Engineering Clean Air:
The Continuous Improvement of Diesel Engine Emission Performance
The Technology of Clean Diesel Engines, Current and Future
March, 2001
One Dulles Tech Center 2191 Fox Mill Road, Suite 100
Herndon, Virginia 20171
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Executive Summary
The diesel industry has made great progress on a path of continuous improvement to virtually eliminate the key pollutants associated with on-road diesel engines. This transformation is of critical importance, because diesel plays a central role in economic activity. This paper (1) explains the inherent performance advantages of diesel; (2) provides an emissions profile of diesel as the starting point for emissions reduction; (3) documents the major emissions reductions that have been made to date, and explains the technologies that have made them possible;
and (4) describes the technologies that will be employed over the next decade to achieve the virtual elimination of key pollutants.
Performance advantages of diesel. The transformation of diesel emissions performance is of critical importance to the economy. Diesel is the
world's most efficient internal combustion engine. It provides both more power and more fuel efficiency than alternatives such as gasoline, compressed natural gas or liquefied natural gas. Diesel accordingly plays a central role in a wide range of economic activities. In the United States, 94% of all freight is moved by diesel power, and diesel is a critical part of a wide range of activities in transportation, agriculture, construction, mining, electric power generation, and fire and rescue services. Diesel's inherent performance advantages include:
• More power at lower engine speeds;
• Better fuel efficiency;
• Greater safety;
• More durability; and
• More power from a given engine size.
Diesel emissions profile. It is not widely recognized that diesel has some environmental advantages over other types of engines. Of the five major emissions from internal combustion engines – carbon monoxide, hydrocarbons, carbon dioxide, particulate matter and nitrogen oxides – diesel emits only small amounts of the first three. The challenge for diesel is reducing particulate matter (PM) and nitrogen oxides (NOx), and it is in those two emissions that vast
improvements have been made.
Technologies found in today's clean diesel engines. Particulate
matter emissions of new on-highway diesel engines have been reduced 83% since
1988. Emissions of nitrogen oxides have been reduced by 63% during the same time
period. This has been accomplished largely through improvements in fuel delivery,
the design of combustion chambers, and turbocharging. Electronic fuel injection
has permitted engine manufacturers to control fuel injection independently of
engine speed, permitting injection to be optimized for emissions performance. Fuel
also is injected at very high pressures to ensure a more complete burn, and the timing of fuel injection can be varied to meet emissions goals under different operating conditions. Combustion chamber design has been enhanced in a variety of ways. Turbocharging has been widely adopted, and has been refined by the development of air-to-air charge cooling to reduce combustion temperatures.
Nitrogen oxides reductions for 2004. Emissions standards for 2004 will cut NOx emissions in half for on-highway diesel engines, effecting an 83% total reduction since 1988. Exhaust gas recirculation (EGR) technology and advanced fuel injection/combustion control systems will play a major role in this reduction.
EGR lowers the temperature of the fuel burn by recirculating oxygen-depleted exhaust gases into the cylinders, reducing the oxygen content of the air involved in the burn. Advanced fuel injection/combustion control systems permit fuel pressure to be controlled independently from engine speed, allowing fuel injection to be shaped to meet temperature control and other emissions objectives.
Technologies to virtually eliminate key pollutants. The next wave of emissions reductions will arise from recently adopted 2007-2010 highway diesel engine standards. The new regulations calls for the reduction of both PM and NOx by 98% from 1988 levels – virtual elimination of these emissions from on-
highway engines. These emissions improvements will be achieved through both
continued refinement of engine technologies, like advanced turbocharging, as well
as new exhaust aftertreatment technologies. The new aftertreatment technologies
will be based on use of low-sulfur diesel fuel, which will enable catalytic converters,
particulate filters and other exhaust treatment technologies to work. Catalytic
converters are the technology that has been used with great success to reduce
gasoline engine emissions. Oxidation catalysts have been used successfully to
reduce PM in diesel applications, and selective catalytic reduction devices have
successfully reduced both NOx and PM. Particulate filters are in development, the
key challenge being the automatic disposal of trapped particulate as the filter
approaches its capacity. Catalysts to convert NOx into harmless nitrogen also are
in development.
