ASHRAE 4731-2004 Overview of Exisiting Guidance and Ventilation Approaches for Control of Diesel Exhaust Inside Locomotive Facilities《为控制柴油车尾气内机车设施RP-1191的现有的指导和通风的办法概述》.pdf

《ASHRAE 4731-2004 Overview of Exisiting Guidance and Ventilation Approaches for Control of Diesel Exhaust Inside Locomotive Facilities《为控制柴油车尾气内机车设施RP-1191的现有的指导和通风的办法概述》.pdf》由会员分享，可在线阅读，更多相关《ASHRAE 4731-2004 Overview of Exisiting Guidance and Ventilation Approaches for Control of Diesel Exhaust Inside Locomotive Facilities《为控制柴油车尾气内机车设施RP-1191的现有的指导和通风的办法概述》.pdf（11页珍藏版）》请在麦多课文档分享上搜索。

1、4731 (RP-1191) Overview of Existing Guidance and Ventilation Approaches for Control of Diesel Exhaust Inside Locomotive Facilities Chadwick C. Rasmussen Kimberly Bunz Student Member ASHRAE ABSTRACT This paper provides an overview of existing guidance, regulations, and design approaches to control di

2、esel exhaust from locomotives operating in buildings. First, design guid- ance andstandards for exposure to major components of diesel exhaust are reviewed. Next, issues regarding engine design, fuel composition, andoutdoor emissions controlstrategies and their potential impact on current and future

3、 indoor emissions are discussed. Ventilation approaches that have been imple- mented in existing facilities are also presented. The review highlights both approaches and information that will be useful to designers planning or retrofitting this type of facility. INTRODUCTION The design of ventilatio

4、n systems for buildings in which locomotives operate requires consideration of contaminant sources that are not easily defined and contaminant targets that are continuously updated. Design approaches have been developed, but no studies targeted specifically to ventilation systems have been performed

5、 to measure their success or to provide research-based guidelines for their implementation. The purpose of this review was to investigate the technical literature and talk with practitioners to identi9 current issues, problems, and approaches to ventilating these types of build- ings. The flow and h

6、eat removal conditions for tunnels present different challenges and are not addressed by this review. First, the review seeks to define the design problem by identifying contaminants for which exposure limits are recommended and those that may be monitored in the near future. Next, the vast amount o

7、f published information on engine performance and emissions is reviewed to identi9 data relevant to the indoor design problem. Possible future developments in fuel charac- Amy Musser, Ph.D., P.E. Associate Member ASHRAE Matthew Radik Student Member ASHRAE teristics and engine design are also identif

8、ied and discussed in the context of impact on low load, cold start, and indoor oper- ation. Finally, some design approaches are discussed, with information on what is effective and areas in which new tech- nology may be helpful. DESIGN CRITERIA Current Design Guidance Several sources provide design

9、and operations guidance relevant to ventilation of railroad facilities. The ventilation rate procedure of ASHRAE Standard 62-1999, Ventilation for Acceptable Indoor Air Quality, specifies 1.5 cfm/ft2 (7.5 I/s per m2) to maintain acceptable indoor air quality in auto repair rooms, which is the closes

10、t listed occupancy (ASHRAE 1999a). This limit is based in large part on carbon monoxide present in auto repair facilities, not the different mix of contaminants present in diesel locomotive facilities. Also, locomotive facilities tend to have high ceilings and larger volumes, so the 2003 ASHRAE Hand

11、book-Applications recommends that a volumetric model instead be used to calcu- late the design ventilation rate (ASHRAE 2003). Both the 2003 ASHRAE Handbook-Applications and the American Railway Engineering and Maintenance-of-Way Associations (AREMA) Manual for Railway Engineering currently suggest

12、6 air changes per hour when dilution ventilation is used (AREMA 2001). The authors know of no cases in which this guideline has failed to produce compliance with the current contaminant limits, although tightening of these limits may require this guideline to be revisited in the future. The American

13、 Conference of Governmental and Indus- trial Hygienists suggests a source-based method of sizing Chad Rasmussen is a Ph.D. candidate in aerospace engineering at the University of Michigan, Ann Arbor, Mich. Amy Musser is an assistant professor, Kim Bunz is a candidate for an MAE, and Matt Radik is an

14、 undergraduate student in the Department of Architecturai Engineering, University of Nebraska, Lincoln, Neb. I , , I l l I l 389 02004 ASHRAE. ventilation systems for facilities where diesel engines are in operation, They recommend 100 cfin (47 11s) per operating horsepower of the engine (NJDHSS 199

15、4). A locomotive engine idling with no head end power (HEP) operates at less than 1 O0 hp (75 kW) and the ventilation system would be sized for 10,000 cfm (4720 Us) based on this guideline. However, the ventilation system designer must also check this against the requirements for heat removal when s

