This study investigated the effects of wind direction on trace metal concentrations in particulate matter in southeast Kansas. Air quality monitoring was conducted from March to October 2000 at nine sites. Concentrations of six metals (beryllium, chromium, arsenic, cadmium, barium, and lead) were analyzed. The results showed that wind direction significantly impacted chromium, barium, and lead concentrations, with calm/variable winds associated with higher chromium and lead levels and north winds linked to higher barium. However, upwind/downwind comparisons found no significant differences near targeted industrial sources. Mean levels of chromium, arsenic, and cadmium exceeded EPA risk levels at some sites.
Unit-IV; Professional Sales Representative (PSR).pptx
Effects of Wind Direction on Trace Metal Concentration in Southeast Kansas
1. Effects of Wind Direction on
Trace Metal Concentration
in Southeast Kansas
Sergio A. Guerra, Dennis D. Lane, Glen A. Marotz,
Ray E. Carter, Richard W. Baldauf, Carrie M. Hohl
Department of Civil, Environmental, and Architectural
Engineering, University of Kansas
2. Introduction
Southeast Kansas supports the highest concentration of
hazardous waste burners in the country
3 cement kilns
1 commercial hazardous waste incinerator
U.S. EPA sponsored the Southeast Kansas Health Study
to investigate air quality and potential health effects from
ambient air in the area
(report available at http://www2.kumc.edu/ceoh/skhs/)
This study was a joint effort between the Department of
Civil and Environmental Engineering at KU and the KU
Medical Center
3. Scope
The environmental sampling element of
the project included the determination of
trace metal concentrations from PM2.5
collected in Teflon filters in Southeast
Kansas.
Effects of spatial and temporal factors on
these concentrations were investigated
Wind direction effects are of particular
interest
4. Air Quality Monitoring
March to October, 2000
Sampling Sites in the cities of Chanute,
Coffeyville, Fredonia, and Independence
Additional Site in Labette County
Sampling Site Design, Sampling and
Analysis Protocols According to EPA
Guidelines
6. Fredonia
Site Name
Site
Code
Fredonia- Lincoln School
FLS
Fredonia- South Farm
FSF
Fredonia- South Mound
FSM
Independence- Eisenhower School
IES
Independence- Radio Tower
IRT
Independence- East of River
IER
Chanute- North Ash Grove
CNA
Chanute- South Ash Grove
CSA
Chanute- Elderly Care Center
CEC
Labette County- Big Hill Lake
LCL
10. Filters of PM2.5
samples from
each sampling
day were
selected
Filters were
digested and
analyzed by
ICP/MS for 20
metals
11. Data Analysis
Descriptive statistics were calculated for
all trace metal concentrations
Analyses of variance (anovas) were
performed on:
Possible effects of sampling site
Possible effects of sampling date
Analogous non-parametric tests also
performed to confirm anova results
12. Data Analysis
The effect of wind direction on PM
concentrations was further investigated by
performing a General Linear Model (GLM)
Data was divided in four wind direction categories (from
NCDC);
South
North
Calm/variable
Other
The effect of the targeted sources was also
analyzed by using the paired t-test and the
analogous non-parametric test
13. Integrated Risk Information System (IRIS)
Metal
Concentration (µg/m3) producing risk levels
1 in 10,000
1 in 100,000
1 in 1,000,000
Be
0.04
0.004
0.0004
Cr(VI)
0.006
0.0006
0.00006
As
0.02
0.002
0.0002
Cd
0.06
0.006
0.0006
Al, V, Fe, Co, Rb
Mn, Ni, Cu, Zn,
Se, Mo, Ag, Sb, Ba,
Tl
Pb
Not listed as hazardous air pollutants
Not assessed under IRIS program
Carcinogen Assessment Group recommends
that numerical estimate not be used
Mean Chromium
conc. was found to
exceed the 1 in
100,000 risk level
Mean and median
arsenic conc.
exceeded the 1 in
1,000,000 risk
level
Mean cadmium
conc. exceeded
the 1 in 1,000,000
14. Six metals were chosen for thorough
analysis
Beryllium
Chromium
Arsenic
Cadmium
Barium
Lead
15. Results
Anova and Kruskal-Wallis analysis shows:
Site is not a statistically significant factor for any metals
(95% confidence)
Temporal factor was found to be statistically significant
for chromium, arsenic, cadmium, barium and lead
Temporal factor was further investigated
through temperature, wind speed and
atmospheric variables
16. Sampling dates were divided into North,
South, calm/variable and other categories
GLM was run to determine the effect of
site and wind direction; site and wind
direction interaction
Wind direction was significant for chromium,
barium, and lead at 95% confidence level
Wind direction was significant for arsenic at
90% confidence level
17. Anova and Kruskal-Wallis tests were run on the
database used for the GLM
Wind direction was not statistically significant for
beryllium, arsenic and cadmium
Wind direction was statistically significant for chromium,
barium and lead
Calm/variable winds produced highest chromium
concentrations
North winds produced highest barium
concentrations
South winds and calm/variable winds produced
the highest lead concentrations
18. Upwind versus downwind samples
The effect of selected sources was tested
by applying the t-test and analogous nonparametric test
Data included upwind and downwind
samples for cities of Chanute,
Independence and Fredonia
Differences between upwind and
downwind samples were not found
statistically significant at the 95% level
19. Conclusions
Mean chromium concentration exceeded the 1
in 100,000 risk level
Though risk level is for Cr(VI)
Mean arsenic and cadmium concentrations
exceeded the 1 in 1,000,000 risk level
Sampling site was not significant for beryllium,
chromium, cadmium, arsenic, barium and lead
Sampling day was significant for all metals
except beryllium
20. Conclusions…
Calm/ variable winds produced the highest
chromium concentrations
Predominantly north winds produced the highest
barium concentrations
Predominantly south and calm/variable winds
produced the highest lead concentrations
No statistically significant differences were found
between samples upwind and downwind from
targeted sources