PERFORMANCE ADVANTAGES OF DIESEL
The diesel's status as the world's most efficient internal combustion engine – producing more power and utilizing less fuel than other comparatively sized engines – has been recognized by widespread application throughout the world. In the United States, 94% of all freight is transported by diesel power. In Europe, where fuel prices put energy conservation at a premium, diesel powers nearly 25% of all new passenger vehicles. In France, Belgium, Austria, and Spain, over 40% of new passenger vehicles are diesel. Diesel power has also been selected for use in prototype vehicles by the U.S. Department of Energy's Partnership For a New Generation of Vehicles - a public/private partnership charged with developing radically more fuel efficient and environmentally friendly passenger vehicles.
Diesel's nearly universal use in a wide range of heavy-duty industrial applications reflects the combination of all its advantages: power, fuel efficiency, safety, durability, and suitability for very large applications. When these factors are taken into account, there is no practical substitute for diesel power in a wide range of activities, including: trucking, rail transport, public transit, inter-city bus service, marine shipping, construction, mining, agriculture, standby electric power generation, and fire and rescue vehicles.
• More Power. Diesels produce more drive force at lower engine speeds. This superior drive force is the result of the diesel engine combustion process, known as "compression ignition". Compression ignition produces superior combustion force in the cylinder, which in turn provides more power or "torque."
The compression ignition process works as follows: a diesel engine subjects air in the combustion chamber to very high compression. This compression heats the air to over 600 degrees Celsius, which is well over the ignition point of diesel fuel. Diesel fuel is then sprayed into the superheated combustion chamber where it spontaneously ignites (without the aid of a sparkplug), generating the power to move the piston. The force achieved in this process is considerably greater than that achieved in lower compression spark ignition engines (like natural gas or gasoline). Diesels thus produce more horsepower at lower engine speeds.
• Better Fuel Efficiency. Light-duty diesels, such as automobiles, use 30-60% less fuel than similarly sized gasoline engines, depending on the type of vehicle and driving conditions. Comparative studies have found on-road heavy-duty diesels to be more than 60% more fuel efficient than similarly sized spark-ignited natural gas engines (both compressed natural gas "CNG" and liquefied natural gas "LNG"). These advantages come from both the greater efficiency of
compression ignition and the higher energy content of diesel fuel.
Diesel's compression ignition process results in greater thermal efficiency – more of the fuel's energy is harnessed. This improves fuel economy. Diesel holds this advantage over any spark-ignited engine, including not only gasoline, but also CNG, LNG, and propane ("LPG"). Like gasoline engines, these other spark ignition engines are less fuel efficient because they burn fuel at lower temperatures under lower compression.
Diesel's superior fuel efficiency is not only a result of compression ignition, but also a result of diesel fuel's higher energy content. A gallon of diesel fuel contains roughly 11% more energy than a gallon of gasoline, 67% more than a gallon of LNG and 250% more than a gallon of CNG (at 3600 psi). The relatively low energy density of natural gas can be addressed in part by using larger fuel tanks, but the added weight of the tanks imposes an additional fuel economy penalty, and the tanks may also reduce the amount of useable space in the vehicle. As a result, LNG and especially CNG engines have a shorter cruising range than diesels.
• Safer. Diesel is less volatile than gasoline or natural gas – that is, the fuel does not as readily vaporize in the air. In addition, diesel fuel ignites only at a much higher temperature. For these reasons, diesel fuel is far less likely to ignite if spilled or released as a result of an accident. Diesel also is safer because it need not be handled in pressurized vessels. This is a sharp contrast to CNG, which is stored in pressurized cylinders (up to 3600 psi). High pressure greatly increases the risk of leaks during loading, unloading, and storage.
• More durable. Diesel engines are more durable than spark ignition engines.
