Heitbrink William A, Collingwood Scott
Department of Occupational and Environmental Health, The College of Public Health, The University of Iowa, Iowa City, Iowa 52241, USA.
J Occup Environ Hyg. 2005 Jan;2(1):45-53. doi: 10.1080/15459620590903020.
In cabin filtration systems, blower motors pressurize a vehicle cabin with clean filtered air and recirculate air through an air-conditioning evaporator coil and a heater core. The exposure reduction offered by these cabins is evaluated by optical particle counters that measure size-dependent aerosol concentration inside and outside the cabin. The ratio of the inside-to-outside concentration is termed penetration. Blower motors use stationary carbon brushes to transmit an electrical current through a rotating armature that abrades the carbon brushes. This creates airborne dust that may affect experimental evaluations of aerosol penetration. To evaluate the magnitude of these dust emissions, blower motors were placed in a test chamber and operated at 12 and 13.5 volts DC. A vacuum cleaner drew 76 m3/hour (45 cfm) of air through HEPA filters, the test chamber, and through a 5 cm diameter pipe. An optical particle counter drew air through an isokinetic sampling probe and measured the size-dependent particle concentrations from 0.3 to 15 microm. The concentration of blower motor aerosol was between 2 x 10(5) and 1.8 x 10(6) particles/m3. Aerosol penetration into three stationary vehicles, two pesticide application vehicles and one tractor were measured at two conditions: low concentration (outside in the winter) and high concentration (inside repair shops and burning incense sticks used as a supplemental aerosol source). For particles smaller than 1 microm, the in-cabin concentrations can be explained by the blower motor emissions. For particles larger than 1 microm, other aerosol sources, such as resuspended dirt, are present. Aerosol generated by the operation of the blower motor and by other sources can bias the exposure reduction measured by optical particle counters.
在车厢过滤系统中,鼓风机电机用清洁的过滤空气对车辆车厢增压,并使空气通过空调蒸发器盘管和加热器芯进行再循环。这些车厢所提供的暴露减少效果通过光学粒子计数器来评估,该计数器测量车厢内外与尺寸相关的气溶胶浓度。车厢内与车厢外浓度的比值称为穿透率。鼓风机电机使用固定碳刷将电流传输通过旋转电枢,而旋转电枢会磨损碳刷。这会产生空气传播的灰尘,可能会影响气溶胶穿透率的实验评估。为了评估这些灰尘排放的程度,将鼓风机电机置于测试室内,并在12伏和13.5伏直流电压下运行。一台真空吸尘器以76立方米/小时(45立方英尺/分钟)的流量通过高效空气过滤器、测试室以及一根直径5厘米的管道抽取空气。一台光学粒子计数器通过等速采样探头抽取空气,并测量0.3至15微米范围内与尺寸相关的粒子浓度。鼓风机电机产生的气溶胶浓度在2×10⁵至1.8×10⁶颗粒/立方米之间。在两种条件下测量了气溶胶进入三辆静止车辆、两辆农药喷洒车和一台拖拉机的情况:低浓度(冬季室外)和高浓度(室内维修店以及使用香作为补充气溶胶源的地方)。对于小于1微米的颗粒,车厢内的浓度可以用鼓风机电机的排放来解释。对于大于1微米的颗粒,则存在其他气溶胶源,如再悬浮的灰尘。鼓风机电机运行以及其他来源产生的气溶胶可能会使光学粒子计数器测量的暴露减少产生偏差。