Diesel exhaust is the gaseous exhaust produced by a diesel type of internal combustion engine, plus any contained particulates. Its composition may vary with the fuel type or rate of consumption, or speed of engine operation (e.g., idling or at speed), and whether the engine is in an on-road vehicle, farm vehicle, locomotive, marine vessel, or stationary generator or other application.
Diesel exhaust is a Group 1 carcinogen, which causes lung cancer and has a positive association with bladder cancer. It contains several substances that are also listed individually as human carcinogens by the IARC.
Methods exist to reduce nitrogen oxides (NOx) and particulate matter (PM) in the exhaust.
- 1 Composition
- 2 Regulation
- 3 Health concerns
- 4 Ecological effects
- 5 Remedies
- 6 Further reading
- 7 See also
- 8 References and notes
- 9 External links
The physical and chemical conditions that exist inside any such diesel engines under any conditions differ considerably from spark-ignition engines, because, by design, diesel engine power is directly controlled by the fuel supply, not by control of the air/fuel mixture, as in conventional gasoline engines. As a result of these differences, diesel engines generally produce a different array of pollutants than spark-driven engines, differences that are sometimes qualitative (what pollutants are there, and what are not), but more often quantitative (how much of particular pollutants or pollutant classes are present in each). For instance, diesel engines produce one-twenty-eighth the carbon monoxide that gasoline engines do, as they burn their fuel in excess air even at full load.
However, the lean-burning nature of diesel engines and the high temperatures and pressures of the combustion process result in significant production of gaseous nitrogen oxides (NOx), an air pollutant that constitutes a unique challenge with regard to their reduction.[not verified in body] While total nitrogen oxides from petrol cars have decreased by around 96% through adoption of exhaust catalytic converters as of 2012, diesel cars still produce nitrogen oxides at a similar level to those bought 15 years ago under real world tests; hence, diesel cars emit around 20 times more nitrogen oxides than petrol cars. Modern on-road diesel engines typically use selective non-catalytic reduction (SNCR) systems to meet emissions laws, as other methods such as exhaust gas recirculation (EGR) cannot adequately reduce NOx to meet the newer standards applicable in many jurisdictions. Auxiliary diesel systems designed to remediate the nitrogen oxide pollutants are described in a separate section below.
Moreover, the fine particles (fine particulate matter) in diesel exhaust (e.g., soot, sometimes visible as opaque dark-colored smoke) has traditionally been of greater concern, as it presents different health concerns and is rarely produced in significant quantities by spark-ignition engines. These especially harmful particulate contaminants are at their peak when such engines are run without sufficient oxygen to fully combust the fuel; when a diesel engine runs at idle, enough oxygen is usually present to burn the fuel completely. (The oxygen requirement in non-idling engines is usually mitigated using turbocharging.) As a result of the particulate emissions, exhaust from diesel vehicles has been reported to be significantly more harmful than those from petrol vehicles.
Diesel exhausts, long known for their characteristic smells, changed significantly with the reduction of sulfur content of diesel fuel, and again when catalytic converters were introduced in exhaust systems.[not verified in body] Even so, diesel exhausts continue to contain an array of inorganic and organic pollutants, in various classes, and in varying concentrations (see below), depending on fuel composition and engine running conditions.
The following are classes of chemical compounds that have been found in diesel exhaust.
|Class of chemical contaminant||Note|
|antimony compounds||Toxicity similar to arsenic poisoning|
|beryllium compounds||IARC Group 1 carcinogens|
|chromium compounds||IARC Group 3 carcinogens|
|dioxins and dibenzofurans|
|mercury compounds||IARC Group 3 carcinogens|
|nitrogen oxides||5.6 ppm or 6500 μg/m³|
|polycyclic organic matter, including
polycyclic aromatic hydrocarbons (PAHs)
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International and federal
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To rapidly reduce particulate matter from heavy-duty diesel engines in California, the California Air Resources Board created the Carl Moyer Program to provide funding for upgrading engines ahead of emissions regulations. In 2008 the California Air Resources Board also implemented the 2008 California Statewide Truck and Bus Rule which requires all heavy-duty diesel trucks and buses, with a few exceptions, that operate in California to either retrofit or replace engines in order to reduce diesel particulate matter. The US Mine Safety and Health Administration (MSHA) issued a health standard in January 2001 designed to reduce diesel exhaust exposure in underground metal and nonmetal mines; on September 7, 2005, MSHA published a notice in the Federal Register proposing to postpone the effective date from January 2006 until January 2011.