Diesels both run more miles before needing rebuilding, and also are more easily rebuilt to original specifications. Light-duty diesel engines generally last
between 200,000 and 600,000 miles, compared to 70,000 to 200,000 miles for comparable gasoline engines. It is not uncommon for heavy-duty diesel truck engines to enjoy a life of 1,000,000 miles or more before rebuilding, nor is it uncommon for heavy-duty engines to power city buses for 15 to 20 years.
• Very large applications. The fact that diesels produce less wasted heat makes
them ideally suited for very large applications: ocean-going ships, railroad
locomotives and earth movers. One of the biggest issues in designing large
engines is the need to provide cooling systems to prevent overheating. This is a
major challenge when dealing with the heat produced in very large combustion
chambers. Because diesels waste less energy as heat, they place lesser demands
on cooling systems than spark ignition engines. This permits diesels to be scaled
up to very large sizes – diesel engines in some applications have cylinders as
large as three feet across.
EMISSIONS PROFILE OF DIESEL POWER SYSTEMS
While the performance advantages of diesel are widely known, diesels have environmental advantages that are less well understood: diesel power systems emit very little carbon monoxide, hydrocarbons, and carbon dioxide. Internal
combustion engines all emit the same basic types of emissions regardless of the type of fuel or combustion cycle used. Only the relative quantities of each emission type vary with the type of engine. The five major mobile source emissions are carbon monoxide, hydrocarbon, carbon dioxide, nitrogen oxides, and particulate matter.
Diesels produce only small proportions of the first three.
• Lower Carbon Monoxide Emissions. Diesels produce very little carbon monoxide (CO). Among all on-road mobile sources, heavy-duty diesel vehicles account for only 3% of total CO emissions. Industries whose personnel operate engines in confined spaces have traditionally used diesels because they produce so little carbon monoxide.
• Lower Hydrocarbon Emissions. Hydrocarbons (HC), a key precursor for ground level ozone (smog), are a major air pollutant from mobile sources.
Diesels, however, yield only small amounts of hydrocarbons. This results both from diesel's high combustion efficiency and from the lower evaporation rate of diesel fuel. Among on-road mobile sources, heavy-duty diesel vehicles account for only 6% of total HC emissions.
• Lower Greenhouse Gas Emissions. Today's diesel engines are low in
emissions of carbon dioxide (CO 2 ). (CO 2 is not a pollutant regulated by the EPA, but is considered a greenhouse gas.) Diesel's performance on this emission stems in part from its fuel efficiency – CO 2 emissions are closely related to overall fuel consumption. Today's on-road diesels are 30-60% more fuel efficient than their light- and heavy-duty counterparts.
While diesel performs well with respect to the emissions just described, diesel combustion inherently tends to produce significant amounts of particulate matter (PM) and nitrogen oxides (NOx). The extreme heat associated with diesel's compression combustion process tends to generate more NOx than less efficient, cooler burning engine types. The low level of oxygen in the combustion zone around individual fuel droplets prevents complete combustion of the diesel fuel which
contributes to the emission of soot (unburned carbon from the fuel) also known as particulate matter (PM).
The reduction of both PM and NOx simultaneously presents a unique emissions control challenge: some techniques used to control one of these pollutants increase the production of the other. For example, a major technique to reduce PM is to cause more complete combustion of the fuel. This reduces PM but also
produces more heat, conflicting with the goal of lowering combustion temperatures
to reduce NOx. The technical challenge of emissions reduction is to reduce both PM and NOx at the same time, without degrading the overall performance of the
system.
EMISSIONS REDUCTION THROUGH CONTINUOUS IMPROVEMENT Diesel power systems are enjoying a revolution in technology that already has achieved dramatic reductions in emissions. Technology incorporated in new on-highway engines has reduced particulate matter ("PM") emissions by 83%, and nitrogen oxides ("NOx") emissions by 63%, compared with engines produced before 1989. Technology now in development will, when it is implemented, enable further improvements so that the reductions from 1988 levels will be 98% for both PM and NOx.
Diesel emissions reductions are being achieved in stages, and
reductions have focused principally on highway engines and urban buses. Charts 1 and 2, set forth on the following page, detail current and future reductions in
emissions, and list some of the technologies that have enabled the reductions.
