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We thank the Office of Research and Sponsored Programs for supporting this research, and Learning & Technology Services for printing this poster.
Effects of Wind and Precipitation on Airborne
Particulate Levels Around a Frac Sand Mine
Hannah Smith| BSB , Pang Houa Xiong- Yang | BSENPH
UNIVERSITY OF WISCONSIN- EAU CLAIRE: SAND FRACKING RESEARCH
BACKGROUND METHODS
OBJECTIVE
 Frac sand mining and processing generate particulate
matter including respirable crystalline silica.
 Different sources of pollution causes human health
concerns associated with frac sand mining in Wisconsin
 Many cardiovascular and respiratory symptoms are
associated with the inhalation of particulate matter:
 PM2.5 and PM10 levels, wind speed, wind direction and
precipitation were measured at the Chippewa Sand
mine in Bloomer, WI.
 Chippewa Sands mine is located Northwest of our
equipment
 Theoretically, wind direction will need to come from NW
to SE to hit our equipment
 Determine correlation between met data and PM2.5
levels found.
Fig. 1: Frac sand mine in Wisconsin (fracctracker.org)
● Collect data from meteorological station at the Bloomer
site
● Use software “Weather link” to download data from field
unit to computer
● Analyze data to determine correlation of the met data
and other direct reading instruments
 Compared direct reading equipment levels to met
data
 Compared high PM2.5 level days to:
 Wind direction
 Rain rate
RESULTS
 Measurements have found higher levels of PM2.5 around
plants, compared to regional levels
 Wind speed and direction don’t play a role in the
movement of particulates
 Precipitation seems to lower PM2.5
 Monitoring for PM2.5 and silica is essential
 These particles are known to cause health impact in the
long term
ACKNOWLEDGEMENTS
REFERENCES
 Dr. Crispin Pierce- Environmental Public Health
Associate Professor
 Office of Research and Sponsored Programs
 Pierce, Crispin. “Air Quality Around Frac Sand Facilities”
19 March 2016. PowerPoint Presentation
 Wisconsin Department of Natural Resources
CONCLUSION
 Precipitation inversely correlates with PM2.5 levels.
 Compared lower levels of PM2.5 to Wind directions
and precipitation
 Wind Directions and speeds don’t correlate with PM2.5
levels.
RESULTS
N
5%
NW
2%
SSW
27%
SW
61%
wnw
5%
7/23/16 Wind direction
N
NW
SSW
SW
wnw
E
3%
ESE
36%
SE
35%
SSE
26%
6/05/15 Wind direction
E
ESE
SE
SSE
W
81%
WNW
13%
WSW
6%
7/29/16 WIND Direction
W WNW WSW
ENE
2% N
21%
NW
57%
W
2%
WNW
18%
8/04/16 Wind Direction
ENE N NNW NW W WNW
 The rain rate is zero for all 4 days
 Lower levels correlates with rain rates
2%
24%
2%
14%
17%
41%
7/17/16 Wind Direction
E
NNW
NW
S
SW
W
WNW
NNW
11% NW
2%
S
2% SE
4%
SSE
11%
SSW
4%
SW
30%
W
8%
WNW
15%
WSW
13%
8/16/16 Wind direction
NNW NW S SE SSE SSW SW W WNW WSW
2%
13%
2%
25%
33%
8%
17%
8/28/16 Wind Direction
E
ESE
S
SE
SSE
SSW
SW
52%
21%
17%
6%
4%
9/03/16 Wind Direction
E ENE ESE NE SSE
Fig. 2: Location of Chippewa Sands company and Our instrument location (google earth)

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frac poster3

  • 1. We thank the Office of Research and Sponsored Programs for supporting this research, and Learning & Technology Services for printing this poster. Effects of Wind and Precipitation on Airborne Particulate Levels Around a Frac Sand Mine Hannah Smith| BSB , Pang Houa Xiong- Yang | BSENPH UNIVERSITY OF WISCONSIN- EAU CLAIRE: SAND FRACKING RESEARCH BACKGROUND METHODS OBJECTIVE  Frac sand mining and processing generate particulate matter including respirable crystalline silica.  Different sources of pollution causes human health concerns associated with frac sand mining in Wisconsin  Many cardiovascular and respiratory symptoms are associated with the inhalation of particulate matter:  PM2.5 and PM10 levels, wind speed, wind direction and precipitation were measured at the Chippewa Sand mine in Bloomer, WI.  Chippewa Sands mine is located Northwest of our equipment  Theoretically, wind direction will need to come from NW to SE to hit our equipment  Determine correlation between met data and PM2.5 levels found. Fig. 1: Frac sand mine in Wisconsin (fracctracker.org) ● Collect data from meteorological station at the Bloomer site ● Use software “Weather link” to download data from field unit to computer ● Analyze data to determine correlation of the met data and other direct reading instruments  Compared direct reading equipment levels to met data  Compared high PM2.5 level days to:  Wind direction  Rain rate RESULTS  Measurements have found higher levels of PM2.5 around plants, compared to regional levels  Wind speed and direction don’t play a role in the movement of particulates  Precipitation seems to lower PM2.5  Monitoring for PM2.5 and silica is essential  These particles are known to cause health impact in the long term ACKNOWLEDGEMENTS REFERENCES  Dr. Crispin Pierce- Environmental Public Health Associate Professor  Office of Research and Sponsored Programs  Pierce, Crispin. “Air Quality Around Frac Sand Facilities” 19 March 2016. PowerPoint Presentation  Wisconsin Department of Natural Resources CONCLUSION  Precipitation inversely correlates with PM2.5 levels.  Compared lower levels of PM2.5 to Wind directions and precipitation  Wind Directions and speeds don’t correlate with PM2.5 levels. RESULTS N 5% NW 2% SSW 27% SW 61% wnw 5% 7/23/16 Wind direction N NW SSW SW wnw E 3% ESE 36% SE 35% SSE 26% 6/05/15 Wind direction E ESE SE SSE W 81% WNW 13% WSW 6% 7/29/16 WIND Direction W WNW WSW ENE 2% N 21% NW 57% W 2% WNW 18% 8/04/16 Wind Direction ENE N NNW NW W WNW  The rain rate is zero for all 4 days  Lower levels correlates with rain rates 2% 24% 2% 14% 17% 41% 7/17/16 Wind Direction E NNW NW S SW W WNW NNW 11% NW 2% S 2% SE 4% SSE 11% SSW 4% SW 30% W 8% WNW 15% WSW 13% 8/16/16 Wind direction NNW NW S SE SSE SSW SW W WNW WSW 2% 13% 2% 25% 33% 8% 17% 8/28/16 Wind Direction E ESE S SE SSE SSW SW 52% 21% 17% 6% 4% 9/03/16 Wind Direction E ENE ESE NE SSE Fig. 2: Location of Chippewa Sands company and Our instrument location (google earth)