16、izing a system. Most design references also suggest the use of localized exhaust to reduce energy use. Entiy OSHA - USA (PEL) Standards for Exposure The Occupational Safety and Health Administration (OSHA 2001a) sets legally enforceable exposure limits for workplace contaminants in the U.S. Most sta

17、tes follow these federal limits, but a few states may set more restrictive require- ments. The OSHA standards specify maximum contaminant concentrations called permissible exposure limits (PEL) that are allowed in the workplace. When determining its standards, OSHA takes into consideration the table

18、 of threshold limit values (TLV) for chemical substances and physical agents published by the American Conference of Governmental Industrial Hygienists (ACGIH). The TLVs provided by the ACGIH are recommendations or guideline values for use in industrial hygiene and are not legally enforceable. Also

19、in the U.S., the National Institute for Occupational Safety and NO2 (PP NO (PPN CO (PPm) so, (PPm 8h 15min ceil 8 h 15min 8 h 15min ceil 8h 15min 5 25 50 5 Health is the federal agency responsible for conducting research on potential workplace hazards and publishes recom- mended exposure levels (EL)

20、 based on this research. Finally, the Mine Safety and Health Administration (MSHA) also publishes legally enforceable limits that apply only to workers in the mining industry. A PEL can be given as a time-weighted average (TWA), short-term exposure limit (STEL), or a ceiling value. The TWA is a time

21、-weighted average of the varying concentrations of a contaminant in an eight-hour workday, which cannot be exceeded during the work shift. The STEL value is usually a 15-minute time-weighted average, and a ceiling value is a maximum limit that cannot be exceeded at any time (Lewis 1996). OSHA does n

22、ot currently regulate diesel exhaust specif- ically, although many substances found in diesel exhaust are regulated. OSHA (OSHA 2001b) identifies carbon dioxide (CO,), carbon monoxide (CO), nitrogen dioxide (NO,), nitric oxide (NO), diesel particulate matter (DPM), and sulfur diox- ide (SO,) as majo

23、r components of diesel exhaust. Thiry-one additional substances are identified as minor components, with seventeen. of these being polycyclic aromatic hydrocar- bons (PAH). These minor components are elements of DPM. Countries outside the U.S. legislate their own contami- nant limits, though these m

24、ay draw heavily from the ACGIH and other U.S. publications. Table 1 compares various Table 1. Contaminant Exposure Limits for Major Diesel Exhaust Components I l I I l l ASHRAE Transactions: Research 390 published exposure limits in parts per million (ppm). OSHA requirements shown are the federal li

25、mits, and a few states may set more restrictive requirements. All OSHA, ACGIH, and NIOSH limits are current as of February 2003 or newer. Other limits are taken primarily from an international database of participating countries (IL0 2003; Lu 1993). Currently, for most jurisdictions, nitrogen dioxid

26、e (NO,) is present in exhaust emissions at the highest levels relative to its published limits. This makes it the “critical contaminant” for design. If it is assumed that all exhaust contaminants are diluted or removed in the same way, the critical contaminant has the highest emissions per required

27、limit. In this case, nitro- gen dioxide has a much higher emissions to limit ratio, and ventilation systems designed to control nitrogen dioxide will maintain other contaminants well below their respective limits. However, the reader should be aware that as more becomes known about other compounds-p

28、articularly diesel particulate matter (discussed below)-the limits for these compounds may become more critical. OSHA does not currently distinguish DPM from other particulates. The PEL for particulates not otherwise regulated (free of asbestos and less than 1% silica) is 15 mg/m3 TWA. The ACGIH has

29、 targeted DPM in its Notice of Intended Changes since 1995. In the 2001 notice, a limit of 0.02 mg/m3 for DPM measured as elemental carbon was proposed (ACGIH 2001). It has been shown that DPM levels can be accurately determined by measuring elemental carbon in rail- road environments (Liukonen 2002

30、). A recent ACGIH press release confirms the addition of diesel exhaust to the 2003 published TLVs, which will be released later in 2003 (ACGIH 2003). The increasing emphasis on diesel particulate is evident in new laws enacted by MSHA in January 2001 to protect mine workers from diesel particulates

31、. These rules will establish an interim maximum eight-hour “full shift” DPM concentration limit of 0.4 mg/m3 for metal and non-metal mines, which is required by law as of July 2002. This limit will be reduced to O. 16 mg/m3 over the following five years. The intent of these rules will be applied to

32、coal mines by requiring reduced emis- sions from diesel equipment, since the presence of coal partic- ulate interferes with the measurement protocol for diesel particulate (MSHA 2001). Outside the U.S., the German “Chemicals Act” specifies maximum concentrations for no adverse effect on worker healt

