Air Quality, Climate Change, and the Environment

How travel behaviors relate to air quality, climate change, and other environmental factors

Transportation behaviors and trends have a significant environmental impact.  Transportation contributes 27 percent of the nation’s greenhouse gas emissions, and this source saw a greater absolute increase during the period from 1990 to 2013 than any other sector (e.g. industry, commercial, electricity, etc.) (EPA, 2015). Exposure to air pollution has been connected to elevated risk of asthma, lower lung function, higher blood pressure, higher cardiac-related mortality, and lower overall life expectancy (National Institute for Transportation and Communities, 2014; Pope 2009). Air pollution exposure is also an environmental justice concern, with disparities in exposure by demographic and socioeconomic characteristics (Jones et al., 2014; Mejia et al., 2011).

Reducing air pollution exposure can be achieved by decreasing the concentration of pollutants and the length of exposure. By shifting shorter trips to walking and biking, Safe Routes to School programs can improve air quality by reducing vehicle trips and miles traveled. Reducing travel volumes is also important for minimizing children’s exposure to pollution during active transportation to school. School site location and design can also influence air pollution exposure, affecting exposure from major roadways and other sources on the way to school and during the school day (EPA, 2015).

The literature in this section explores the relationship between transportation mode choice and vehicle emissions, air pollution, and health impacts.


  • Motor vehicles are responsible for up to 30% of total greenhouse gas emissions (Solomon et al., 2009)
  • In one study, a 5% increase in neighborhood walkability (as measured using an index based on residential density, street connectivity, land use mix, and retail floor area ratio) was associated with:
    • 6.5% fewer vehicle miles traveled (VMT) per capita
    • 5.6% fewer grams of nitrogen dioxide per capita
    • 5.5% fewer grams of volatile organic compound (VOC) emitted per capita (Frank, et al., 2006)
  • Living in majority white neighborhoods has been associated with lower air pollution exposure, and living in majority Hispanic neighborhoods has been associated with higher pollution exposures (Jones et al., 2014)
  • Lower socioeconomic status has been connected with closer school proximity to pollution sources (Mejia et al., 2011)
  • Rates of asthma have been associated with closer residential distance to a freeway among children (Gauderman et al., 2005); exposure to roads with high vehicle traffic (representing near-road traffic-related pollution) accounted for 14% of all asthma cases across 10 European cities (Perez et al., 2013)
  • In a study model, substitution of cycling for short vehicle trips had the potential to reduce gasoline demand about 35% and CO2 emissions by 12% (Higgins et al., 2005)
  • Health benefits of shifting from car to bicycle was associated with greater benefits from increased physical activity (3-14 months of life gained) compared with potential effects of inhaled air pollution (0.8-40 days of life lost) (de Hartog et al., 2010)
  • Improved air quality accounted for as much as 15% of the overall increase in life expectancy in one study (Pope et al., 2009)

See 2011 and Earlier Archived Articles

Academic Research Articles and Findings:

Can air pollution negate the health benefits of cycling and walking?

Key takeaway:

  • The long-term health benefits of physical activity through active travel generally outweigh the health risks of air pollution.


  • At the global average for air pollution from particulate matter (i.e., PM2.5 concentration 22 μg/m3), the benefits of physical activity outweigh air pollution exposure even at extreme levels of active travel.
  • Air pollution would have to reach PM2.5 concentration 95 μg/m3, a level only present in 1% of cities worldwide, in order for half an hour of cycling to have greater health risks from air pollution than benefits from physical activity.


  • This study used health impact modeling to estimate the influence of physical activity from active transportation and air pollution exposures on all-cause mortality. PM2.5 was selected as the indicator of air pollution exposure because it is commonly used in health impact modeling and has a significant health burden.
  • This study estimated the “tipping point,” or point after which an increase in active travel would no longer result in health benefits, and “break-even point,” or the point at which risk from air pollution outweighs the benefits of active transportation.

