FREQUENTLY ASKED QUESTIONS

GLOSSARY

Light extinction coefficient: A measure of the amount of light attenuated by scattering or absorption as the light traverses the atmosphere, hence it is a measure of atmospheric transparency. It has units of inverse length, and is the sum of four components: light scattering by gas molecules and particles and light absorption by gas molecules and particles.

Meteorological range: The furthest distance at which a black object silhouetted against a sky would be visible assuming a 2% threshold value for distinction of an object from the background.

Particles/Aerosols: Any solid or liquid in the atmosphere with diameter between approximately 0.002 and 100 µm.

Primary particles: Particles emitted directly into the atmosphere.

PM10: Particles of diameter 10 µm. Also referred to as 'inhalable particles'.

PM2.5: Particles of diameters 2.5 µm (fine particles). Typically, dry fine (PM2.5) particle mass is dominated by; sulphates, organics, ammonium nitrate, soil, and elemental carbon.

Receptor oriented source apportionment: Techniques used to identify the sources (origins) of particles. These techniques rely on the principle of defining patterns within ambient samples of chemically speciated particulate matter to infer source types.

Secondary particles: Particles formed within the atmosphere from gaseous precursors.

Source oriented source apportionment: Relate emissions to ambient concentrations using numerical models which simulate the physical and chemical transport and transformations.

TSP: Total suspended particles. The total atmospheric aerosol burden.

Visibility: The distance at which the contrast of the target is equal to the threshold contrast value for the human eye.

Visual range: The greatest distance at which a black target can be perceived against the horizon.

Units:
µm: micro-meter (micron) (10-6 m-1)
µg m-3: micro-gram per meter cubed.
ng: nano-gram (10-9 grams).


BACKGROUND INFORMATION

What is visual air quality?
Humans see an object as a result of light reflected from the object (we actually see the object in terms of a contrast against the background, so a black target silhouetted against a light coloured sky is more visible than a light target against a light sky). As light from the object traverses the atmosphere some portion of the beam is scattered away from the observers view or absorbed by particles and gases in the atmosphere. Equally, light from other "sources" can be scattered into the observers line of sight and therefore reduce the perceived contrast of the viewed object. Hence it can be shown that visibility (the ability of the observer to see an object) will decrease as the amount of particles and gases in the atmosphere increases (resulting in decreasing atmospheric transparency). Visibility is often defined within air pollution literature as the distance at which the contrast of a visual target against the background (usually the sky) is equal to the threshold contrast value for the human eye.

(1)    i.e. Visual Range (VR) = ln(C(0)/Cd)/bext
where: bext = light extinction coefficient which is a measure of atmospheric transparency.
C(0) = objects inherent contrast (i.e. contrast at zero distance)
Cd = threshold for detection of the objects contrast.
Note: Using this definition, the visual range is the distance at which the target is just visible.
The extinction coefficient, bext is given by;
(2)    bext = bsp + bsg + bap + bag
where bsp, and bsg are the scattering coefficients by particles and gases, respectively,
and bap and bag the absorption coefficients for particles and gases, respectively.

In general, light scattering by particles is the largest of the terms in (2). Scattering of light by particles is most efficient for small particles of diameter approximately equal to the wavelength of the incident light. Given that sunlight has its maximum intensity at around 0.3 *10-6 m-1, this is the diameter of particles that most efficiently scatters light and reduces visibility.

Visibility perception is more complex than simply calculating visual range, and human perception of visibility conditions includes the effects of atmospheric constituents on the ability of an observer to see colour, texture, and form of both near and distant vistas, and the scene characteristics. Protection of visibility/visual range/Visual Air Quality (VAQ) is difficult to regulate because unlike other atmospheric pollutants, it involves physiological parameters of human perception. As Saxena and Weintraub (1990) state; "This perception involves the combination of the following: (1) the thermal structure and water vapor gradients in the atmosphere, (2) ambient concentration, chemical composition, and size distribution of particulates and gases, (3) illumination of the target and sight-path associated with cloud cover, (4) the physical characteristics of the target itself, and (5) the disposition of the observer."

What are atmospheric aerosols?
"Atmospheric particles" and "atmospheric aerosols" are terms used to describe both solid and liquid matter suspended in the atmosphere. Elevated particle concentrations in the atmosphere are responsible for health impacts, and degradation of visual air quality. Atmospheric aerosols may be emitted directly into the atmosphere (primary particles), or may form within the atmosphere from gases (secondary particles). Typically secondary aerosols have relatively small diameters and so are efficient at scattering light, are easily inhaled into the respiratory tract and have long atmospheric lifetimes. Three categories of atmospheric particles are defined based on particle size diameter and effects of the particles;

The relative abundance of particles in these size ranges; TSP, PM10 and PM2.5 is highly variable in space and time, and has a profound influence upon the potential health and visibility impacts of a given aerosol mass.

