Category: Transportation and Climate Blog

Supporting California’s Move to Zero-Emission Vehicles: Creating a Viable, Large-Scale Fuel-Cell Vehicle and Hydrogen System

Hydrogen station

Photo: Adapted from Scharfsinn86 / Adobe Stock.

California is marching ahead with firm rules now in place for both light-duty and medium/heavy-duty vehicles to transition to zero emission stock by 2045. The State is requiring that all new vehicles sold from 2035 onward be “zero-emission vehicles” (ZEVs)—battery electric, plug-in hybrid, or hydrogen-powered fuel-cell vehicles. While battery electric vehicles currently dominate ZEV sales and discussions of the zero-emissions future, fuel-cell vehicles are expected to play a key role, especially in truck and bus fleets and some households. They offer a different set of strengths, such as extended driving ranges, fast refueling, and potentially greater payloads for trucks.

But creating an economically viable hydrogen system and scaling it up to meet 2035 targets will require massive investments over the next decade. While many initial investments have been made, there is no clear overarching strategy for what a full hydrogen system and supply chain infrastructure might look like in 5, 10, or 20 years. Some kind of system will be needed, given the projected needs of various sectors (transportation, industry, and buildings) and the need for low-cost renewable hydrogen to contribute to the goal of carbon neutrality by 2045 in California. Acknowledging the urgency of the moment, the state recently formed the ARCHES partnership to develop this system further.

For the past two years, a team at UC Davis has been working on the California Hydrogen Analysis Project to investigate potential future hydrogen systems and to assist in planning them through modeling. The current results of the project are described in detail in our full report. We modeled potential demands for hydrogen across sectors (with a focus on transportation), potential types and locations of hydrogen supply, and how hydrogen could be moved and stored between supply and demand locationss. We also analyzed the transportation sector, the electricity sector, and supply chains from production to end-use.

Our study has many findings across the various hydrogen sectors. Here are a few of the key findings and related policy recommendations.

Key findings

  • Transportation can lead hydrogen developments. California’s hydrogen system will need to be driven by growth in hydrogen demand from various end uses, and this growth can be led by transportation (especially by medium/heavy-duty road vehicles). By 2030 we estimate that road transportation, if properly incentivized, could create a hydrogen demand on the order of 500 metric tons per day. This should be sufficient to support development of a hydrogen production and distribution system that would be large enough to benefit from economies of scale.
  • Transportation is scalable. Rapid and incremental sales and adoption of light-duty and medium/heavy-duty fuel-cell vehicles, fostered by supply and demand-based incentives, can be supported by parallel growth of infrastructure to produce and distribute hydrogen. The decentralized nature of a transportation-focused approach can help to develop a regional hydrogen production/distribution network that can then be scaled with more stations and eventually other “offtakers”—i.e., end-users who contract to purchase hydrogen fuel when produced.
  • Strong early investment is needed. In the early years of developing hydrogen systems for transportation, many refueling stations will be needed to ensure adequate coverage so drivers can reliably find fuel as they travel. This can mean generally low utilization of stations and challenging station economics that may require policies to ensure profitability. The Low Carbon Fuel Standard (LCFS) credit systems, the Inflation Reduction Act (IRA) renewable hydrogen production cost credit, and other incentives can help. But the most important solution is to support investments in areas such as refueling stations and fleet vehicle purchases, which will quickly increase transportation demand.
  • On-going rapid scale-up should occur after 2030. Then, with lower hydrogen costs and prices available, the market should be able to further scale in a profitable manner to reach much higher fuel-cell vehicle shares and hydrogen demand. If fuel-cell vehicles succeed in growing to about 10% of light-duty vehicle shares and 25% of truck shares by 2045, hydrogen demand could be 10 times higher than in 2030, and refueling station numbers could eventually reach many hundreds or even thousands in California, depending on average station sizes.
  • Liquid hydrogen may play an important role. Currently all hydrogen is produced, stored, and moved as a compressed gas; but cryogenic liquid hydrogen may play an important role, especially for refueling large, long-haul trucks. Liquid hydrogen production/storage/station systems have significant advantages given their fuel density and potential for faster dispensing (even into gaseous storage on vehicles), particularly for vehicles, such as heavy-duty trucks, with a lot of hydrogen storage.

Policy Recommendations

The analysis has led to a wide range of findings and conclusions. Some of the most important are policy recommendations for the California Energy Commission and other agencies and stakeholders to consider. These include:

  • Set a new vision for 2030/2035. Work with other agencies and ARCHES to create a clearer vision for the fuel-cell vehicle and hydrogen market in California for the 2030-2035 timeframe, with specific targets for vehicles, fuel, and infrastructure. Align investments in all areas to grow all elements of the system in parallel.
  • Create new fuel-cell vehicle support systems. For example, the state should link incentives and rebates for fuel-cell vehicle purchases to their incremental costs over diesel vehicles, at least for the next 5 years, until market scale can be achieved. This could also be adopted for battery electric vehicles, to keep the system technology-neutral.
  • Build more and larger stations oriented to heavy-duty vehicles. The state should fund a minimum hydrogen station infrastructure to 2030 with increased emphasis on heavy-duty trucks and some stations (such as highway rest stops) that can provide for both light-duty vehicles and all types of trucks. For heavy-duty trucks, at least 50 high-volume stations (each with a capacity of around 10 tons/day) will be needed by 2030 to support a system of several thousand trucks. Larger and potentially more profitable stations are also needed. Defining these levels is key. The ARCHES partnership is developing targets and specific roll-out plans that state agencies should coordinate with and build upon.
  • Find Champion Fleets. Within the Advanced Clean Fleets policy system, find champion fleets to help support major uptake of specific numbers and types of trucks to ensure demand that aligns with a roll-out of hydrogen stations and supply growth to serve these vehicles.
  • Create a data/tracking system for fuel-cell vehicles and hydrogen systems as they develop and grow, to ensure that investments are aligned and the system is functioning as planned for all stakeholders. This system must be kept up to date with annual statistics on numbers and types of vehicles, their usage and performance, refueling infrastructure characteristics and performance, and a range of other information considered important to fleets and policy makers. This database should be publicly available and well supported by the state.

In summary, a hydrogen production and distribution system that serves the growth of fuel-cell vehicles and other end-uses in California will be key to slowing climate change. It should be both feasible and eventually cost-effective, but navigating growth over the next few years will be key. We will continue our research to support planning and informed policymaking.

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For more the full report that this blog is based on and information on the ongoing hydrogen research at ITS-Davis, click here and here.