Tainio, M., de Nazelle, A. J., Götschi, T., Kahlmeier, S., Rojas-Rueda, D., Nieuwenhuijse, M. J.,de Sá, T. H., et al. (2016). Can air pollution negate the health benefits of cycling and walking?. Preventive Medicine.

Cycling and Urban Air Quality: A Study of European Experiences (2014)

Key takeaway:

  • Cycling measures can improve urban air quality levels as part of a multifaceted approach toward reducing road traffic.


  • Modeling a 23% increase in cycling mode share significantly reduced projected NOx, PM10 and black carbon emissions, resulting in improved air quality levels in the surrounding areas of each city. Projected emissions reductions varied by city, with 16-27% reductions in NOx and 4-19% reductions in PM 10.
  • Improved air quality reduced disability-adjusted life years for cardiopulmonary disease caused by poor air quality levels. Changes in cycling levels reduced disability per 10,000 residents by 4-50 years in three cities.


  • This study conducted simulations of shifts in mode share in 5 European cities and analyzed predicted air quality levels and health improvements.

Hitchcock, G. & Vedrene, M. (2014). Cycling and Urban Air Quality: A Study of European Experiences. European Cyclists’ Federation.

Evaluation of Bicyclists Exposure to Traffic-Related Air Pollution along Distinct Facility Types (2014)

Key takeaway:

Bicyclists’ exposure to air pollution can vary with roadway and travel characteristics, and transportation-related strategies can reduce exposure.


  • Concentrations of pollutants are generally higher on high-traffic facilities, except for high exposure on off-street paths running through industrial zones.
    • Concentrations of BTEX compounds (benzene, toluene, ethylbenzene, and xylenes) were 50-120% higher on major arterials than local roads.
    • One- to two-block detours to low-volume streets can significantly reduce exposure concentrations.
  • Weather and traffic variables are approximately related to BTEX compound exposure.
  • BTEX exposure concentrations increase 2% for every 1,000 average daily traffic (ADT).
  • Researchers suggested separated bicycle facilities, low-volume routes, and off-peak travel as strategies to reduce cyclist exposure to pollutants. Bicyclists’ respiration rates are two to five times faster than motorists, resulting in higher pollution intake. Exposure to traffic-related air pollution has been connected to elevated risk for asthma, lower lung function, higher blood pressure, and cardiac mortality.


  • This report included a literature review of bicyclist exposure and dose measurements as well as on-road physiology and air quality data collected by three cyclists in Portland, OR over nine days. 

National Institute for Transportation and Communities. (2014). Evaluation of Bicyclists Exposure to Traffic-Related Air Pollution along Distinct Facility Types. NITC-RR-560.

Race/Ethnicity, Residential Segregation, and Exposure to Ambient Air Pollution: The Multi-Ethnic Study of Atherosclerosis (MESA) (2014)

  • Objectives. We described the associations of ambient air pollution exposure with race/ethnicity and racial residential segregation.
  • Methods. We studied 5921 White, Black, Hispanic, and Chinese adults across 6 US cities between 2000 and 2002. Household-level fine particulate matter (PM2.5) and nitrogen oxides (NOX) were estimated for 2000. Neighborhood racial composition and residential segregation were estimated using US census tract data for 2000.
  • Results. Participants in neighborhoods with more than 60% Hispanic populations were exposed to 8% higher PM2.5 and 31% higher NOX concentrations compared with those in neighborhoods with less than 25% Hispanic populations. Participants in neighborhoods with more than 60% White populations were exposed to 5% lower PM2.5 and 18% lower NOX concentrations compared with those in neighborhoods with less than 25% of the population identifying as White. Neighborhoods with Whites underrepresented or with Hispanics overrepresented were exposed to higher PM2.5 and NOX concentrations. No differences were observed for other racial/ethnic groups.
  • Conclusions. Living in majority White neighborhoods was associated with lower air pollution exposures, and living in majority Hispanic neighborhoods was associated with higher air pollution exposures. This new information highlighted the importance of measuring neighborhood-level segregation in the environmental justice literature.

