8 research outputs found
Quantifying O<sub>3</sub> Impacts in Urban Areas Due to Wildfires Using a Generalized Additive Model
Wildfires
emit O<sub>3</sub> precursors but there are large variations
in emissions, plume heights, and photochemical processing. These factors
make it challenging to model O<sub>3</sub> production from wildfires
using Eulerian models. Here we describe a statistical approach to
characterize the maximum daily 8-h average O<sub>3</sub> (MDA8) for
8 cities in the U.S. for typical, nonfire, conditions. The statistical
model represents between 35% and 81% of the variance in MDA8 for each
city. We then examine the residual from the model under conditions
with elevated particulate matter (PM) and satellite observed smoke
(“smoke days”). For these days, the residuals are elevated
by an average of 3–8 ppb (MDA8) compared to nonsmoke days.
We found that while smoke days are only 4.1% of all days (May–Sept)
they are 19% of days with an MDA8 greater than 75 ppb. We also show
that a published method that does not account for transport patterns
gives rise to large overestimates in the amount of O<sub>3</sub> from
fires, particularly for coastal cities. Finally, we apply this method
to a case study from August 2015, and show that the method gives results
that are directly applicable to the EPA guidance on excluding data
due to an uncontrollable source
Interannual Variability in Baseline Ozone and Its Relationship to Surface Ozone in the Western U.S.
Baseline
ozone refers to observed concentrations of tropospheric
ozone at sites that have a negligible influence from local emissions.
The Mount Bachelor Observatory (MBO) was established in 2004 to examine
baseline air masses as they arrive to North America from the west.
In May 2012, we observed an O<sub>3</sub> increase of 2.0–8.5
ppbv in monthly average maximum daily 8-hour average O<sub>3</sub> mixing ratio (MDA8 O<sub>3</sub>) at MBO and numerous other sites
in the western U.S. compared to previous years. This shift in the
O<sub>3</sub> distribution had an impact on the number of exceedance
days. We also observed a good correlation between daily MDA8 variations
at MBO and at downwind sites. This suggests that under specific meteorological
conditions, synoptic variation in O<sub>3</sub> at MBO can be observed
at other surface sites in the western U.S. At MBO, the elevated O<sub>3</sub> concentrations in May 2012 are associated with low CO values
and low water vapor values, consistent with transport from the upper
troposphere/lower stratosphere (UT/LS). Furthermore, the Real-time
Air Quality Modeling System (RAQMS) analyses indicate that a large
flux of O<sub>3</sub> from the UT/LS in May 2012 contributed to the
observed enhanced O<sub>3</sub> across the western U.S. Our results
suggest that a network of mountaintop observations, LiDAR and satellite
observations of O<sub>3</sub> could provide key data on daily and
interannual variations in baseline O<sub>3</sub>
Global Atmospheric Transport and Source-Receptor Relationships for Arsenic
Arsenic and many of its compounds
are toxic pollutants in the global
environment. They can be transported long distances in the atmosphere
before depositing to the surface, but the global source-receptor relationships
between various regions have not yet been assessed. We develop the
first global model for atmospheric arsenic to better understand and
quantify its intercontinental transport. Our model reproduces the
observed arsenic concentrations in surface air over various sites
around the world. Arsenic emissions from Asia and South America are
found to be the dominant sources for atmospheric arsenic in the Northern
and Southern Hemispheres, respectively. Asian emissions are found
to contribute 39% and 38% of the total arsenic deposition over the
Arctic and Northern America, respectively. Another 14% of the arsenic
deposition to the Arctic region is attributed to European emissions.
Our results indicate that the reduction of anthropogenic arsenic emissions
in Asia and South America can significantly reduce arsenic pollution
not only locally but also globally
Fast Time Resolution Oxidized Mercury Measurements during the Reno Atmospheric Mercury Intercomparison Experiment (RAMIX)
The
Reno Atmospheric Mercury Intercomparison Experiment (RAMIX)
was carried out from 22 August to 16 September, 2011 in Reno, NV to
evaluate the performance of new and existing methods to measure atmospheric
mercury (Hg). Measurements were made using a common sampling manifold
to which controlled concentrations of Hg species, including gaseous
elemental mercury (GEM) and HgBr<sub>2</sub> (a surrogate gaseous
oxidized mercury (GOM) compound), and potential interferents were
added. We present an analysis of Hg measurements made using the University
of Washington’s Detector for Oxidized Hg Species (DOHGS), focusing
on tests of GEM and HgBr<sub>2</sub> spike recovery, the potential
for interference from ozone (O<sub>3</sub>) and water vapor (WV),
and temporal variability of ambient reactive mercury (RM). The mean
GEM and HgBr<sub>2</sub> spike recoveries measured with the DOHGS
were 95% and 66%, respectively. The DOHGS responded linearly to HgBr<sub>2</sub>. We found no evidence that elevated O<sub>3</sub> interfered
in the DOHGS RM measurements. A reduction in RM collection and retention
efficiencies at very high ambient WV mixing ratios is possible. Comparisons
between the DOHGS and participating Hg instruments demonstrate good
agreement for GEM and large discrepancies for RM. The results suggest
that existing GOM measurements are biased low
Impact of Wildfires on Ozone Exceptional Events in the Western U.S.
Wildfires
generate substantial emissions of nitrogen oxides (NO<sub><i>x</i></sub>) and volatile organic compounds (VOCs).
