nology that undergoes more learn- 2025, the cost of these two technolo- ing after its introduction. Its costs gies will have fallen to about 85% of The dotted blue and brown lines illus- decrease rapidly at first, then the rate their original costs. Similarly, on the trate how the learning curves shift of decrease slows to about the same brown curve, EPA estimates that stop- assuming production volume in a rate as a fully learned technology. start costs will fall to about 75% of bifurcated market is reduced to 40% WORKING PAPER 2018-23 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION 11
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS of full learning rates (solid lines). The 18% dotted lines decrease at a rate 40% as SS Percent increase in 2025 estiamted cost 16% fast as the solid lines, indicating the MHEV rate of production volume accumula- 14% WR,
ASSESSING CANADA’S 2025 PASSENGER VEHICLE GREENHOUSE GAS STANDARDS: TECHNOLOGY DEPLOYMENT AND COSTS References Posada, F., Isenstadt, A., Sharpe, B., & German, J. (2018c). Assessing Canada’s 2025 passenger vehicle green- Lutsey, N., Meszler, D., Isenstadt, A., German, J., & Miller, J. house gas standards: Benefits analysis >>>. Retrieved (2017). Efficiency technology and cost assessment for U.S. from the International Council on Clean Trans- 2025–2030 light-duty vehicles. Retrieved from the Interna- portation http://www.theicct.org/publications/ tional Council on Clean Transportation https://www.theicct. canada-2025-cafe-standards-benefits-201809. org/publications/US-2030-technology-cost-assessment Regulations Amending the Passenger Automobile and Light Posada, F., Isenstadt, A., Sharpe, B., & German, J. (2018a). Truck Greenhouse Gas Emission Regulations, Canada Assessing Canada’s 2025 passenger vehicle green- Gazette, Vol. 146, No. 49, December 8, 2012, http://www. house gas standards: Characteristics of the Canadian gazette.gc.ca/rp-pr/p1/2012/2012-12-08/html/reg1-eng.html fleet. Retrieved from the International Council on Clean Transportation http://www.theicct.org/publications/ Regulations Amending the Passenger Automobile and Light canada-2025-cafe-standards-fleet-201809. Truck Greenhouse Gas Emission Regulations. Vol. 148, No. 21. Ottawa, ON, Canada Gazette, Part II. September 18, 2014. Posada, F., Isenstadt, A., Sharpe, B., & German, J. (2018b). http://www.gazette.gc.ca/rp-pr/p2/2014/2014-10-08/html/ Assessing Canada’s 2025 passenger vehicle greenhouse sor-dors207-eng.html gas standards: Methodology and OMEGA model descrip- tion. Retrieved from the International Council on Clean U.S. Environmental Protection Agency, National Highway Transportation http://www.theicct.org/publications/ Traffic Safety Administration, & California Air Resources canada-2025-cafe-standards-methods-201809. Board, “Draft Technical Assessment Report: Midterm Evaluation of Light-Duty Vehicle Greenhouse Gas Emis- sion Standards and Corporate Average Fuel Economy Standards for Model Years 2022-2025” (2016), https:// www.epa.gov/regulations-emissions-vehicles-and-engines/ midterm-evaluation-light-duty-vehicle-greenhouse-gas#TAR WORKING PAPER 2018-23 INTERNATIONAL COUNCIL ON CLEAN TRANSPORTATION 13
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