Lew Fulton is the Director of Sustainable Transportation Energy Pathways Plus.

Cutting US road sector GHG emissions by 90% or more by 2050 takes both ZEVs and low-carbon fuels

Big reductions in greenhouse gas (GHG) emissions from the transportation sector are needed to limit the magnitude of climate change impacts. Understanding what kinds of policy and market dynamics are at play can help us meet national goals. Our recent study shows that there is an interplay between policy, vehicle types, and fuel sources, and that early investment in zero-emission vehicles (ZEVs) could yield big savings and big reductions in GHG emissions, by 2050. Low-carbon fuels for non-electric vehicles will also need to play an important role.

While the United States has not formally adopted long term targets for the sales of ZEVs, including battery electric, plug-in hybrid, and fuel cell vehicles, the Biden administration is a 50% sales share of light-duty ZEVs by 2030 and the US EPA has issued a proposed rule intended to slightly exceed this target.

California is leading the transition with nearly 20% ZEV market share in 2023, and with the most ambitious rules requiring a full transition of LDV sales to ZEV by 2035 and trucks to ZEV by 2040. Many states are following. So far, 16 states have committed to adopting the California LDV ZEV program, and at least 16 have signed the Multi-State Medium- and Heavy-Duty Zero Emission Vehicle MOU. If the Biden administration adopts the CO2 rules as currently drafted all 50 state vehicle markets will be required to move in the same direction. It then seems likely that most states will achieve 100% ZEV sales by 2045, 10 years after California’s target.

We recently published a major report on transitioning the US to ZEVs, along with other steps to achieve a very low carbon road-transport sector in the US by 2050. Our report considers a range of scenarios based on vehicle market and policy trends, extending trajectories to 2050. In each case, overall GHG emissions reductions are achieved sooner with the adoption of low-carbon fuels such as advanced biofuels. Our results show that it is possible to reach a 90% or greater reduction in road GHG emissions by 2050 compared to 2015, even in our slowest ZEV transition scenario.

Major findings include:

  • Fast ZEV uptake works but is challenging. Our Low Carbon California (LC CA) scenario is the most ambitious, reaching 100% ZEV sales nationwide by 2035, and 90% ZEV stock by 2050. It involves achieving 68% and 51% of ZEV sales by 2030 for LDVs and trucks, respectively, which will be challenging over the coming seven years.
  • Very high uptake of low-carbon fuels is another, complementary option. Our Low Carbon 10-to-15-year (LC 10-15) scenario is the least ambitious for ZEV uptake and therefore requires the most liquid fuels to reach a 90% GHG reduction. It does not reach 100% ZEV sales nationwide until 2050, resulting in about 54% ZEV stock in that year. These, along with a high uptake of low-carbon fuels in remaining ICE vehicles, achieves an overall GHG reduction of 90% in 2050.
  • Low GHG electricity and hydrogen are critical for both types of scenarios. All ZEVs must eventually be powered from these energy sources, with the electricity and hydrogen providing net zero carbon energy hopefully well before 2050.
  • The slower the ZEV uptake, the more challenging the biofuels component. The result of slower ZEV uptake is a build-up to very high—possibly infeasible or unsustainable—levels of advanced, very low-carbon biofuel use to ensure ongoing GHG reductions in the transportation energy sector. A transition will be needed from today’s dominant grain and oil-based biofuels to predominantly cellulosic biomass-based fuels to maximize their GHG benefits.
  • All scenarios save money, but ZEVs are likely to be cheaper than low-carbon fuels. Cumulative costs of the alternative scenarios from 2020 to 2050, aggregated across LDVs and trucks, are much lower than the business-as-usual (BAU) scenario. The faster the ZEV transition, the greater the net savings between now and 2050. This is mainly due to the lower need for maintenance and higher fuel efficiency of ZEVs. As ZEV prices fall over time, savings on vehicle costs of the alternative scenarios also contribute to overall savings. However, for some specific vehicle types, such as long-haul (LH) trucks that are dominated by fuel cell vehicles (FCV) with only a modest increase in fuel economy over diesel trucks, there are no fuel cost savings, so overall costs are higher than the BAU scenario.

Our analysis also evaluates battery electric energy vs. hydrogen fuel cells for 10 different vehicle types, including LDVs, trucks and buses of different sizes and types. The general results are shown here, with sales shares varying by vehicle type and year for our BAU and two fastest transition scenarios. Our background technology analysis shows that electric vehicles dominate LDV and most truck sales by 2035. However, for long haul trucks, we find hydrogen fuel cell trucks eventually could dominate. In any case, the ZEV sales share is 100% by 2050 in all our scenarios except the BAU.

Bar chart showing vehicle sales shares across vehicle types, scenarios, technologies, and years.

Comparing the fastest transition (LC CA) to BAU for costs, including purchase, fuels, and maintenance costs of all vehicles, we find that this scenario is more expensive than BAU until around 2030, then has lower net costs, becoming much lower very quickly. These higher “investment” costs pay off with around 54 times the savings after 2028 in a non-cost discounted scenario. Slower ZEV transition scenarios save less money, since it’s the ZEVs—particularly battery electric vehicles—that save money, while biofuels costs are generally higher than fossil fuels.

Plot graph showing total vehicle and operation and maintenance cost differences from 2015 to 2050 for light-duty vehicles and trucks combined for the LC CA scenario and BAU.

As our report describes, there are many details that are uncertain. Continuing research will be needed to better predict outcomes. For example, costs may change over time in unpredictable ways, and will depend to a large degree on scaling and learning. The level of policy support that may be needed to help manage the costs of transition are uncertain. The net societal costs of various types of policies and/or regulatory strategies are important, though often difficult to estimate. Our research over the coming one to two years will focus on better understanding fleet behavior, non-cost decision factors, electricity costs, and the potential role, sourcing, and costs of advanced biofuels as well as e-fuels.

 

Addressing the Impact of Lithium-ion Batteries on Low- and Middle-income Countries

The impacts of lithium-ion batteries on low- and middle-income countries are increasing as the global electric vehicle (EV) market continues to grow. The environmental and health burdens of production mainly affect countries that supply raw materials for EV batteries, while increasing exports of used EVs are going to poorer countries.

In the absence of strategic policies, the positive impacts of new EVs—such as decreased pollution and greenhouse gas emissions—could disproportionately benefit higher-income countries, while the negative impacts of second-hand EVs—such as battery disposal—could fall more on lower-income countries. 

