Jc. Chow et al., Cross-border transport and spatial variability of suspended particles in Mexicali and California's Imperial Valley, ATMOS ENVIR, 34(11), 2000, pp. 1833-1843
The city of Mexicali, the state capitol of Baja California, Mexico, lies 18
9 kilometers (km) inland from the Pacific Coast on the California border at
the lower end of California's Imperial Valley. Mexicali is adjacent to the
California city of Calexico and 20 km south of the Imperial county seat of
El Centro. The Mexicali and Calexico PM10 monitors were separated by only
10 km; yet, three measurements at Calexico exceeded 150 mu g m(-3), while 2
3 samples exceeded this PM10 standard at the Mexicali site. Air how through
Mexicali is channeled by the Imperial Valley and is usually from the north
west or southeast, with northwesterlies being most frequent. During the stu
dy period from March 1992 through August 1993, hourly PM10 concentrations w
ere higher in the border area during southerly than northerly flow. For win
d flow patterns in both directions, PM10 initially decreased with wind spee
d due to improved ventilation, then increased at high wind speeds due to in
creased suspension of soil particles. Average cross-border transport of PM1
0 was three times higher for southerly flow from Mexico than for northerly
flow from the United States into Mexico. Because northerly winds were more
frequent, the time-integrated cross-border transport over the study period
was only about one-and-one-half times higher from Mexico. PM10 mass concent
rations at the Mexicali site were highest when flow was over the main Calex
ico-Mexicali urban area (northwesterly flow) but were lower when flow was f
rom less urbanized desert areas (southeasterly flow). Although Mexicali's P
M10 concentrations were almost double those measured at Calexico, annual av
erage relative source contributions were similar, with 70% from fugitive du
st, 10-15% from motor vehicle exhaust, 4-8% from vegetative burning or cook
ing, 2-3% from marine aerosol (Gulf of California), 1.5-3% from secondary a
mmonium sulfate, and 1.5% to 2.5% from secondary ammonium nitrate. Primary
industrial source contributions were negligible. (C) 2000 Published by Else
vier Science Ltd. All rights reserved.