Which parameters are typically used to characterized visibility?
Visibility related characteristics and measurements may be partitioned into three groups:

  • Optical - The ability of the atmosphere to scatter or absorb light passing through it. The physical properties of the atmosphere are described by extinction, scattering and absorption coefficients plus an angular dependence of the scattering known as the normalized phase function.
  • Aerosol - The physical properties of the ambient atmospheric particles (chemical composition, size, shape, concentration, temporal and spatial distribution and other physical properties).
  • Scene - The appearance of a scene viewed through the atmosphere. Scene characteristics include observer visual range, scene contrast, colour, texture, and clarity.

What are typical background concentrations of atmospheric aerosols?
Under the NAPAP research effort Trijonis (1990) developed estimates of natural background annual average aerosol concentrations for the western United States for coarse particles (2.5-10 µm) and fine aerosols (<2.5 µm) of 1.5 and 3 µg m-3, respectively.


REVEAL II AND THE REVEAL II DATABASE

What was REVEAL?
REVEAL (Regional Visibility Experimental Assessment in the Lower Fraser Valley) was a field campaign conducted during July and August 1993 to characterize summertime visibility and ambient aerosol loadings in southwestern British Columbia (B.C.).

What is REVEAL II?
REVEAL II is a field programme which was conducted to assess visibility and aerosol conditions in the Fraser Valley over an entire year and hence was designed to supplement the information collected during REVEAL. The main aims of REVEAL II were to collect and analyze ambient data in order:

  1. To characterize aerosol and visibility conditions in the Fraser Valley (FV) over an entire year.
  2. To provide public information regarding the sources and effects of current aerosol concentrations.

What was measured during REVEAL II?
To meet the objectives listed above, three groups of visibility related characteristics and measurements were monitored at sites in the Fraser Valley during April 1994 - June 1995.

  1. Optical - The ability of the atmosphere to scatter or absorb light passing through it (the atmospheric transparency). Particle light scattering (bsp) was measured on a semi-continuous basis at Chilliwack (CHIL) and Clearbrook (CLBR).
  2. Aerosol- The physical properties of the ambient atmospheric particles (chemical composition, size, shape, concentration, temporal and spatial distribution and other physical properties). 24 hour average fine aerosol concentrations and composition were monitored at two sites; Chilliwack (CHIL) and Clearbrook (CLBR). Sampling occurred on Saturdays and Wednesdays.
  3. Scene - The appearance of a scene viewed through the atmosphere. Scene characteristics include observer visual range, scene contrast, colour, texture, and clarity. Photographs to document scene characteristics were taken three times daily at Abbotsford International Airport (AIA) (this site was later moved to Matsqui Municipal Hall (MMH)) and CHIL. At two further sites, Hope (HOPE) and Mission (MISS) further cameras were deployed to record scene characteristics.

What other data are contained in the REVEAL II data base?
In addition to the data collected specifically under the REVEAL II monitoring campaign, other data which are useful to understanding visibility and aerosol concentrations in the valley have been incorporated into the database. These include the following datasets kindly provided by both local and federal agencies e.g. British Columbia Ministry of Environment, Land and Parks (BCMoELP), Greater Vancouver Regional District (GVRD), Atmospheric Environment Service (AES).

  1. Hourly average PM10 concentrations. These data help to examine spatial variability for aerosol concentrations (many of the sites are in the western valley where aerosol monitoring was not undertaken as part of REVEAL II), and because they are hourly data they provide information regarding the diurnal variability of aerosol concentrations.
  2. Hourly average routinely collected meteorological observations (including wind speed and direction, surface pressure, relative humidity, temperature, cloud cover, visual range) from Vancouver International Airport (VIA) and Abbotsford International Airport (AIA). These data help to determine meteorological conditions (and source regions) of pollutants monitored at the REVEAL II sampling locations.
  3. Hourly average gas concentrations (including ozone (O3), sulphur dioxide (SO2), nitrous oxide (NO), NOx, carbon monoxide (CO)). Many of these species are precursors of aerosol formation (they are the "building blocks" or ingredients of aerosol formation).
  4. Profiles of upper air parameters recorded twice daily from the radiosonde release site at Quillayute on the Olympic Peninsula (from NCDC).

What is required to use the REVEAL II database?
The database described in Pryor and Barthelmie (1999) has been designed using the Paradox software package. To use this database you require:

The data contained within the database are also provided in ASCII format (as ordinary DOS files which can be read with any editor). The advantage of using the data in the database is that a central time index has been supplied to link the data. Thus it is possible to perform straight-forward data analysis and manipulation using data from different sources. Data within the database are uniquely identified using field names and a time index. The database also includes files which describe the data.