To shed light on this problem and outline possible policy solutions, researchers at ITS-Davis collaborated with the United Nations Environment Programme (UNEP) and produced a March 2023 report entitled Electric Vehicle Lithium-ion Batteries in Lower- and Middle-income Countries: Life Cycle Impacts and Issues. Alissa Kendall, lead author and UC Davis professor of Civil and Environmental Engineering highlighted the aims of the study:

“The exponential growth of new EV sales in regions like Europe and the US is exciting to see given the key role that vehicle electrification will play in decarbonizing the transport sector. Second-hand or used vehicles from high-income regions are important sources of lower-cost vehicles in many lower- and middle-income countries, so the rapidly changing fleets have implications for the vehicles available in these regions. Unlike engines and other powertrain components in gasoline and diesel vehicles, which can be repaired, EV batteries aren’t as repairable, and as they age, their capacity and power inevitably fade. We undertook this research to make a first estimate of the magnitude of internationally traded second-hand EVs in the coming decades, and then explored the potential impacts, risks, and benefits to lower- and middle-income countries.”

The report and Figure 1 describe the life-cycle of lithium-ion batteries (LIBs)—from mineral extraction, to use in original vehicles, to secondary use in 2- and 3-wheel vehicles and microgrids, and finally disposal and recycling of components.

Life cycle of lithium-ion batteries in second-hand electric vehicle exports.

Figure1. Life cycle of lithium-ion batteries in second-hand electric vehicle exports.

The impact of second-hand EVs and batteries in lower- and middle-income countries, and whether they provide a net benefit or impact, is a function of the EV battery state-of-health at the time of import, the potential for repairing or replacing the battery, the availability of charging infrastructure, and the energy resources (fossil-fuel or renewable) used to charge batteries.

The authors of the report conducted an extensive literature review, consulted with an expert in a major used-EV importing country (Sri Lanka), and analyzed data from multiple sources on EV sales, imports, and exports. This last endeavor revealed major discrepancies in vehicle numbers reported by paired exporting and importing countries, such as the US and Mexico shown below.

Chart showing second-hand vehicle export and import estimates, with discrepancies in data from paired countries. The number of vehicles going from the US to Mexico surged when the North American Free Trade Agreement began, then fell when policies limiting imports went into effect.

Figure 2. Second-hand vehicle export and import estimates, showing discrepancies in data from paired countries. The number of vehicles going from the US to Mexico surged when the North American Free Trade Agreement began, then fell when policies limiting imports went into effect.

Policy suggestions stemming from this research, include:

  • Upon export, provide information on battery condition, technical information for safe repair and repurposing of batteries, and data on the movement of second-hand vehicles.
  • Ensure that secondary parties other than battery and vehicle manufacturers have the right to repair batteries and EVs and have access to real-time information on battery condition.
  • Create a harmonized reporting system for collecting data at the point of export and import.
  • Institute export and import controls, such as minimal requirements for the state-of-health of batteries.

Such measures can help prevent second-hand EV and battery exports from becoming a least-cost disposal option for exporting markets, burdening rather than benefiting importing markets.

 


Seth Karten is a science writer at ITS-Davis.

Design Strategies in Shared Vehicles to Prevent Disease Transmission

Ventilation figure

Ventilation figure

Through the evolving phases of the COVID-19 pandemic, most of us have had to consider, wonder, and worry how safe we or our personal contacts are when riding in vehicles with other people. The resulting decisions about whether to ride or work on a mode of transportation have far-reaching impacts: on individuals’ income, education, and social life, and, collectively, on transportation equity, road congestion, pollution, and greenhouse gas emissions. A new study from ITS-Davis will help researchers, transportation service providers, policymakers, and the public determine how well different design features in vehicles—such as ventilation and physical barriers—can prevent transmission of COVID-19 and other contagious diseases.

The study provides a comprehensive classification system for existing and proposed design strategies for vehicles that are used by multiple individuals at the same time (“pooled modes”) or one after another (“shared modes”). After conducting a literature search, the researchers classified design elements in modes including buses, trains, subways, ride-hailing cars and taxis, airplanes, ferries, and shared cars, bikes, and scooters.

The classification includes the following 12 categories:

  • Seating configuration—e.g., spreading out or changing the direction of seats
  • Pathways—e.g., changing how passengers move about and their proximity to drivers or other passengers
  • Barriers
  • Ventilation and air circulation
  • Air filtration and cleaning
  • Onboard surface sanitization—equipment installed in the vehicle that controls cleaning processes (e.g., ultraviolet light, heat, chemicals, or air)
  • Hygienic materials—easy to clean materials that are not porous
  • Hygienic construction—e.g., minimizing seams and joints; detachable or movable trays and seats to facilitate cleaning
  • Touchless technology
  • PPE (personal protective equipment) and supply provisioning
  • Communication and monitoring—e.g., public announcements to follow guidelines, displays that report on occupancy levels or air flow
  • Multimodal support —e.g., providing bike/scooter racks to shorten rides in pooled and shared modes

The published study includes an illustrated guide to these categories in a downloadable appendix, and it classifies 12 mechanisms through which each of the above strategies work, such as by physical distancing or increased air exchange.

A second part of the study is a survey of experts’ opinions on which design strategies may be most effective for reducing COVID transmission and where gaps in knowledge remain. The experts included physicians, engineers, epidemiologists, and social scientists with public health and communications backgrounds. Not surprisingly, they prioritized strategies that worked through increased air exchange, air flow, and air cleaning. The social scientists also emphasized the importance of affecting perceived safety, through education and communications, to make riders aware of strategies that are unfamiliar or, like air filtration, not visible.

Research and guidance on effective measures to reduce disease transmission on shared and pooled transportation has been published. However, much of the guidance focuses on behavioral rather than design interventions. And much of the design guidance has been industry specific, coming from disparate sources, such as the Centers for Disease Control, Department of Transportation, Occupational Health and Safety Administration, and American Society of Heating, Refrigerating, and Air-Conditioning Engineers. The new classification system builds on the earlier work and aims to make future research and guidance more widely applicable and robust.

A clear classification system should allow for a better understanding and comparative evaluation of a multitude of design possibilities. Evaluating which strategies are most effective and how they are perceived by the public can inform budgeting decisions by transportation providers and help raise ridership on pooled and shared modes. Many of these modes are key to transportation equity, employment of essential workers, and reduced greenhouse gas emissions.


Additional information: article in Transportation Research Recordproject web page.

Seth Karten is a science writer at ITS-Davis.

Angela Sanguinetti is a research environmental psychologist at ITS-Davis.