Miranda R. Jones PhD, Ana V. Diez-Roux, MD, PhD, Anjum Hajat, PhD, Kiarri N. Kershaw, PhD, Marie S. O’Neill, PhD, Eliseo Guallar, MD, DrPH, Wendy S. Post, MD, MS, Joel D. Kaufman, MD, MPH, and Ana Navas-Acien, MD, PhD. Race/Ethnicity, Residential Segregation, and Exposure to Ambient Air Pollution: The Multi-Ethnic Study of Atherosclerosis (MESA). AJPH 2014;104(11):2130-2137.

Climate Change: Challenges and Opportunities for Global Health (2014)

  • Importance:  Health is inextricably linked to climate change. It is important for clinicians to understand this relationship in order to discuss associated health risks with their patients and to inform public policy.
  • Objectives:  To provide new US-based temperature projections from downscaled climate modeling and to review recent studies on health risks related to climate change and the cobenefits of efforts to mitigate greenhouse gas emissions.
  • Data Sources, Study Selection, and Data Synthesis:  We searched PubMed from 2009 to 2014 for articles related to climate change and health, focused on governmental reports, predictive models, and empirical epidemiological studies. Of the more than 250 abstracts reviewed, 56 articles were selected. In addition, we analyzed climate data averaged over 13 climate models and based future projections on downscaled probability distributions of the daily maximum temperature for 2046-2065. We also compared maximum daily 8-hour average with air temperature data taken from the National Oceanic and Atmospheric Administration National Climate Data Center.
  • Results:  By 2050, many US cities may experience more frequent extreme heat days. For example, New York and Milwaukee may have 3 times their current average number of days hotter than 32°C (90°F). The adverse health aspects related to climate change may include heat-related disorders, such as heat stress and economic consequences of reduced work capacity; and respiratory disorders, including those exacerbated by fine particulate pollutants, such as asthma and allergic disorders; infectious diseases, including vectorborne diseases and water-borne diseases, such as childhood gastrointestinal diseases; food insecurity, including reduced crop yields and an increase in plant diseases; and mental health disorders, such as posttraumatic stress disorder and depression, that are associated with natural disasters. Substantial health and economic cobenefits could be associated with reductions in fossil fuel combustion. For example, the cost of greenhouse gas emission policies may yield net economic benefit, with health benefits from air quality improvements potentially offsetting the cost of US carbon policies.
  • Conclusions and Relevance:  Evidence over the past 20 years indicates that climate change can be associated with adverse health outcomes. Health care professionals have an important role in understanding and communicating the related potential health concerns and the cobenefits from reducing greenhouse gas emissions.

Patz JA FH, Holloway T, Vimont DJ, Haines A. Climate Change: Challenges and Opportunities for Global Health. JAMA. 2014;online.

Residential Traffic Exposure and Childhood Leukemia: A Systematic Review and Meta-analysis (2014)

  • CONTEXT:  Exposure to elevated concentrations of traffic-related air pollutants in the near-road environment is associated with numerous adverse human health effects, including childhood cancer, which has been increasing since 1975. Results of individual epidemiologic studies have been inconsistent. Therefore, a meta-analysis was performed to examine the association between residential traffic exposure and childhood cancer.
  • EVIDENCE ACQUISITION:  Studies published between January 1980 and July 2011 were retrieved from a systematic search of 18 bibliographic databases. Nine studies meeting the inclusion criteria were identified. Weighted summary ORs were calculated using a random effects model for outcomes with four or more studies. Subgroup and sensitivity analyses were performed.
  • EVIDENCE SYNTHESIS:  Childhood leukemia was positively associated (summary OR=1.53, 95% CI=1.12, 2.10) with residential traffic exposure among seven studies using a postnatal exposure window (e.g., childhood period or diagnosis address) and there was no association (summary OR=0.92, 95% CI=0.78, 1.09) among four studies using a prenatal exposure window (e.g., pregnancy period or birth address). There were too few studies to analyze other childhood cancer outcomes.
  • CONCLUSIONS:  Current evidence suggests that childhood leukemia is associated with residential traffic exposure during the postnatal period, but not during the prenatal period. Additional well-designed epidemiologic studies that use complete residential history to estimate traffic exposure, examine leukemia subtypes, and control for potential confounding factors are needed to confirm these findings. As many people reside near busy roads, especially in urban areas, precautionary public health messages and interventions designed to reduce population exposure to traffic might be warranted.