Chart 1
Diesel PM Emission Reductions and Enabling Technologies (Heavy-duty Highway Diesel Engines)
0.60
0.10
0.01 g/bhp/hr
1988 1998
• Computer-controlled high pressure fuel injection
• Improved combustion chamber configuration
• Turbo charging
• Low sulfur fuel
• Oxidation catalysts
• Selective Catalytic Reduction
• Particulate filters 2007
Chart 2
Diesel NOx Emission Reductions and Enabling Technologies (Heavy-duty Highway Diesel Engines)
While this review is focused on heavy-duty on-highway engine
emissions, these technologies also are being used in other applications. Light duty diesel engines for use in passenger vehicles, for example, will be required to meet the same emissions standards as gasoline powered vehicles under EPA standards that will be phased in from 2004 to 2009. Many of these same technologies will be employed in those engines.
This section describes the emissions reductions and enabling technologies in three parts: (1) the technologies found in current engines, which reflect the first wave of PM and NOx reductions in the years 1990-1994; (2) the further reduction in NOx emissions for the 2004 model year; and (3) the latest reductions in PM and NOx set for implementation in 2007-2010. 1
1 / Standards for NOx emissions from heavy-duty diesel engines were first established in 1974, but emissions control in the 1970s and 1980s was focused principally on
automobiles and other light duty gasoline vehicles. Those vehicles account for over 93% of vehicle miles traveled in the United States. The following chart lists heavy-duty diesel engine standards from 1988 through 2007:
(Footnote continued on next page)
10.70
4.00
2.50
0.20 g/bhp/hr
1988 1998 2004
• Computer-controlled high pressure fuel injection
• Improved combustion chamber configuration
• Injection timing retard
• Air-to-air charge cooling
• Low sulfur fuel
• Oxidation catalysts
• Selective Catalytic Reduction
• Exhaust gas recirculation
2007
Technologies Found in Today's Clean Diesel Engines
The emissions reductions achieved from 1990 through 1994 were massive: PM emissions of on-highway engines were reduced by 83% during that time. This was an extremely significant improvement – as a consequence of this change, the old image of a diesel truck accelerating up a hill and projecting a cloud of dirty black soot into the air is a picture of the past. While there are still such engines on the road, no engine sold in the United States since 1994, properly maintained and burning the proper fuel, will smoke in this way.
The PM reduction was accomplished by improvements designed to ensure a more complete burn of fuel within the engine. The primary enhancements include improved fuel delivery systems, improved configuration of combustion chambers, and turbocharging.
The same wave of emissions reductions produced a 63% improvement in NOx emissions of on-highway engines. These reductions also were achieved primarily through modifications in the engine. The modifications helped control combustion temperature, including offsetting the temperature increases caused by systems adopted to reduce PM emissions. NOx reductions have been achieved principally through improved fuel delivery, including electronic fuel injection and variable injection timing, and though air-to-air charge cooling, which reduces the higher temperatures created by turbocharging.
• Electronic Fuel Injection. The development of electronic fuel injection systems for diesel engines has played a central role in reducing both PM and NOx. Electronic systems calibrate fuel injection based on information from
Heavy-duty Diesel Engine Emission Standards (g/bhp-hr)
NOx PM
PM-Urban BusModel Year Standard %Change
aStandard % Change
aStandard % Change
c1988 10.7 - 0.60 0.60 -
1990 6.0 -44% 0.60 0% 0.60 0%
1991 5.0 -53% 0.25 -58% 0.25 -58%
1993 5.0 -53% 0.25 -58% 0.10 -83%
1994 5.0 -53% 0.10 -83% 0.07 -88%
1996 5.0 -53% 0.10 -83% 0.05
b-92%
1998 4.0 -63% 0.10 -83% 0.05 -92%
2004 2.0
cc-81% 0.10 -83% 0.05 -92%
2 20 00 07 7 0. 0 .2 2 - -9 98 8% % 0. 0 .0 01 1 - -9 98 8% % 0.01 -98%
a