Beth Ferguson, Assistant Professor in the Department of Design at UC Davis, contributed significantly to the study described here as a co-principal investigator with Dr. Sanguinetti.

The study was made possible through funding received by the University of California Institute of Transportation Studies from the State of California through the Road Repair and Accountability Act of 2017 (Senate Bill 1).

Get in the Know About California Climate and Transportation Policy

Signing bill into law

It’s September–the month when Californians (especially policy wonks) wait with bated breath for the Governor’s end-of-the-month deadline for signing or vetoing bills. This year, Governor Newsom has championed a portfolio of ambitious climate bills and the Legislature has delivered them, with measures seeking to cut carbon from the electricity grid, transportation, buildings, natural lands, and industry. While nothing is final until the bills are signed, the time and effort the Governor’s Office has spent on these bills over the last month presages a strong chance that they will be signed into law.

Climate Planning Bills

First, let’s speak to two headline bills that escalate California’s ambitious climate policy. AB 1279 codifies the current target of carbon neutrality by 2045 into state law, where it was previously an executive order. It also specifies that greenhouse gas (GHG) emissions must be at least 85% below 1990 levels by that time, ensuring that no more than 15% of the goal could be met by carbon capture and sequestration, natural land uptake, or offsets.

SB 1020 enhances the state’s commitment to switching to zero-emission sources of electricity by specifying timelines and milestones. Existing law requires the state to supply 100% of its electricity from non-emitting sources—such as wind, solar, hydroelectric, geothermal, or nuclear—by 2045. SB 1020 requires that 90% of electricity come from such sources by 2035, and 95% by 2040, ensuring that utilities make significant progress immediately, while recognizing that switching the last 5–10% of supply over to clean sources may be more challenging than earlier parts of the transition.

Several other bills help define how the state would achieve its GHG targets. AB 2438 aligns transportation spending with California’s climate goals, AB 1322 requires the California Air Resources Board to map a plan to reduce emissions from commercial aviation to align with state goals and get 20% of aviation fuel from sustainable sources by 2030. SB 1137 prevents drilling to create new petroleum wells, or expand old ones, within 3200 feet of schools, hospitals, residential areas, or other sensitive sites. These, combined with many others, help align state policies with the strategy for achieving carbon neutrality in transportation laid out by a research team from UC Davis, UC Berkeley, and UC Irvine in a major report released last year.

Electric Vehicle Bills

Electric vehicle legislation advanced in the legislature, and the Governor will have a chance to consider AB 1738, which would empower the California Department of Housing and Community Development to come up with standards for EV charger installations for California homes. San Francisco has already set requirements for new buildings to include EV-ready parking spaces. But solidifying statewide standards is critical, given that most EV owners charge at home and home is the most influential charging location affecting the decision to purchase and continue owning an EV. Ensuring equitable EV access was a big focus of the legislature this year. If signed, SB 1382 will reform the state’s Clean Cars 4 All program to support more outreach to encourage people with low-incomes to buy EVs with state rebates, and it also adds additional tax benefits as an incentive.

Car Free California

Lawmakers are proposing to just pay people to give up their cars. SB 1230 would reform the Clean Cars 4 All program, including benefits for qualifying Californians who do not have a car by providing a “mobility option” voucher for transit or shared mobility services like bikeshare or scooter share. And if vouchers weren’t incentive enough to shed their vehicles, SB 457 takes it a step further, offering Californians cash for not driving. The bill will give a $1,000 tax credit to car-free households in the state. Together these two programs would put some real money in the pockets of car-free California households.

Bicycle and Pedestrian Bills

Perhaps some people who receive the car free bonuses will buy an e-bike and really max their state kickbacks. AB 117 would offer CARB $10 million to get a new and improved e-bike incentive program off the ground, separate from the state’s clean vehicle rebate program, where it is housed currently. Other e-bike bills include AB 1909, which would update bike law to authorize local governments to decide whether e-bikes can operate on bike trails (taking this authority from the state). On the pedestrian side, AB 2147 would decriminalize jaywalking, “unless a reasonably careful person would realize there is an immediate danger of collision with a moving vehicle or other device moving exclusively by human power.” According to research by Jesus Barajas, jaywalking policies have been historical tools for discriminatory enforcement against people who walk, and especially people of color.

Public transportation Bills

In the wake of many local transit agencies providing free rides in the early part of the COVID-19 pandemic, state lawmakers were actively debating how to make public transit free for Californians who need it most. The Governor will be considering AB 1919, which would provide funding to local agencies to offer a 5-year pilot for college and K-12 students to get free transit passes. A related transit bill, SB 942 would allow agencies to use certain existing funds for more discretionary purposes, including for free passes. Check out this Freakonomics episode featuring our UCLA colleague Brian Taylor explaining some of the pros and cons of fare-free transit.

Sustainable Land Use Planning Bills

There are also several sustainable planning bills for the Governor to consider. SB 922 would make it easier to build bike lanes, pedestrian projects, and transit, thanks to a streamlined environmental review process. Expediting these types of transportation investments can create a virtuous cycle that enables people to drive less. As Professor Susan Handy stated, “land use patterns shape travel behavior, transport investments shape land use patterns, transport is itself a sizable land use, and these relationships are self-reinforcing.” Another bill addressing the tension between land use and transportation is AB 2438, which seeks to align transportation projects with state plans. This bill will touch on some of the recommendations in the recent report by Betty Deakin that evaluated whether state planning efforts can succeed at reaching state climate goals. Other land use bills address parking, which is another hot (asphalt) topic. AB 2097 would restrict local governments from requiring parking minimums. This is another sign of research-backed policy, onsite parking has been shown to correlate with car ownership and use.

Bills that failed to get out of the Legislature

Some bills won’t get to the Governor’s desk. SB 917, the so-called “Seamless Transit Transformation Act” failed to make it out of its final committee. This bill aimed to streamline the San Francisco Bay Area’s 27 transit districts. According to the sponsor of the bill, Seamless Bay Area, it’s possible that the bill failed because many of the integration requirements are already being planned by regional regulators. Another bill that failed to get out of the legislature (dying in a nail-biter moment in its final committee) is AB 2133, which proposed to strengthen climate plans to strive for a 2030 goal of 55% of 1990 emissions levels (up from the 40% already required by law).