Boothe VL, Boehmer TK, Wendel AM, Yip FY. (2014). Residential Traffic Exposure and Childhood Leukemia: A Systematic Review and Meta-analysis. Am J Prev Med, 46(4), 413-422. doi: 10.1016/j.amepre.2013.11.004.

“Cobenefits of Replacing Car Trips with Alternative Transportation: A Review of Evidence and Methodological Issues” (2013)

  • It has been reported that motor vehicle emissions contribute nearly a quarter of world energy-related greenhouse gases and cause non-negligible air pollution primarily in urban areas.
  • Reducing car use and increasing ecofriendly alternative transport, such as public and active transport, are efficient approaches to mitigate harmful environmental impacts caused by a large amount of vehicle use. Besides the environmental benefits of promoting alternative transport, it can also induce other health and economic benefits.
  • At present, a number of studies have been conducted to evaluate co-benefits from greenhouse gas mitigation policies. However, relatively few have focused specifically on the transport sector. A comprehensive understanding of the multiple benefits of alternative transport could assist with policy making in the areas of transport, health, and environment. However, there is no straightforward method which could estimate co-benefits effect at one time.
  • In this paper, the links between vehicle emissions and air quality, as well as the health and economic benefits from alternative transport use, are considered, and methodological issues relating to the modelling of these co-benefits are discussed. 

Ting Xia, Ying Zhang, Shona Crabb, and Pushan Shah, . (2013). “Cobenefits of Replacing Car Trips with Alternative Transportation: A Review of Evidence and Methodological Issues,”. Journal of Environmental and Public Health, 2013(Article ID 797312), Article ID 797312. doi: 10.1155/2013/797312

Chronic burden of near-roadway traffic pollution in 10 European cities (APHEKOM network) (2013)

  • Recent epidemiological research suggests that near road traffic-related pollution may cause chronic disease. Childhood asthma attributable to air pollution in 10 European cities was estimated by calculating the number of cases of 1) asthma caused by near road traffic-related pollution, and 2) acute asthma events related to urban air pollution levels. The researchers then expanded their approach to include coronary heart diseases in adults.
  • Derivation of attributable cases required combining concentration-response function (CRF) between exposures and the respective health outcome of interest (obtained from published literature), an estimate of the distribution of selected exposures in the target population, and information about the frequency of the assessed morbidities.
  • Exposure to roads with high vehicle traffic, a proxy for near road traffic-related pollution, accounted for 14% of all asthma cases. When a causal relationship between near road traffic- related pollution and asthma is assumed, 15% of all episodes of asthma symptoms were attributable to air pollution. Without this assumption, only 2% of asthma symptoms were attributable to air pollution. Similar patterns were found for coronary heart diseases in older adults.  In the discussion, the authors suggest that their estimate of cases is likely low, due to under-reporting of cases.  They point out that proximity to traffic will vary across an urban area, so finer analyses may be needed to tease out relationships between air quality and chronic disease burden.
  • The authors conclude that pollutants along busy roads are responsible for a large and preventable share of chronic disease and related acute exacerbation in European urban areas.

Perez L, Declercq C, Aguilera I, et al. (2013). Chronic burden of near-roadway traffic pollution in 10 European cities (APHEKOM network). Eur Respir J. 2013 Mar 21.