As such, wildfires contribute to elevated ozone (O<sub>3</sub>) in
the atmosphere. However, there is a large amount of variability in
the emissions of O<sub>3</sub> precursors and the amount of O<sub>3</sub> produced between fires. There is also significant interannual
variability as seen in median O<sub>3</sub>, organic carbon and satellite
derived carbon monoxide mixing ratios in the western U.S. To better
understand O<sub>3</sub> produced from wildfires, we developed a statistical
model that estimates the maximum daily 8 h average (MDA8) O<sub>3</sub> as a function of several meteorological and temporal variables for
three urban areas in the western U.S.: Salt Lake City, UT; Boise,
ID; and Reno, NV. The model is developed using data from June-September
2000–2012. For these three locations, the statistical model
can explain 60, 52, and 27% of the variability in daily MDA8. The
Statistical Model Residual (SMR) can give information on additional
sources of O<sub>3</sub> that are not explained by the usual meteorological
pattern. Several possible O<sub>3</sub> sources can explain high SMR
values on any given day. We examine several cases with high SMR that
are due to wildfire influence. The first case considered is for Reno
in June 2008 when the MDA8 reached 82 ppbv. The wildfire influence
for this episode is supported by PM concentrations, the known location
of wildfires at the time and simulations with the Weather and Research
Forecasting Model with Chemistry (WRF-Chem) which indicates transport
to Reno from large fires burning in California. The contribution to
the MDA8 in Reno from the California wildfires is estimated to be
26 ppbv, based on the SMR, and 60 ppbv, based on WRF-Chem. The WRF-Chem
model also indicates an important role for peroxyacetyl nitrate (PAN)
in producing O<sub>3</sub> during transport from the California wildfires.
We hypothesize that enhancements in PAN due to wildfire emissions
may lead to regional enhancements in O<sub>3</sub> during high fire
years. The second case is for the Salt Lake City (SLC) region for
August 2012. During this period the MDA8 reached 83 ppbv and the SMR
suggests a wildfire contribution of 19 ppbv to the MDA8. The wildfire
influence is supported by PM<sub>2.5</sub> data, the known location
of wildfires at the time, HYSPLIT dispersion modeling that indicates
transport from fires in Idaho, and results from the CMAQ model that
confirm the fire impacts. Concentrations of PM<sub>2.5</sub> and O<sub>3</sub> are enhanced during this period, but overall there is a poor
relationship between them, which is consistent with the complexities
in the secondary production of O<sub>3</sub>. A third case looks at
high MDA8 in Boise, ID, during July 2012 and reaches similar conclusions.
These results support the use of statistical modeling as a tool to
quantify the influence from wildfires on urban O<sub>3</sub> concentrations
Sequence data
MBO_mapping_file_impingers_controls_figshare.txt - A tab-delimited text file with sample information. The columns of the text file include a sample identifier ("SampleID"), barcode sequences ("BarcodeSequence"), forward primer sequence ("LinkerPrimerSequence"), date of sample collection ("Sample_date"), sample type (rDNA or rRNA, "Sample_type"), barcode, and sample description (samples versus controls, "Description").<div><br></div><div>seqs_figshare.fastq - Raw 16S sequence data in FASTQ format, produced by a sequencing run using Illumina MiSeq 300 bp single-end sequencing technology. </div
Do We Understand What the Mercury Speciation Instruments Are Actually Measuring? Results of RAMIX
From August 22 to September 16, 2012, atmospheric mercury
(Hg)
was measured from a common manifold in the field during the Reno Atmospheric
Mercury Intercomparison eXperiment. Data were collected using Tekran
systems, laser induced fluorescence, and evolving new methods. The
latter included the University of Washington-Detector for Oxidized
Mercury, the University of Houston Mercury instrument, and a filter-based
system under development by the University of Nevada-Reno. Good transmission
of total Hg was found for the manifold. However, despite application
of standard protocols and rigorous quality control, systematic differences
in operationally defined forms of Hg were measured by the sampling
systems. Concentrations of reactive Hg (RM) measured with new methods
were at times 2-to-3-fold higher than that measured by Tekran system.
The low RM recovery by the latter can be attributed to lack of collection
as the system is currently configured. Concentrations measured by
all instruments were influenced by their sampling location in-the-manifold
and the instrument analytical configuration. On the basis of collective
assessment of the data, we hypothesize that reactions forming RM were
occurring in the manifold. Results provide a new framework for improved
understanding of the atmospheric chemistry of Hg
Regional Influence of Aerosol Emissions from Wildfires Driven by Combustion Efficiency: Insights from the BBOP Campaign
Wildfires
are important contributors to atmospheric aerosols and
a large source of emissions that impact regional air quality and global
climate. In this study, the regional and nearfield influences of wildfire
emissions on ambient aerosol concentration and chemical properties
in the Pacific Northwest region of the United States were studied
using real-time measurements from a fixed ground site located in Central
Oregon at the Mt. Bachelor Observatory (∼2700 m a.s.l.) as
well as near their sources using an aircraft. The regional characteristics
of biomass burning aerosols were found to depend strongly on the modified
combustion efficiency (MCE), an index of the combustion processes
of a fire. Organic aerosol emissions had negative correlations with
MCE, whereas the oxidation state of organic aerosol increased with
MCE and plume aging. The relationships between the aerosol properties
and MCE were consistent between fresh emissions (∼1 h old)
and emissions sampled after atmospheric transport (6–45 h),
suggesting that biomass burning organic aerosol concentration and
chemical properties were strongly influenced by combustion processes
at the source and conserved to a significant extent during regional
transport. These results suggest that MCE can be a useful metric for
describing aerosol properties of wildfire emissions and their impacts
on regional air quality and global climate