Looking Back to Inform Looking Forward

It’s important to note that all of these bills come on the heels of a record-setting budget package that was signed by the Governor in late June (with budget trailer bills tacked on in July). During the weeks of budget negotiations, lawmakers outlined plans to spend $308 billion (which includes a surplus of $49 billion more than initially projected), 6.4% of this to be spent on transportation. Big ticket items include $15 billion for the next four years of transportation infrastructure, $7.7 billion for transit, $4.2 billion for high-speed rail, $1.2 billion for goods movement and ports, and $1 billion for making active modes more safe and attractive. These historic investments are locked in, but it remains to be seen which transportation-related bills from this legislative session will receive the Governor’s signature and benefit from that windfall budget.

[UPDATE: AB 1919 was vetoed by the Governor on September 13th. A veto statement can be found here.]


Mollie Cohen D’Agostino is Policy Director at the UC Davis Policy Institute for Energy, Environment, and the Economy (PIEEE)

Colin Murphy is Deputy Director at PIEEE

Josh Stark is Policy Analyst at PIEEE

New Mobility for Sustainable Suburban and Rural Travel

Sustainable Suburban and Rural Travel

There are many reasons to reduce our reliance on cars—they are polluting, inefficient, dangerous, and expensive to own. In dense urban areas, travel modes such as walking, bicycling, and public transit can be reasonable alternatives for many peoples’ transportation needs.

But what about suburban and rural areas with lower population densities and longer distances between destinations? Land use patterns in these regions make it challenging to get around without a private vehicle. Can emerging mobility options reduce car dependence in these environments?

Based on our research so far, the answer appears to be yes. Our research teams are at the forefront of evaluating how new mobility services such as microtransit (on-demand, small shuttles providing shared rides), carsharing, and ridesharing are being used and the extent to which they are substituting for private car travel in California’s suburban and rural contexts.

Microtransit in Suburban Sacramento

Suburban communities around Sacramento are not well served by fixed-route transit. In 2018, Sacramento Regional Transit launched a microtransit service called SmaRT Ride to fill this gap. SmaRT Ride is available in eight outlying areas and the downtown core that allows travelers to request a “door-to-door” or “corner-to-corner” ride via a smartphone app. Rides cost the same as fixed-route transit.

Dr. Xing’s team studied early adopters of SmaRT Ride, conducting surveys and focus groups of both users and non-users of the service. When asked about transportation choices, more than 40% of riders said that, without SmaRT Ride, they would have made their last microtransit trip by car instead. This suggests that microtransit has real potential to reduce dependence on driving.

The study also found that more than half of SmaRT Ride users had an annual household income of less than $50,000, and that users of the service are more likely than non-users to have physical limitations. Finally, people who do not like fixed-route transit or have a neutral attitude towards it are more likely to use SmaRT Ride than are those who like fixed-route transit. This suggests that microtransit is more of a complement to, rather than a replacement for, fixed-route transit.

Innovative Mobility in the San Joaquin Valley

Dr. Rodier has been engaged with regional partners since 2014 to plan, launch, and evaluate three mobility pilots in the rural San Joaquin Valley. The region is characterized by high levels of poverty and air pollution and long distances between destinations, presenting particular challenges for providing clean and affordable transportation.

In 2019, three services were launched in the region: Míocar, an electric carsharing program with vehicle hubs at affordable housing complexes in Tulare and Kern counties; VOGO, a volunteer ridesharing service; and Vamos, a Mobility-as-a-Service app that facilitates trip planning and ticket purchasing across the valley’s many transit services.

So far, the research shows that each of these services is helping people move around the region in new ways. More than 60% of Míocar trips would not have occurred without access to the service, and three-quarters of the miles traveled on these “new” trips were made by travelers from households below the median income level in their county. People who would have used another mode to make their trip in the absence of Míocar would have traveled almost exclusively by gasoline-powered cars. So the service reduces greenhouse gas emissions for those trips.

Similarly, most of those using the VOGO ridesharing service would not have otherwise been able to make their trips. Most VOGO riders do not have access to a personal vehicle and are uncomfortable driving vehicles due to medical issues or other concerns, leaving them with few options for trips that cannot be made via existing transit services. Finally, early study results suggest that Vamos is a valuable transit fare payment tool and contributes to an improved transportation experience for its active users. More study is needed to assess the effects of Vamos on transit use and mobility as this app expands its service area and user base.

Key Takeaways

Small mobility programs like these are proliferating as communities seek affordable, sustainable alternatives to private vehicle ownership. Our research is showing early indications that these programs can be successful in meeting rural and suburban transportation needs, particularly for low-income travelers. However, these services need continued support. Private ridehailing and carsharing companies typically offer their services in higher-income urban areas that already have plentiful transportation options. To increase clean transportation access in underserved communities, new business models may be needed. These may include direct service provided by a transit agency, such as SmaRT Ride, or a non-profit service operated with public subsidies, such as Míocar. Further coordination among transportation providers and community-based organizations will be essential in identifying and developing transportation solutions to meet the needs of individual communities. Rigorous evaluations of these programs as they develop can assess their contributions to policy goals related to transportation equity and climate change, and inform longer-term investments.

Further reading:

NCST SmaRT Ride report and policy brief: https://ncst.ucdavis.edu/project/exploring-consumer-market-and-environmental-impacts-microtransit-services

UC ITS Míocar report and policy brief: https://www.ucits.org/research-project/2019-44/

NCST San Joaquin mobility report and policy brief: https://ncst.ucdavis.edu/project/before-and-after-evaluation-shared-mobility-projects-san-joaquin-valley

 

Yan Xing is a postdoctoral researcher at ITS-Davis.

Caroline Rodier is a researcher at ITS-Davis and the associate director of the Urban Land Use and Transportation Center at UC Davis.

Brian Harold is the policy evaluation specialist at the UC Davis Policy Institute for Energy, Environment, and the Economy.

Mike Sintetos is the policy director at the National Center for Sustainable Transportation (NCST) and UC ITS Statewide Transportation Research Program.

Ecology 101: Protecting Wildlife from Transportation

Wallis Annenburg Wildlife Crossing | Photo: Courtesy of the National Wildlife Federation

(Photo: Courtesy of the National Wildlife Federation)

 

The Wallis Annenberg Wildlife Crossing in Agoura Hills, California, which will soon be under construction, is unprecedented in its size, cost, and primary purpose. Estimated to cost $90 million, it is the first major wildlife over-crossing primarily aimed at bringing genetic diversity to isolated animal populations rather than preventing roadkills—though it will do that, too.

The crossing, also known as the Liberty Canyon Wildlife Crossing, will be an overpass covered with vegetation, spanning ten very busy lanes of US Highway 101. It will allow mountain lions and other species to cross between the Simi Hills to the north and the Santa Monica Mountains to the south. Without this crossing, the mountain lion populations in the area would likely disappear in the next few decades because of inbreeding, vehicle strikes, and limited space to escape from wildfires.