How do you use the REVEAL II database? (an introduction to the basics)

How were the data in the data base quality checked?
It was assumed that all

  • meteorological data provided by AES and NCDC
  • and PM10 and gaseous data provided by GVRD and BCMoELP
have been subject to rigorous quality control at source (confirmed by agencies supplying the data) and so no further quality assurance was performed on this data and no QA codes have been assigned. The data collected under the REVEAL II monitoring campaign was rigorously assessed for quality and codes applied which indicate the level of data quality of each data point. No data have been removed from the database, but data which are considered suspicious or dubious quality or which lie outside the expected range of data values have been assigned the appropriate QA codes (which are described in Pryor and Barthelmie 1996).

Which other resources have been developed to aid use and interpretation of the REVEAL II data?
A World Wide Web site has been designed which summarizes the REVEAL II data, analyses and results. This WWW site may be accessed from:
http://php.indiana.edu/~spryor.


ANALYSIS AND INTERPRETATION OF DATA COLLECTED DURING REVEAL II

What was the average meteorological range at Clearbrook and Chilliwack during REVEAL II?
During REVEAL II the average meteorological range at both sites calculated for periods of simultaneous measurements were as follows: CLBR = 30 km, CHIL = 36 km.

How spatially homogeneous were visibility conditions during REVEAL II?
Surface visual range from Vancouver and Abbotsford International Airports, light scattering from nephelometers, and visibility estimated from photographs show a high degree of association (spearman correlations are significant for all variables at all sites). Light scattering measurements from CLBR and CHIL show the highest degree of association (correlation) in the daytime. This implies that at night local conditions may be decoupled from regional air quality.

What were average PM10 concentrations during REVEAL II?
Hourly PM10 concentrations observed using TEOMs deployed at a number of sites in the Fraser Valley showed average concentrations of between 8 and 18 µgm-3. Data from these sites showed the levels exceeded 30 µgm-3 on an average of one hour in ten, and occasionally exceeded 50 µgm-3 during REVEAL II. PM10 concentrations in the valley were highest at T28 (Downtown Abbotsford).

What were average PM2.5 concentrations during REVEAL II?
Average fine mass measured during REVEAL, was approximately 8 µgm-3 at CLBR and 9 µgm-3 at CHIL. These values are six times the natural background concentration proposed for the western USA.
On average PM2.5 contributes in excess of half of 24 hour average PM10 and occasionally contributes as much as 3/4 of PM10. (This indicates the presence of significant quantities of secondary aerosols.)

What was the PM2.5 'made of' (i.e. what was the average composition of the fine aerosol)?
Inorganic aerosol species dominated measured fine mass during REVEAL II at both
CLBR and CHIL but organic aerosols are a consistently high proportion of measured mass.

How did the composition of the PM2.5 vary with season?
The mean seasonal contributions of the five components of fine mass indicate: Highest nitrate and sulphate were observed in the summer. Highest organic mass was observed in the autumn and winter seasons. Lowest elemental carbon concentrations were observed during the summer. Highest soil concentrations were observed in winter perhaps due to the influence of strong outflow events and the large source areas available during the winter season.

How much of the sulphate aerosol might be marine derived?
Using algorithms from the IMPROVE network and ambient data from the IMPROVE samplers deployed at Clearbrook and Chilliwack it was shown that a maximum of up to 39 and 34% of the total S recorded at
CLBR and CHIL (respectively) is of marine origin.

Which aerosol components were primarily responsible for the visibility impairment?
Reconstructed light scattering budgets indicate inorganic aerosol species dominated light scattering at both CLBR and CHIL. Days with high light scattering were characterized by higher nitrate and organic aerosol concentrations suggesting that these aerosol components may be the primary cause of variability of visibility conditions.
Average particle light scattering efficiencies are higher at CLBR than CHIL. This indicates that on a per unit mass basis aerosols at CLBR degrade visibility more efficiently than those sampled at CHIL. This reflects differing aerosol composition and is an explanation of the observation that meteorological range is lower at CLBR despite lower average fine mass.

What are the major sources of PM2.5?
Receptor modeling to identify sources of ambient aerosols indicates the following components dominate the sources of fine mass at the two receptor sites:
CLBR: Mobile emissions, secondary aerosols, primary geologic materials, industrial emissions and a marine contribution (listed in terms of average contribution to measured mass).
CHIL: Mobile emissions, secondary aerosols, primary diesel emissions, primary geologic materials, a marine contribution and a local component (dominated by iron) (listed in terms of average contribution to measured mass).


   
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