Emissions from diesel vehicles have been reported to be significantly more harmful than those from petrol vehicles.[better source needed] Diesel combustion exhaust is a source of atmospheric soot and fine particles, which is a component of the air pollution implicated in human cancer, heart and lung damage, and mental functioning. Moreover, diesel exhaust contains contaminants listed as carcinogenic for humans by the IARC (part of the World Health Organization of the United Nations), as present in their List of IARC Group 1 carcinogens. Diesel exhaust pollution is thought[by whom?] to account for around one quarter of the pollution in the air in previous decades,[when?] and a high share of sickness caused by automotive pollution.[better source needed]
Occupational health effects
Exposure to diesel exhaust and diesel particulate matter (DPM) is an occupational hazard to truckers, railroad workers, and miners using diesel-powered equipment in underground mines. Adverse health effects have also been observed in the general population at ambient atmospheric particle concentrations well below the concentrations in occupational settings.
In March 2012, U.S. government scientists showed that underground miners exposed to high levels of diesel fumes have a threefold increased risk for contracting lung cancer compared with those exposed to low levels. The $11.5 million Diesel Exhaust in Miners Study (DEMS) followed 12,315 miners, controlling for key carcinogens such as cigarette smoke, radon, and asbestos. This allowed scientists to isolate the effects of diesel fumes.
For over 10 years, concerns have been raised in the USA regarding children's exposure to DPM as they ride diesel-powered school buses to and from school. In 2013, the Environmental Protection Agency (EPA) established the Clean School Bus USA initiative in an effort to unite private and public organizations in curbing student exposures.
Concerns regarding particulates
Diesel particulate matter (DPM), sometimes also called diesel exhaust particles (DEP), is the particulate component of diesel exhaust, which includes diesel soot and aerosols such as ash particulates, metallic abrasion particles, sulfates, and silicates. When released into the atmosphere, DPM can take the form of individual particles or chain aggregates, with most in the invisible sub-micrometre range of 100nanometers, also known as ultrafine particles (UFP) or PM0.1.
The main particulate fraction of diesel exhaust consists of fine particles. Because of their small size, inhaled particles may easily penetrate deep into the lungs. The rough surfaces of these particles makes it easy for them to bind with other toxins in the environment, thus increasing the hazards of particle inhalation.[verification needed]
A study of particulate matter (PM) emissions from transit buses running on ULSD and soybean biodiesel (B20) was reported by Omidvarborna and coworkers, where they conclude PM emissions appeared lower in cases of biodiesel use, where they were dependent on the engine model, cold and hot idle modes, and fuel type, and that heavy metals in PM emitted during hot idling were greater than those from cold idling; reasons for PM reduction in biodiesel emissions were suggested to result from the oxygenated structure of biodiesel fuel, as well as arising from changes in technology (including the use of a catalytic converter in this test system).
Exposures have been linked with acute short-term symptoms such as headache, dizziness, light-headedness, nausea, coughing, difficult or labored breathing, tightness of chest, and irritation of the eyes and nose and throat. Long-term exposures can lead to chronic, more serious health problems such as cardiovascular disease, cardiopulmonary disease, and lung cancer. Elemental carbon attributable to traffic was significantly associated with wheezing at age 1 and persistent wheezing at age 3 in the Cincinnati Childhood Allergy and Air Pollution Study birth cohort study.
The NERC-HPA funded Traffic Pollution and Health in London project at King's College London is currently[when?] seeking to refine understanding of the health effects of traffic pollution. Ambient traffic-related air pollution was associated with decreased cognitive function in older men.
Mortality from diesel soot exposure in 2001 was at least 14,400 out of the German population of 82 million, according to the official report 2352 of the Umweltbundesamt Berlin (Federal Environmental Agency of Germany).
The study of nanoparticles and nanotoxicology is in its infancy, and health effects from nanoparticles produced by all types of diesel engines are still being uncovered. It is clear, that diesel health detriments of fine particle emissions are severe and pervasive. Although one study found no significant evidence that short-term exposure to diesel exhaust results in adverse extrapulmonary effects, effects that are correlated with an increase in cardiovascular disease, a 2011 study in The Lancet concluded that traffic exposure is the single most serious preventable trigger of heart attack in the general public, as the cause of 7.4% of all attacks. It is impossible to tell how much of this effect is due to the stress of being in traffic and how much is due to exposure to exhaust.
Since the study of the detrimental health effects of nanoparticles (nanotoxicology) is still in its infancy, and the nature and extent of negative health impacts from diesel exhaust continues to be discovered. There is little controversy, however, that the public health impact of diesels is higher than that of petrol-fuelled vehicles despite the wide uncertainties.