Traffic Light and Noise

The planned crossing features design elements that will encourage mountain lions and other species that are sensitive to light and noise to actually use it. Barriers and berms will be built to reduce the amount of traffic-generated noise and light that reaches the areas that animals will use to approach the crossing. Three of our research projects at the Road Ecology Center on roadway light and noise helped influence this design. These projects were supported through state (SB1) and federal (USDOT) funds to the UC Davis Institute of Transportation Studies and the National Center for Sustainable Transportation, respectively. 

In the first of our related projects, we found that wildlife crossings are used by larger proportions of nearby, light- and noise-sensitive animal species if the crossings are comparatively dark and quiet. Our second study showed that the different behaviors among animal species in response to traffic noise and light determined how much they used wildlife crossings with varying traffic disturbance conditions. In the third study, we investigated ways of mitigating light and noise near the Wallis Annenberg crossing and a proposed over-crossing for I-15, near Temecula, California. First we found that light and noise from traffic could be detected more than 100 meters away from the highway in the animal approach zones of both crossings. We then used 3D-design software and traffic-noise modelling software to show that changing the configuration of barriers and berms near the crossings could reduce the traffic noise and light in the approach zones (Figure). Based on the results, we made recommendations to the designers to increase the chance that wildlife will approach the crossings.

Noise glare mitigation

Figure: Noise and glare mitigation in the approach zone to the crossing. (A) Typical approach to crossing structure without noise and light abatement. (B) Quiet and dark paths created by excavating and redistributing landscape materials (tan areas) and adding barriers along the highway.

The Need for Fencing and Crossings

Every year, more than 7,000 vehicle collisions with large, wild animals (e.g., deer, black bear) are reported in California, according to our California Roadkill Observation System (https://wildlifecrossing.net/California), and this is likely a significant undercount. For example, State Farm Insurance Co. estimates that there are upwards of 20,000 claims/year for deer-vehicle collisions in California. Not only can these crashes lead to loss of human life, property, and animal life, they can also affect the balance of ecosystems. 

One way to slow the decline of wildlife species is by lowering direct and indirect mortality from traffic. We know that we can reduce the number of vehicle collisions and alleviate genetic isolation with simple tools: 1) traffic calming and reduction, 2) fencing alone, and 3) fencing combined with wildlife crossing structures. Research done in California by the Road Ecology Center has shown where wildlife crossings and fencing are most needed and could provide greater economic benefits than their cost (https://wildlifecrossingcalculator.org). The state is already home to more than 100 wildlife crossings, used by a wide range of reptile, amphibian, and mammal species. But there is a grave need for at least ten times as many. 

Policy Environment

In the past few years, public support for wildlife crossings has grown significantly. Knowledge and awareness of crossings has spread from research scientists, to transportation planners and engineers, to the wider world. But policies and related budgets remain inadequate to the needs. Two Legislative efforts reflect this picture. 

First, the 2021 Federal Bipartisan Infrastructure Law initially authorized $350 million for new wildlife crossings. Ultimately, however, Congress appropriated $0 of the $350 million for crossings. Second, California Assembly Bill (AB) 2344 initially required the Department of Fish and Wildlife and Caltrans (the California Department of Transportation) to investigate areas that are essential to wildlife movement and habitat connectivity, to develop a plan to address these areas, and for Caltrans to implement 10 crossing structures per year. This last and strongest requirement was supported by hunting and environmental groups, but was recently removed from the bill. Although compromise of environmental legislation is an all-too-common occurrence in California, the future will tell whether this critical requirement will be negotiated back into the bill. 

In California, Road Ecology Center research shows that wildlife-vehicle collisions cost the state upwards of $250 million per year. While the state’s transportation budget is $20-25 billion per year, Caltrans has claimed that only two to three wildlife crossings are built per year in California, which, at most, would account for about 0.1% of the annual transportation budget. Yet, surveyed taxpayers consistently report that they would be willing to pay more taxes in order to protect wildlife. And state policy may finally be starting to reflect this outlook. SB 790, signed by Governor Newsom in October 2021, included $61 million for building wildlife crossings, $7 million of which was allocated for the Wallis Annenberg crossing. 

In sum, we know where to build wildlife crossings and fences; research is improving the effectiveness of these tools; and we can approximate their cost and benefits. We have a lot of information for decision support on how to address habitat fragmentation, wildlife deaths, vehicle accidents, and the cost to humans and nonhuman animals. While the policy and transportation planning response has grown significantly, we still need more from implementing transportation agencies to protect wildlife and from legislative bodies to require action and allocate more funding to make it possible.

 

Fraser Shilling is the director of the Road Ecology Center at the UC Davis Institute of Transportation Studies (ITS-Davis); Seth Karten is a senior writer at ITS-Davis.

How Providing Emissions Information Can Begin Greening Aviation

Illustration of flight schedule board with blank rows and positive or negative CO2 indicators at the end of each row

Those carefree, pre-pandemic days of hopping on a flight for a meeting or vacation without a second thought may seem like a distant memory to some of us right now. Still, air travel this fall has far exceeded that of 2020, even if it has yet to recover to pre-pandemic levels. Fairly soon, flying will almost certainly return to the upward trend that showed global air travel more than doubled from 2004-2019.

That’s a problem for the climate.

Flights accounted for about 2.5% of worldwide greenhouse gas emissions in 2019. While the federal government has announced an emissions reduction target of 20% by 2030 and a key airline industry group has recently proposed a net-zero plan, there is no firm consensus on a path to decarbonization for the aviation sector.

Can individual travelers play a role in reducing emissions?

Many climate hawks are cutting back or choosing not to fly at all. And it turns out that even when we do fly, our choices matter–different flight itineraries on the same route can vary quite a bit in the amount of greenhouse gases they generate, primarily due to the number of layovers (take-offs and landings produce a lot of emissions), the locations of the layovers, and the fuel efficiency of the aircraft. For example, a traveler heading from Sacramento, CA to Washington, DC might see a selection of flights that vary in emissions by as much as 30%.

That’s why the new emissions information you see when searching on Google Flights is so important. Our research indicates that people will use this information to choose lower-emissions flights.

Illustration of flight schedule board with blank rows and positive or negative CO2 indicators at the end of each row

 

How Emissions Information Can Make a Difference

In 2015 we began work on GreenFLY.ucdavis.edu, a demo flight search website that shows the emissions of each flight as prominently as the price, labels the lowest emissions options “Your GreenFLY,” and, by default, sorts flights from lowest to highest emissions. Experimenting with GreenFLY helped us demonstrate the wide variation in emissions among flights with the same origins and destinations, especially for long cross-country or international flights.