"Health Co-Benefits and Transportation-Related Reductions in Greenhouse Gas Emissions in the San Francisco Bay Area" (2013)

  • Background:  Greenhouse gas emissions (GHGE) linked to climate change is the biggest threat to public health worldwide.  California generates 7% of the US GHGE, and is the 12th largest emitter worldwide. Within transportation, the largest emitting sector in California (38%) and personal vehicles are the largest portion of that sector (79%).  Two strategies to reduce emissions include increased use of clean emission vehicles and reducing miles driven.  The latter approach would have the public health benefit of improved health from active transportation and reduced air pollution. The authors quantified transportation strategies to reduce greenhouse gas emissions using both approaches.
  • Statistics on travel patterns and injuries, physical activity, fine particulate matter, and GHGE in the San Francisco Bay Area, California, were input into a model that calculated the health impacts of walking and bicycling short distances usually traveled by car or driving low-emission automobiles. The change in disease burden was calculated in disability-adjusted life years (DALYs) based on dose–response relationships and the distributions of physical activity, particulate matter, and traffic injuries.
  • Increasing median daily walking and bicycling from 4 to 22 minutes reduced the burden of cardiovascular disease and diabetes by 14% (32466 DALYs), increased the traffic injury burden by 39% (5907 DALYS), and decreased GHGE by 14%. Low-carbon driving reduced GHGE by 33.5% and cardiorespiratory disease burden by less than 1%.
  • Increased physical activity associated with active transport could generate a large net improvement in population health. Measures would be needed to minimize pedestrian and bicyclist injuries. Together, active transport and low-carbon driving could achieve GHGE reductions sufficient for California to meet legislative mandates of reducing emissions to 80% of 1990 levels levels by 2050.

Neil Maizlish, PhD, James Woodcock, PhD, Sean Co, MS, Bart Ostro, PhD, Amir Fanai, CEng IMechE, and David Fairley, PhD. (2013). Health Cobenefits and Transportation-Related Reductions in Greenhouse Gas Emissions in the San Francisco Bay Area. Am J Public Health, e1-e7. doi: doi:10.2105/AJPH. 2012.300939

“Costs of Childhood Asthma Due to Traffic-Related Pollution in Two California Communities.” (2012)

  • Recent research suggests the burden of childhood asthma that is attributable to air pollution has been underestimated in traditional risk assessments, and there are no estimates of these associated costs.
  • This study aimed to estimate the yearly childhood asthma-related costs attributable to air pollution for Riverside and Long Beach, CA, USA, including: 1) the indirect and direct costs of healthcare utilization due to asthma exacerbations linked with traffic-related pollution (TRP); and 2) the costs of health care for asthma cases attributable to local TRP exposure.
  • The authors calculated costs using estimates from peer-reviewed literature and the authors’ analysis of surveys (Medical Expenditure Panel Survey, California Health Interview Survey, National Household Travel Survey, and Health Care Utilization Project).
  • A lower-bound estimate of the asthma burden attributable to air pollution was US$18 million yearly. Asthma cases attributable to TRP exposure accounted for almost half of this cost. The cost of bronchitic episodes was a major proportion of both the annual cost of asthma cases attributable to TRP and of pollution-linked exacerbations.
  • Traditional risk assessment methods underestimate both the burden of disease and cost of asthma associated with air pollution, and these costs are borne disproportionately by communities with higher than average TRP.

Brandt, S. J., L. Perez, et al. (2012). Costs of Childhood Asthma Due to Traffic-Related Pollution in Two California Communities. European Respiratory Journal 40(2): 363-370.