Variation with engine conditions
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The types and quantities of nanoparticles can vary according to operating temperatures and pressures, presence of an open flame, fundamental fuel type and fuel mixture, and even atmospheric mixtures. As such, the resulting types of nanoparticles from different engine technologies and even different fuels are not necessarily comparable. One study has shown that 95% of the volatile component of diesel nanoparticles is unburned lubricating oil. Long-term effects still need to be further clarified, as well as the effects on susceptible groups of people with cardiopulmonary diseases.
Diesel engines can produce black soot (or more specifically diesel particulate matter) from their exhaust. The black smoke consists of carbon compounds that have not burned because of local low temperatures where the fuel is not fully atomized. These local low temperatures occur at the cylinder walls, and at the surface of large droplets of fuel. At these areas where it is relatively cold, the mixture is rich (contrary to the overall mixture which is lean). The rich mixture has less air to burn and some of the fuel turns into a carbon deposit. Modern car engines use a diesel particulate filter (DPF) to capture carbon particles and then intermittently burn them using extra fuel injected directly into the filter. This prevents carbon buildup at the expense of wasting a small quantity of fuel.
The full load limit of a diesel engine in normal service is defined by the "black smoke limit", beyond which point the fuel cannot be completely burned. As the "black smoke limit" is still considerably lean of stoichiometric, it is possible to obtain more power by exceeding it, but the resultant inefficient combustion means that the extra power comes at the price of reduced combustion efficiency, high fuel consumption and dense clouds of smoke. This is only done in high performance applications where these disadvantages are of little concern.
When starting from cold, the engine's combustion efficiency is reduced because the cold engine block draws heat out of the cylinder in the compression stroke. The result is that fuel is not burned fully, resulting in blue and white smoke and lower power outputs until the engine has warmed. This is especially the case with indirect injection engines, which are less thermally efficient. With electronic injection, the timing and length of the injection sequence can be altered to compensate for this. Older engines with mechanical injection can have mechanical and hydraulic governor control to alter the timing, and multi-phase electrically controlled glow plugs, that stay on for a period after start-up to ensure clean combustion; the plugs are automatically switched to a lower power to prevent their burning out.
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With emissions standards increasing, diesel engines are having to become more efficient and have fewer pollutants in their exhaust. For instance, light duty truck must now have NOx emissions less than 0.07 g/mile,[when?] and in the U.S., by 2010, NOx emissions must be less than 0.03 g/mile. Moreover, in recent years the United States, Europe, and Japan have extended emissions control regulations from covering on-road vehicles to include farm vehicles and locomotives, marine vessels, and stationary generator applications. Engineers have come up with two principle and distinct systems to all on-market products meet the U.S. 2010 emissions criteria,[needs update] selective non-catalytic reduction (SNCR), and exhaust gas recirculation (EGR). Both are in the exhaust system of diesel engines, and are further designed to promote efficiency.
Selective non-catalytic reduction
Selective non-catalytic reduction (SNCR) injects a reductant such as ammonia or urea — the latter aqueous, where it is known as diesel exhaust fluid, DEF) — into the exhaust of a diesel engine to convert nitrogen oxides (NOx) into gaseous dinitrogen and water. SNCR systems have been prototyped that reduce 90% of the NOx in the exhaust system, with commercialized systems being somewhat lower. SNCR systems do not necessarily need particulate matter (PM) filters; when SNCR and PM filters are combined, some engines have been shown to be 3-5% more fuel efficient. A disadvantage of the SNCR system, in addition to added upfront development cost (which can be offset by compliance and improved performance), is the need to refill the reductant, the periodicity of which varies with the miles driven, load factors, and the hours used.[full citation needed][better source needed][third-party source needed] The SNCR system is not as efficient at higher revolutions per minute (rpm). SNCR is being optimized to have higher efficiency with broader temperatures, to be more durable, and to meet other commercial needs.
Exhaust gas recirculation
Exhaust gas recirculation (EGR), on diesel engines, can be used to achieve a richer fuel to air mixture and a lower peak combustion temperature. Both effects reduce NOx emissions, but can negatively impact efficiency and the production of soot particles. The richer mix is achieved by displacing some of the intake air, but is still lean compared to petrol engines, which approach the stoichiometric ideal. The lower peak temperature is achieved by a heat exchanger that removes heat prior to re-entering the engine, and works due to the exhaust gases' higher specific heat than air. With the greater soot production, EGR is often combined with a particulate matter (PM) filter in the exhaust.[full citation needed] In turbocharged engines, EGR needs a controlled pressure differential across the exhaust manifold and intake manifold, which can be met by such engineering as use of a variable geometry turbocharger, which has inlet guide vanes on the turbine to build exhaust backpressure in the exhaust manifold directing exhaust gas to the intake manifold. It also requires additional external piping and valving, and so requires additional maintenance. 