We conducted two experiments to test whether this method of providing emissions information on available flight options would nudge travelers toward choosing lower-emitting flights. After all, someone using a flight-search website is already balancing many factors, such as when to fly, price, length of layover and perhaps a favorite airline; why not put emissions into the mix? In our studies we asked people to choose between a few flights, and we used that data to build a predictive model of how much value people put on different factors such as price, layovers, and emissions.

As most other researchers into flight choice have found, price was the most important consideration. But we also found that people were willing to pay more for a lower-emissions flight. For instance, an international flight might emit around a metric ton of carbon (1000kg); and people were willing to pay $20 more for a ticket that avoided 100kg of CO2 emissions, or about 10%. This translates to a rate (“willingness to pay”) of about $200/ton of CO2 saved, much higher than the average price of carbon offsets, which is about $3-6/ton! This surprisingly strong effect was consistent between two studies looking at different populations (one of UC Davis employees and one of more broadly recruited American travelers).

Real-World Emissions Reductions

Our studies presented travelers with hypothetical trips, and our GreenFLY site was just a demo. But now that Google Flights is using an emissions-focused interface, we will have an opportunity to see how emissions information will influence consumer behavior on a huge scale. We’re optimistic that we’ll see an impact on the travel choices of Google Flights’ many users and, possibly, on overall aviation emissions.

The possibilities are exciting. If more travel booking and search platforms follow the lead of Google and others like Kayak, Skyscanner, and Lite Flights, this could have a cascading effect. Many consumers choosing lower-carbon flights could push airlines to invest in more fuel-efficient aircraft as well as sustainable aviation fuels. Repeatedly seeing emissions information could raise traveler’s awareness of the environmental cost of flying. This may ultimately build support for emissions reduction regulations and investments in more sustainable travel alternatives.

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More information on the authors’ GreenFLY research is available in an NCST ReportNCST Policy Brief, a 2021 Transportation Research Record paper, and a 2017 Design, User Experience, and Usability Conference Paper.

 

Angela Sanguinetti is a Research Environmental Psychologist at the UC Davis Institute of Transportation Studies and Energy & Efficiency Institute.

Nina Amenta is professor of Computer Science at UC Davis.

Mike Sintetos is Policy Director for the National Center for Sustainable Transportation (NCST) and SB1 Research Program at the UC Davis Institute of Transportation Studies.

Electric, automated, shared mobility in the future: how will people choose? The role of monetary and non-monetary factors

Illustration of money/time balance

Illustration of money/time balance

By Lew Fulton and Mike Sintetos

Much has been written about the three revolutions transforming transportation—automation, electrification, and sharing—and about their potential to shape the future sustainability of the transportation system. Yet it is also important to consider that these profound changes in travel options may also have varying impacts on the environment.

Take, for example, the potential of vehicle automation. Fully automated vehicles may become widely available as a low-cost ride-hailing or private vehicle option within a decade. The lower monetary and time-cost (related to time spent traveling) of automated vehicle travel could dramatically increase vehicle miles traveled, pollution, and traffic congestion, unless policies are put in place to manage a rapidly changing system. Low-cost, driverless ride-hailing trips may also reduce the incentive to pool rides if it reduces the price advantage of pooling. Furthermore, whether the vehicles are electric or gas-powered will be a critical determinant of their environmental impacts.

The relative costs of mode choices, technology choices, and new technology introductions will be a major factor in whether the net effects of these “3 revolutions” add up to more or less traffic, pollution, and greenhouse gas emissions. Fundamental questions to consider include: will future travelers decide to purchase their own automated vehicles or use automated ride-hailing? Will they use fleets of “robo-taxis” primarily for solo trips or will they share those trips with others, reducing traffic impacts? Will they choose electric over gas-powered vehicles in cases where they have a choice? And what factors will go into these decisions?

We have explored these questions in a series of recent papers.

Factors Influencing Travel Choice

Our research explores the many monetary and non-monetary factors that go into people’s travel decisions. Monetary costs related to owning a vehicle include the purchase cost, maintenance, fuel, and parking costs. Among these, some are fixed and some vary, occurring with each trip. The variable costs appear likely to be more influential in short-term decisions about what modes to choose for a given trip (once a car is bought, the purchase cost may be ignored in daily travel decisions). For travel choices such as on-demand ride hailing, all costs are essentially variable, paid for each trip and roughly per mile.

Non-monetary factors also play a big role in traveler mode choices. Travel time, convenience, certainty of departure and arrival times, safety/security concerns, and other factors all play a role in our decisions about how we get from point A to point B. There is considerable research exploring these factors in traditional mode choice contexts, such as driving vs. taking public transit. But it is less clear how these factors will impact choices in our “3 revolutions” future, with its many new types of choices. Which travel choices will appear to be lowest cost in different situations when considering monetary and non-monetary costs together as a “generalized cost”?

To understand how people might make travel decisions in a future with fully automated vehicles, various ride-hailing and sharing options, and the possibility of vehicle electrification, we need to understand the relative values of these different monetary and non-monetary factors and how these generalized costs might compare across travel modes.

Our team used existing research and data estimates, along with some projections of future costs, to develop generalized cost estimates for several future travel modes, including private vehicle travel, solo ride-hailing, and pooled ride-hailing, for electric and gas-powered vehicle technologies, considering the presence of a human driver in the near term analysis and focused on automated vehicles in the 2030-35 timeframe. Our estimates take into account the costs of vehicles, energy, and perhaps most importantly, the value of time during specific trips. We looked at several specific trip situations, focusing mainly on 1) a short-distance, urban trip, and 2) a longer-distance, suburban trip.

Generalized Costs of Future Travel

While we have estimated monetary and some non-monetary costs of travel options, we have ultimately learned that there are many more possible costs than we can realistically estimate values for at this time. One example is the “cost” associated with the hassle of having to remove personal belongings such as child seats from a shared vehicle rather than leaving things in a personal car. We used value of time assumptions to estimate values for a number of factors that have a clear time component, such as the time spent traveling in the vehicle, waiting for a vehicle to arrive, and searching for parking.