33、h (MAK) or concentrations achievable using technically available measures (TRK). These regulations currently limit elemental carbon to O. 1 mg/m3 in diesel environments and 0.3 mg/rn3 in non-coal mines and tunneling (DieselNet 2001). POLLUTANT SOURCE ISSUES Indoor emissions are influenced by many fa

34、ctors, includ- ing engine design, operation, and fuel quality. Therefore, an understanding of these effects is a necessary context for apply- ing published emissions data and to begin to anticipate future trends and changes. It may also be helpful in addressing emis- sions issues specific to a parti

35、cular facility. Diesel Exhaust Characterization Pollutants that have been specifically targeted by diesel emissions research include oxides of nitrogen (NO,), sulfur dioxide, DPM, carbon monoxide, and unburned hydrocar- bons. A detailed knowledge of combustion processes is needed to quantify the gen

36、eration of each contaminant in a diesel engine. Designers cannot be expected to become experts in the subject of engine design, but some identified relationships between fuel composition, environment, and operating conditions provide some insight into the nature of emissions generation and trends th

37、at impact the indoor envi- ronment. DPM emissions are primarily a result of the inability of some fuel to adequately interact with oxygen. This is most likely a result of a locally rich fuel-air mixture (Barry et al. 1985). Increasing the combustion temperature has been shown to reduce the amount of

38、 particulate emissions, and engine design parameters such as swirl can also affect their formation. The particles themselves contain cores of elemental carbon or unburned fuel that accrue other substances such as hydrocar- bons, sulfates, PAHs, nitro-PAHs, nitroarenes, and metals on the outer surfac

39、e (MECA 2001). Diesel particulate matter emissions are “reasonably anticipated to be a human carcino- gen” by the US. Department of Health and Human Services (U.S. DHHS 2001). The health effects of the major gaseous pollutants, such as nitrogen dioxide and carbon monoxide, are relatively well unders

40、tood. However, the health risks associated with many compounds found in DPM are less clear. Ongoing research is adding to our understanding of the components of DPM and their potential health effects. Therefore, future DPM regula- tions are likely and may continue to develop to reflect ongoing and f

41、uture research that better quantifies the health effects of the many substances found in DPM. Design guidance should be flexible enough to respond to tightening restrictions in a timely manner. Ventilation systems that are easily adapted, updated, or retrofitted may be of value to owners as well. Su

42、lfur has been targeted by emissions standards because of its role in DPM formation and associated adverse health effects. Inhalation of SO, contributes to respiratory side effects such as lung and throat irritation and shortness of breath (ATSDR 2001). Sulfur dioxide is prone to oxidize during combu

43、stion to form sulfates. These sulfates are emitted as DPM (U.S. DOE 1999), and increased amounts of sulfur in diesel fuel have been shown to correlate to increased DPM emissions (Barry et al. 1985; US. DOE 1999). Diesel combustion processes readily form oxides of nitro- gen because of the lean condi

44、tions under which combustion typically occurs. As a result, excess oxygen is present in the cylinder and may react with nitrogen in the air to form NO,. Increasing temperature will result in formation of larger amounts of NO, (Chevron 1998). Nitrogen dioxide exposure can cause negative health effect

45、s such as shortness of breath, as well as eye, nose, and throat irritation (US. EPA 2001). ASHRAE Transactions: Research 391 Diesel Fuel Composition Diesel fuel is derived from crude oil and is thicker and heavier than traditional gasoline. Useful products such as diesel fuel and kerosene are extrac

46、ted from crude oil through a process called distillation, which separates the components based on their respective boiling points (Chevron 1998; Bonnan and Ragland 1998). Different batches of crude oil vary in composition and, as a result, the properties of diesel fuels can vary significantly betwee

47、n batches. Both this varia- tion and the likelihood of future advancements in fuel qualiy should be anticipated in efforts to relate fuel composition to emissions. Cetane, or n-hexadecane (CI6H3 however, cetane numbers may range as high as 55 (U.S. DOE 2000). The most commonly used diesel fuel is No

48、. 2-D since it has a slightly higher energy content than No. 1-D. No. 1-D is often recommended for colder climates because it has a higher cetane level and flow properties better suited for cold environments. Locomotives generally run on No. 2-D with No. 1-D used only in extremely cold conditions. I

49、t is becoming more common for additives to be used with No. 2-D to improve operation in cold climates rather than using No. 1 -D at all. Other Considerations and Future Trends Altitude can play a large part in emissions composition since combustion at higher altitudes is less efficient. There- fore, higher concentrations of unburned hydrocarbons, carbon monoxide, and particulate matter should be expected. Design of facilities at high altitudes should account for slightly higher emissions concentrations. The EPA publishes altitude emis- sion adjustment factors for heavy-duty diesel engines