ASHRAE OR-05-15-1-2005 Field Evaluation of Ventilation and Control of Diesel Exhaust in Enclosed Locomotive Facilities《在密封的机车设施RP-1191里的 通风及柴油车尾气控制实地评估》.pdf
《ASHRAE OR-05-15-1-2005 Field Evaluation of Ventilation and Control of Diesel Exhaust in Enclosed Locomotive Facilities《在密封的机车设施RP-1191里的 通风及柴油车尾气控制实地评估》.pdf》由会员分享,可在线阅读,更多相关《ASHRAE OR-05-15-1-2005 Field Evaluation of Ventilation and Control of Diesel Exhaust in Enclosed Locomotive Facilities《在密封的机车设施RP-1191里的 通风及柴油车尾气控制实地评估》.pdf(11页珍藏版)》请在麦多课文档分享上搜索。
1、OR-05-15-1 (RP-1191) Field Evaluation of Ventilation and Control of Diesel Exhaust in Enclosed Locomotive Amy Musser, PhD, PE Associate Member ASHRAE ABSTRACT This paper summarizes the results ofjeld measurements that were conducted in four operating diesel locomotive shops. Thephysicalgeometry and
2、ventilation system design are docu- mented for each shop, and their usage is described. Measure- ments taken over a four-day period at each location are discussed, and typical data are presented. When possible, average contaminant concentrations for similar operating events are also analyzed togethe
3、r to provide a more complete assessment of ventilation system operation. Finally, qualita- tive observations gathered during thejeld study that may be useful to designers are discussed. These include insights on locomotive position within the shop, control issues, and the importance of temperature i
4、n certain types of design. INTRODUCTION Currently available design guidance for ventilation of enclosed locomotive facilities has been developed based on practical experience. However, little research exists to validate or invalidate the effectiveness of these ventilation quantities for removal of d
5、iesel exhaust. Furthermore, there is little inde- pendent published information that surveys current practice and reports routine operating experiences. This work describes field measurements that were conducted in four shops located in the United States under normal operating conditions. There were
6、 several goals of this study. First, the design of each ventilation system was docu- mented and described. Second, contaminant measurements were collected to compare and evaluate the various systems and also to provide validation data that can be used to develop a computational model. Also, addition
7、al information was collected while visiting the shops that may be useful to design- Faci I it es Matthew Radik Student Member ASHRAE ers in planning future systems. The final goal of this effort, combined with future CFD modeling, is to develop handbook appropriate material to guide the design proce
8、ss for these facilities. Several sources provide design and operations guidance relevant to ventilation of railroad facilities. The ventilation rate procedure of ASHRAE Standard 62-2001, Gntilation for Acceptable Indoor Air Quality, specifies 1.5 cfinlft2 (7.5 LIS per m2) to maintain acceptable indo
9、or air qualiy in auto repair rooms, which is the closest listed occupancy (ASHRAE 2001). However, locomotive facilities tend to have high ceil- ings and larger volumes, so the 1999 ASHME ffandbook- Applications recommends that a volumetric model instead be used to calculate the design ventilation (A
10、SHRAE 1999). Both the ASHRAE Handbook-Applications and the Ameri- can Railway Engineering and Maintenance-of-Way Associa- tion (AREMA) Manual for Railway Engineering suggest 6 air changes per hour when dilution ventilation is used (AREMA 2001). These values provide a benchmark for comparing the syst
11、ems analyzed here. FIELD MEASUREMENTS Test Protocols The test protocol implemented at the shops included oper- ations monitoring, contaminant, and temperature arrays inside the shop, ventilation assessment, and weather monitoring. Because the purpose of the measurements was to characterize the respo
12、nse of the ventilation system to locomotive operation, contaminant and temperature arrays in each shop were set up near tracks that experienced the most locomotive movement. In some cases, it was possible to leave the arrays in one loca- tion for several hours each day. In shops that experienced les
13、s Amy Musser is a partner at Vandemusser Design, LLC, Asheville, NC. Matthew Radik is a student at the University of Nebraska, Omaha, Neb. O2005 ASHRAE. 1015 traffic, it was necessary to move the arrays based on the planned daily schedule. During the times when instruments were installed, all locomo
14、tive movement and operation were recorded. This was done not just for the track adjacent to the instrument array, but for all tracks in the shop. Vertical contaminant and temperature arrays were set up inside the shop to obtain profiles that could be used for vali- dation of a computational model. I
15、n most cases the array consisted of three sets of sensors that were either hung from the ceiling structure or mounted on a telescoping pole. These sensors were capable of collecting time series data for up to eight hours at a time. In all of the shops, electrochemical sensors capable of measuring ca
16、rbon monoxide, nitric oxide, and nitrogen diox- ide were installed. Manufacturer information for the carbon monoxide sensor states a range of 0-500 ppm, a resolution of 1 ppm, a cross-reactivity without filtering of 3 ppm to 35 ppmNO, and-1 ppm to 5 ppmN0,. The nitric oxide sensor has a range of 0-2
17、50 ppm, a resolution of 1 ppm, no cross-reac- tivity to 300 ppm CO, and 1.5 ppm cross-reactivity to 5 ppm NO,. The nitrogen dioxide sensor has a range of 0-30 ppm, a resolution of O. 1 ppm, a cross-reactivity of 15 ppm to 300 ppm CO, and no cross reactivity to 35 ppm NO. The temperature sensors have
18、 a range of 4OF to 158F (-20C to 70C). They have a resolution of O.8“F at 68F (0.4“C at 20C) and about 1.2“F at 140F (0.7“C at 60C). At one of the sites, carbon dioxide sensors were also installed. These sensors have a range of 0-4000 ppm when used with a data logger and a resolution of 50 ppm. They
19、 were not deployed at the other sites because the recorded variation in CO, that accompanied locomotive operation was not much larger than the normal fluctuations observed throughout the day. Therefore, they were not useful as an indicator of loco- motive operation. Mechanical flow rates were verifi
20、ed in a number of ways, depending primarily on equipment accessibility. Manufac- turer ratings were taken fi-om drawings and nameplate infor- mation. When possible, flow rates were verified by pitot tube duct traverse or traverse-type measurements at air outlets. Although the latter method is not a
21、particularly accurate Site la lb 2 method of determining airflow (order *20%), it does provide a means of verifiing the rated equipment flow rates. Outdoor wind speed, temperature, and relative humidity were recorded using a weather station mounted on the roof of each shop. Due to some lapses in our
22、 data recording device, hourly average weather data recorded at nearby airports were also obtained from a weather service and used when needed to supplement the collected data. These data were primarily collected to assist in developing computational models of the facilities. Shop Area Ceiling Heigh
23、t Exhaust Airflow Air Change Location (ftY Volume (ft?) Ventilation System Rate (cfm) Rate (hr-) Chicago 12,800 42 537,600 General exhaust 60,000 6.7 Chicago 12,800 42 537,600 General exhaust 72,000 - 102,000 8 - 1 1.3 New Orleans 21,600 19.5 and 34.5 543,000 Gcncral exhaust 5 19,000 57 Test Schedul
24、e The four sites studied were locomotive repair shops located throughout the United States. Pilot tests were conducted at site 1 for two days in December 200 1. A second visit of three days duration was then made to this location in March 2002. Because of a calibration problem that was later discove
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