John Deere, the farm equipment manufacturer is implementing such a combined SNCR-EGR design, in a 9-liter "inline 6" diesel engine that involves both system types, a PM filter and additional oxidation catalyst technologies.[better source needed][third-party source needed] The combined system incorporates two turbochargers, the first on the exhaust manifold, with variable geometry and containing the EGR system; and a second a fixed geometry turbocharger. Recirculated exhaust gas and the compressed air from the turbochargers have separate coolers, and air merges before entering the intake manifold, and all subsystems are controlled by a central engine control unit that optimizes minimization of pollutants released in the exhaust gas.
A new technology being tested in 2016 has been created by Air Ink which collects carbon particles using a "Kaalink" cylindrical device that is retrofitted into a vehicle's exhaust system, after processing to remove heavy metals and carcinogens, the company plans to use the carbon to make ink.
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- Department of Labor, Mine Safety and Health Administration. Diesel Particulate Matter Exposure of Underground Metal and Nonmetal Miners: Final Rule, January 19, 2001. Federal Register 66(13):5706.
- Monforton, C (2006). "Weight of the Evidence or Wait for the Evidence? Protecting Underground Miners from Diesel Particulate Matter". American Journal of Public Health. 96 (2): 271–276. doi:10.2105/ajph.2005.064410.
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- Wichmann, H.-E. Abschaetzung positiver gesundheitlicher Auswirkungen durch den Einsatz von Partikelfiltern bei Dieselfahrzeugen in Deutschland Umweltbundesamt Berlin 2003. Report 2352, especially page 32
- Umweltbundesamt Berlin Future Diesel. Abgasgesetzgebung Pkw, leichte Nfz und Lkw – Fortschreibung der Grenzwerte bei Dieselfahrzeugen 2003. Report 2353, especially page 25
- Vehicle emissions control
- Carl Moyer Program
- National Emissions Standards for Hazardous Air Pollutants
- List of IARC Group 1 carcinogens
- List of IARC Group 2A carcinogens
- List of IARC Group 2B carcinogens
- List of IARC Group 3 carcinogens
- Volkswagen emissions violations
References and notes
- Lippmann, Morton, ed. (2009). Environmental Toxicants (PDF). pp. 553, 555, 556, 562. doi:10.1002/9780470442890. ISBN 9780470442890.
composition can vary markedly with fuel composition, engine type, operating conditions ... combustion of petroleum fuel produces primarily carbon dioxide, water, and nitrogen ... The health risks lie in the small, invisible or poorly visible particles ... carbon (EC) core of diesel soot ... serves as a nucleus for condensation of organic compounds from unburned or incompletely burned fuel ... it still appears that nitrated PAHs are the most predominant bacterial mutagens
- "IARC: DIESEL ENGINE EXHAUST CARCINOGENIC" (Press release). International Agency for Research on Cancer (IARC). June 12, 2012. Retrieved August 14, 2016.
The scientific evidence was reviewed thoroughly by the Working Group and overall it was concluded that there was sufficient evidence in humans for the carcinogenicity of diesel exhaust. The Working Group found that diesel exhaust is a cause of lung cancer (sufficient evidence) and also noted a positive association (limited evidence) with an increased risk of bladder cancer
- "Report on Carcinogens: Diesel Exhaust Particulates" (PDF). National Toxicology Program, Department of Health and Human Services. October 2, 2014.
Exposure to diesel exhaust particulates is reasonably anticipated to be a human carcinogen, based on limited evidence of carcinogenicity from studies in humans and supporting evidence from studies in experimental animals and mechanistic studies.
- "Diesel engine exhaust; CASRN N.A." (PDF). U.S. Environmental Protection Agency. 2003-02-28.
Using U.S. EPA's revised draft 1999 Guidelines for Carcinogen Risk Assessment (U.S. EPA, 1999), diesel exhaust (DE) is likely to be carcinogenic to humans by inhalation from environmental exposures.