“Near-Roadway Pollution and Childhood Asthma: Implications for Developing “Win-Win” Compact Urban Development and Clean Vehicle Strategies” (2012)

  • The emerging consensus that exposure to near-roadway traffic-related pollution causes asthma has implications for compact urban development policies designed to reduce driving and greenhouse gases.
  • The authors estimated the current burden of childhood asthma-related disease attributable to near-roadway and regional air pollution in Los Angeles County (LAC) and the potential health impact of regional pollution reduction associated with changes in population along major traffic corridors. The burden of asthma attributable to the dual effects of near-roadway and regional air pollution was estimated, using nitrogen dioxide and ozone as markers of urban combustion-related and secondary oxidant pollution, respectively.
  • The authors also estimated the impact of alternative scenarios that assumed a 20% reduction in regional pollution in combination with a ± 3.6% increase in the proportion of the total population living near major roads, a proxy for near-roadway exposure.
  • The authors estimated that 27,100 cases of childhood asthma (8% of total) in LAC were at least partly attributable to pollution associated with residential location within 75m of a major road. As a result, a substantial proportion of asthma-related morbidity is a consequence of near-roadway pollution, even if symptoms are triggered by other factors. Benefits resulting from a 20% regional pollution reduction varied markedly depending on the associated change in near-roadway proximity.
  • Study findings suggest that there are large and previously unappreciated public health consequences of air pollution in LAC and probably in other metropolitan areas with dense traffic corridors. To maximize health benefits, compact urban development strategies should be coupled with policies to reduce near-roadway pollution exposure.

Perez, L., F. Lurmann, et al. (2012) Near-Roadway Pollution and Childhood Asthma: Implications for Developing “Win-Win” Compact Urban Development and Clean Vehicle Strategies. Environmental Health Perspectives 120:1619–1626

“Traffic-Related Air Pollution, Particulate Matter, and Autism” (2012)

  • Autism is a heterogeneous disorder with genetic and environmental factors likely contributing to its origins. Examination of hazardous pollutants has suggested the importance of air toxics in the etiology of autism, yet little research has examined its association with local levels of air pollution using residence-specific exposure assignments. This study examines the relationship between traffic-related air pollution, air quality, and autism.
  • This population-based case-control study includes data obtained from 279 children with autism and 245 control children with typical development who were enrolled in the Childhood Autism Risks from Genetics and the Environment study in California.
  • The mother's address from the birth certificate and addresses reported from a residential history questionnaire were used to estimate exposure for each trimester of pregnancy and first year of life. Traffic-related air pollution was assigned to each location using a line-source air-quality dispersion model. Regional air pollutant measures were based on the Environmental Protection Agency's Air Quality System data. Logistic regression models compared estimated and measured pollutant levels for children with autism and for control children with typical development. The main outcome measures were crude and multivariable adjusted odds ratios (AORs) for autism.
  • Children with autism were more likely to live at residences that had the highest quartile of exposure to traffic-related air pollution, during gestation and during the first year of life, compared with control children. All regional pollutant estimates were scaled to twice the standard deviation of the distribution for all pregnancy estimates.
  • Exposure to traffic-related air pollution, nitrogen dioxide, PM2.5, and PM10 during pregnancy and during the first year of life was associated with autism. Further epidemiological and toxicological examinations of likely biological pathways will help determine whether these associations are causal.

Volk H.E., Lurmann, F., Penfold, B., Hertz-Picciotto, I., McConnell, R.  (2012). Traffic-Related Air Pollution, Particulate Matter, and Autism. Archives of General Psychiatry 1-7.

“Air Quality and Exercise-Related Health Benefits from Reduced Car Travel in the Midwestern United States” (2012)