Overall, our findings suggest that a few things are likely to occur once automated vehicles are widely available. These are reflected in the figure below, which provides a snapshot of relative costs of modes in 2030 taking into account a range of monetary and non-monetary factors:

  • Not having to drive will save about half the generalized cost of private vehicle trips, as long as people find their time as a passenger somewhat useful and preferable to driving.
  • A driverless ride-hailing trip appears likely to be, from a generalized cost point of view, cheaper than today’s ride-hailing options, including pooled trips, with no need to pay a driver.
  • The reduced monetary cost of both solo and pooled ride-hailing services will shrink pooled ride-hailing’s relative advantage without affecting its non-monetary disadvantages (longer travel time, less predictability, potential safety concerns). Thus, pooled ride-hailing may become even more unappealing in an automated future.
  • While electric vehicles are slightly more expensive (higher purchase cost, mostly offset by lower driving cost), their relative cost differences with conventional vehicles are tiny compared to the various non-monetary costs associated with different modes. Once automation is available, it seems the financial cost of whether a vehicle is electric or not will be relatively unimportant compared to automation-related factors.
Monetary and non-monetary costs for vehicles types - 2030

Figure 1. Monetary and non-monetary costs in 2030 for various vehicle types, for a typical mid-length trip (US dollars/mile) (Source: Estimating the Costs of New Mobility Travel Options: Monetary and Non-Monetary Factors)

All of these costs will vary by situation, by person, and over time as these technologies develop, and while we explore these uncertainties in our papers, we acknowledge that much more work is needed to investigate the range of potential costs. Still, we believe these basic results are likely to hold up across many situations. If one had hoped that the net costs of various trip choices would eventually push people to share rides and reduce vehicle miles traveled, these initial results are not encouraging.

Balancing the Scales

Policies such as pricing strategies (e.g. road tolls and urban access pricing schemes) can tip the balance of costs between modes. In our May 2021 Transport Policy paper, we looked at existing road pricing schemes around the world to understand whether trip fees on solo ride-hailing, per-mile tolls, or congestion-area fees would change the relative attractiveness of solo private vehicle driving vs. ride-hailing. Our analysis showed that, with the exception of London’s daily charge to enter the central city, none of the existing road fee systems create differences that are anywhere near large enough to significantly affect travel choices. These policies tend to create differences (e.g. between solo and shared trips) that are less than $0.10 per mile, while we estimated the generalized cost differences between these modes to be as high as $1.00 per mile.

Therefore, future road pricing policies may need be much more aggressive in terms of creating per-mile cost differentials in order to have considerable impact on overall car travel, ride sharing levels, and shifts away from automobile travel altogether. Without such policies, the low cost of travel in either private or on-demand automated vehicles could lead to even more vehicle travel and roads clogged with single-passenger automated vehicles. One silver lining from our research points to the fact that the relative closeness of the generalized costs of electric vehicles and conventional vehicles may provide a good opportunity to use road pricing to promote electric vehicle adoption—a definite benefit for environmental concerns.

Based on this work, we believe that governments looking to increase the use of pooled ride-hailing to encourage more sustainable travel choices can take several actions:

  • Set ride-hailing fees to meaningfully incentivize pooled travel. Fees on solo trips need to be much higher to make a difference.
  • Prioritize access for pooled travel. Policies that reduce travel times for pooled vehicles, such as curb access or priority lanes, will lower the generalized costs of these modes.
  • Consider per-mile fees or restrictions on personal automated vehicles. The time is now to implement these policies, before AVs are widespread.

If left to develop unregulated, automated vehicle technology may only reinforce our tendency towards solo travel, particularly private automated vehicle travel, and encourage much longer trips, given their lower generalized cost. Early and effective policy action will be needed to avoid this path and ensure a more sustainable transportation future.

Additional Resources

January 2020 Transport Policy paper
May 2021 Transport Policy paper
SB1 Report
NCST Report
Policy Brief

Lew Fulton  is Director of the Sustainable Freight Research Center and the Energy Futures Research Program at the UC Davis Institute of Transportation Studies.

Mike Sintetos is Policy Director for the National Center for Sustainable Transportation (NCST) and SB1 Research Program at the UC Davis Institute of Transportation Studies.

City and County Pavement Improvement Center (CCPIC): Supporting Local Government to Make Their Pavements Better

Better Pavements

If we are going to operate ground transportation, we are going to need pavement, regardless of how those vehicles (cars, trucks, bicycles, feet) are powered. Leaving aside the question of how much pavement we want or need, pavements directly contribute to global warming throughout their life cycle. They require: materials extraction and production, transport, construction, maintenance, rehabilitation, reconstruction, and demolition (“end-of-life,” although they seldom really die, they get reused or repurposed). Pavements also affect vehicle emissions by impacting vehicle life-span and the amount of energy needed to propel vehicles.

To reduce emissions and help local governments maximize the value of their pavement dollars, a group of California universities and local governments created the City and County Pavement Improvement Center (CCPIC). The center provides cities and counties with training, tools, guidance, and outreach regarding advanced, cost-effective, and sustainable pavement practices. Many of these are available through the CCPIC website.

The CCPIC resources address the three main strategies that are currently used to reduce global warming emissions from the pavement life cycle:

  • Better engineering and construction quality at the outset of a project to minimize the environmental impacts of subsequent maintenance and rehabilitation. About 95% of all pavement spending is on keeping existing pavement functional.
  • Keeping pavements smooth and choosing the best pavement type to reduce vehicle fuel use and prolong vehicle life.
  • Better timing and treatment selection in pavement maintenance and rehabilitation through improved use of pavement management systems. These systems include low-impact preservation treatments and selection of optimal rehabilitation strategies for the pavement type and condition, climate, and traffic.

One of the projects that used CCPIC resources was the Fulton Road Reconstruction, in Santa Rosa, which won the 2021 overall award in the California’s Outstanding Local Streets and Roads Project Awards. The section of road reconstructed has 25,000 vehicles traveling on it in each direction every day. The project used a draft version of the model PCC Pavement Specifications from the CCPIC for the design of the materials and construction. Because of these and other strategies used on the renovation project, it is expected to require minimal maintenance and last longer—which will conserve funding, reduce environmental impact, and eliminate additional road work leading to traffic delays and hazards.

The CCPIC will continue expanding its training program, launching a pavement engineering and management certificate program, producing more model specifications, software tools, and technical guidance, and continuing outreach to local agencies. Support for CCPIC comes from SB1 funds from the UC Institute of Transportation Studies (Davis, Berkeley, Los Angeles and Irvine) and the California State University Transportation Consortium (Mineta Transportation Institute).

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John Harvey is a professor of Civil and Environmental Engineering at UC Davis and Director of the UC Pavement Research Center and the City and County Pavement Improvement Center.