- Silverman, Debra T.; Samanic, Claudine M.; Lubin, Jay H.; Blair, Aaron E.; Stewart, Patricia A.; Vermeulen, Roel; Coble, Joseph B.; Rothman, Nathaniel; Schleiff, Patricia L. (2012-06-06). "The Diesel Exhaust in Miners study: a nested case-control study of lung cancer and diesel exhaust". Journal of the National Cancer Institute. 104 (11): 855–868. doi:10.1093/jnci/djs034. ISSN 1460-2105. PMC . PMID 22393209.
- Attfield, Michael D.; Schleiff, Patricia L.; Lubin, Jay H.; Blair, Aaron; Stewart, Patricia A.; Vermeulen, Roel; Coble, Joseph B.; Silverman, Debra T. (2012-06-06). "The Diesel Exhaust in Miners study: a cohort mortality study with emphasis on lung cancer". Journal of the National Cancer Institute. 104 (11): 869–883. doi:10.1093/jnci/djs035. ISSN 1460-2105. PMC . PMID 22393207.
- IARC. "Diesel Engine Exhaust Carcinogenic" (Press release). International Agency for Research on Cancer (IARC). Retrieved June 12, 2012.
After a week-long meeting of international experts, the International Agency for Research on Cancer (IARC), which is part of the World Health Organization (WHO), today classified diesel exhaust as probably carcinogenic to humans (Group 1), based on enough evidence that exposure is associated with an increased risk of lung cancer.
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New diesels produce similar nitrogen oxides to those bought 15 years ago. Typical modern diesel cars emit around 20 times more nitrogen oxides than petrol cars.
- Lean, Geoffrey (Jul 19, 2013). "Why is killer diesel still poisoning our air?". The Telegraph. Retrieved 5 June 2015.
Much of the problem is down to EU emission standards, which have long allowed diesel engines to emit much more nitrogen dioxide than petrol ones.
- Carslaw D., Beevers, S., Westmoreland E., Williams, M., Tate, J., Murrells, T., Stedman, J., Li, Y., Grice, S., Kent A, and Tsagatakis, I. (2011). Trends in NOX and NO2 emissions and ambient measurements in the UK. London: Department for Environment, Food and Rural Affairs.
However, vehicles registered from 2005–2010 emit similar or higher levels of NOx compared with vehicles prior to 1995. In this respect, NOx emissions from diesel cars have changed little over a period of about 20 years.
- Omidvarbornaa, Hamid; Kumara, Ashok; Kim, Dong-Shik (2015). "Recent Studies on Soot Modeling for Diesel Combustion". Renewable and Sustainable Energy Reviews. 48: 635–647. doi:10.1016/j.rser.2015.04.019.
- Board, California Air Resources. "The Report on Diesel Exhaust". www.arb.ca.gov. Retrieved 2016-10-11.
Diesel exhaust includes ... acetaldehyde; antimony compounds; arsenic; benzene; beryllium compounds; bis(2-ethylhexyl)phthalate; dioxins and dibenzofurans; formaldehyde; inorganic lead; mercury compounds; nickel; POM (including PAHs); and styrene.
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- "CDC: Phthalates Overview".
High doses of di-2-ethylhexyl phthalate (DEHP), dibutyl phthalate (DBP), and benzylbutyl phthalate (BzBP) during the fetal period produced lowered testosterone levels, testicular atrophy, and Sertoli cell abnormalities in the male animals and, at higher doses, ovarian abnormalities in the female animals (Jarfelt et al., 2005; Lovekamp-Swan and Davis, 2003; McKee et al., 2004; NTP-CERHR, 2003a, 2003b, 2006).
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Acute (short-term) exposure ... results in irritation of the eyes, mucous membranes, ... Chronic (long-term) exposure ... has resulted in effects on the peripheral and central nervous systems and the liver and kidney.
- Report on Carcinogens Background Document for Diesel Exhaust Particulates (PDF). National Toxicology Program. December 3, 1998.
Concentration (ng/mg extract) ... Concentration (µg/g of particles)
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- Google search
- Vidal, John (Jan 27, 2013). "Diesel fumes more damaging to health than petrol engines". The Guardian. Retrieved 5 June 2015.
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- "... [O]dds ratios and frequencies of each trigger were used to compute population-attributable fractions (PAFs), which estimate the proportion of cases that could be avoided if a risk factor were removed. PAFs depend not only on the risk factor strength at the individual level but also on its frequency in the community. ... [T]he exposure prevalence for triggers in the relevant control time window ranged from 0.04% for cocaine use to 100% for air pollution. ... Taking into account the OR and the prevalences of exposure, the highest PAF was estimated for traffic exposure (7.4%) ...
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