  • Automobile exhaust contains precursors to ozone and fine particulate matter (PM ≤ 2.5 µm in aerodynamic diameter; PM2.5), posing health risks. Dependency on car commuting also reduces physical fitness opportunities.
  • In this study, the authors sought to quantify benefits from reducing automobile usage for short urban and suburban trips.
  • The authors simulated census-tract level changes in hourly pollutant concentrations from the elimination of automobile round trips ≤ 8 km in 11 metropolitan areas in the upper Midwestern United States using the Community Multiscale Air Quality (CMAQ) model. Next, they estimated annual changes in health outcomes and monetary costs expected from pollution changes using the U.S. Environmental Protection Agency Benefits Mapping Analysis Program (BenMAP). In addition, the authors used the World Health Organization Health Economic Assessment Tool (HEAT) to calculate benefits of increased physical activity if 50% of short trips were made by bicycle.
  • The authors estimate that, by eliminating these short automobile trips, annual average urban PM2.5 would decline by 0.1 µg/m3 and that summer ozone (O3) would increase slightly in cities but decline regionally, resulting in net health benefits of $4.94 billion/year [95% confidence interval (CI): $0.2 billion, $13.5 billion), with 25% of PM2.5 and most O3 benefits to populations outside metropolitan areas. Across the study region of approximately 31.3 million people and 37,000 total square miles, mortality would decline by approximately 1,295 deaths/year (95% CI: 912, 1,636) because of improved air quality and increased exercise. Making 50% of short trips by bicycle would yield savings of approximately $3.8 billion/year from avoided mortality and reduced health care costs (95% CI: $2.7 billion, $5.0 billion]. They also estimate that the combined benefits of improved air quality and physical fitness would exceed $8 billion/year.
  • The study findings suggest that significant health and economic benefits are possible if bicycling replaces short car trips. Less dependence on automobiles in urban areas would also improve health in downwind rural settings.

Grabow, M. L., S. N. Spak, et al. (2012). “Air Quality and Exercise-Related Health Benefits from Reduced Car Travel in the Midwestern United States.” Environmental Health Perspectives 120(1): 68.

“Health Co-Benefits and Transportation-Related Reductions in Greenhouse Gas Emissions in the Bay Area: Technical Report" (2012)

  • This study assessed the forecasted health impacts associated with different strategies to reduce GHG from automobiles.
  • Governmental researchers from CDPH and Bay Area transportation and air quality organizations teamed up with researchers from the London School of Hygiene and Tropical Medicine to try to answer the question: "What might be the health benefits or harms associated with active transport or low carbon driving?"
  • The current research attempted to adapt this model to the health and travel patterns of Bay Area residents. The model uses statistical data on deaths, life shortening illness and injury, and years living with disability for major health conditions strongly linked to physical activity, traffic injuries, and the fine particles in air pollution that can reach deep into the lungs.
  • At high levels of active transport, the model predicts annually 13% fewer premature deaths and 15% fewer years of life lost for cardiovascular disease and diabetes and 5% reductions in each of four other chronic diseases. After accounting for a 19% increase in the disease burden from fatal and serious traffic injuries to pedestrians and bicyclists, the Bay Area would still experience annually 2,236 fewer deaths and 22,807 years of life gained.
  • Because it reduces air pollution, low carbon driving yields 22 fewer deaths and a gain of 232 years of life lost from heart and respiratory disease; however, increased physical activity rather than less air pollution accounts for almost all the health benefits. While low carbon driving generated little health co-benefits, it is estimated to reduce GHG emissions 9% to 33.5% from the 2000 baseline. The most ambitious active transport scenario would achieve from 9% to 14.5% in GHG reductions.
  • Reducing risks from chronic disease of the magnitude suggested by this research would reduce the estimated $34 billion annual cost in California from cardiovascular disease and other chronic conditions such as obesity.

Maizlish, N., J. Woodcock, et al. "Health Co-Benefits and Transportation-Related Reductions in Greenhouse Gas Emissions in the Bay Area: Technical Report."

“Traffic-Related Air Pollution and Development of Allergic Sensitization in Children During the First 8 Years of Life” (2012)

  • The role of exposure to air pollution in the development of allergic sensitization remains unclear.
  • We sought to assess the development of sensitization until school age related to longitudinal exposure to air pollution from road traffic.
  • More than 2500 children in the birth cohort BAMSE (Children, Allergy, Milieu, Stockholm, Epidemiological Survey) from Stockholm, Sweden, were followed with repeated questionnaires and blood sampling until 8 years of age. Outdoor concentrations of nitrogen oxides, as a marker of exhaust particles, and particles with an aerodynamic diameter of less than 10 μm (PM10), mainly representing road dust, were assigned to residential, day care, and school addresses by using dispersion models. Time-weighted average exposures were linked to levels of IgE against common inhalant and food allergens at 4 and 8 years of age.
  • Air pollution exposure during the first year of life was associated with an increased risk of pollen sensitization at 4 years of age (odds ratio, 1.83; 95% confidence interval, 1.02-3.28) for a 5th to 95th difference in exposure to nitrogen oxides. At 8 years, there was no general increase in the risk of sensitization; however, the risk of food sensitization was increased, particularly among children free of sensitization at 4 years of age (odds ratio, 2.30; 95% confidence interval, 1.10-4.82). Results were similar by using PM10. No associations between air pollution exposure after the first year of life and sensitization were seen.
  • Traffic-related air pollution exposure does not seem to increase the overall risk of sensitization to common inhalant and food allergens up to school age, but sensitization to certain allergens might be related to exposure during infancy.

Gruzieva, O., T. Bellander, et al. (2012). "Traffic-related air pollution and development of allergic sensitization in children during the first 8 years of life." Journal of Allergy and Clinical Immunology 129(1): 240-246.

“Kids and Cars: Environmental Attitudes in Children” (2011)

  • This article aims to supplement scarce research on the children’s attitudes to cars and the environment. Assuming that attitudes to cars develop in childhood, this article draws upon the writing assignments and interviews exploring the upper-elementary school children’s attitudes to cars.
  • The study was conducted in Amsterdam, The Netherlands, between January and December 2010.
  • Briefly examining existing research on children’s environmental attitudes in general, and in relation to cars in particular, the author argues that in-depth qualitative research is essential to the understanding of the factors that explain present attitudes and perhaps predicting the behavior of future drivers.
  • In conclusion, the author makes a recommendation for the development of a curriculum addressing the development of children’s awareness of sustainable transportation and the environmental implications of car driving.

Kopnina, Helen. (2011). “Kids and cars: Environmental attitudes in children.” Transport Policy 18(4): 573-578.

“Can Smart Growth Policies Conserve Energy and Reduce Emissions?” (2011)

  • This article examines the role smart growth can play in achieving planning objectives, including energy conservation and emission reductions. It summarizes existing literature on land use impacts on travel activity, energy consumption and pollution emissions. It examines claims that smart growth policies are ineffective and harmful.
  • Land use policies can significantly affect transportation options and costs, and therefore travel activity. People who live and work in automobile-dependent locations tend to drive more annual miles, consume more fuel and produce more pollution than they would in more accessible, multi-modal communities. As a result, smart growth reforms can provide various economic, social and environmental benefits.
  • Some critics claim that these impacts are small and not cost effective but their analysis tends to misrepresent key issues. The only consider land use density, ignoring the effects of other land use factors such as regional accessibility, land use mix, road and path connectivity, transport system diversity, and parking management. They overlook additional benefits, and growing consumer demand for more accessible, multi-modal home locations. As a result, they underestimate smart growth impacts and benefits.
  • This is important because existing land use development policies and planning practices tend to favor sprawl and automobile dependency. Smart growth requires policy reforms that allow more compact and mixed development, support alternative modes, and reduce existing subsidies to automobile such as generous minimum parking requirements. These reforms tend to face institutional inertia and political opposition. It is therefore important to have accurate information on the full potential impacts and benefits of smart growth policy reforms. When all impacts are considered, smart growth policies are often a cost effective way to achieve planning objectives.

Litman, Todd. (2011). “Can Smart Growth Policies Conserve Energy and Reduce Emissions?” Portland State University’s Center for Real Estate Quarterly 5(2): 21-30.

See 2011 and Earlier Archived Articles