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Jim Sullivan Ruth Roberson
Steve Irwin aq-ppt5-10
• What we do now? • Why refine what we do? • Scope of existing quantitative practices • Why geostatistic approaches are preferred • Case Study • Driving question – Guidance or Working Practice? • Thoughts and Comments
• Current Guidance • Hierarchy of choices
• Design Value • Representative Monitor • Alternative approaches
• Design Values are low • Representative monitor guidance reflects elements of a
quantitative analysis • Needs clarification to set expectation • Begs the question
• When does clarification look more like a new approach? • Guidance revision? Working practices memorandum? Other?
• Clarity of purpose • More realistic selection of monitor for development of a
background • Based on available data
• Recognize importance of the most relevant factors • Source and Emission Density are primary drivers • Terrain and meteorology are relevant explanatory components
• Make clear that this approach is for the selection of a monitor • Background can be calculated in a variety of acceptable ways
• Qualitative is meaningless in this situation • Thematic data is not indicative of the conditions present in the modeled or
monitored domains • Quantitative data exists for nearly the entire state (some surrounding
states as well)
• Statistical and Geostatistical approaches are available • Statistical is “aspatial” in that it does not account for distances between
points • This is a key dimension that is omitted from traditional statistical
approaches • Most analysts treat data as normal or log-normal
• This is frequently not appropriate
• Geostatistical approaches are preferred • Accounts for spatial distance between points • Quantitatively address
• Characteristics of distributions • Pattern analysis
• MPCA and other State Agencies have digital data sets • Most (if not all) analysis can be completed in ARCGIS
• Most extensions are license-specific • The proposed Guidance refinement reflects standard geostatistical practices
• Considers statistically “representative” analysis between monitoring locations and modeling domain
• Practical differences can be resolved through additional lines of data • Meteorology, surface roughness, terrain, etc.
• Proposed new construction of a large coal-fired brewery in north-central Minnesota (St. Cloud). • Expected emissions of SO2 are 98 Tons Per Year
• Will be higher after planned expansion • No ambient SO2 air quality monitor is present in the area • Design value is too high for the proposers comfort • Project proposer wants to use a more refined approach based on
monitoring data
First Task: Find a “representative” monitor
• What does a “representative” monitor look like?
• What data do I use? • What methods do I need to use to conduct
the analysis? • How do I present the findings?
• What does a “representative” monitor look like? • Statistical and Practical Significance is relevant
• Focus is on point sources • Recognize other sources may be relevant
• Comparison must be made with same size geographic area • 50 kilometer radius from the source under review and selected monitor
• Compositionally, geographic areas must include same/similar type of setting or context • Spatial location of emission sources • Emission inventory data
• Especially “significant” sources in the inventory • Meteorology and terrain
• This is the key feature of the analysis!
• What data do I use? • Existing MPCA Nearby Source Tool has most current data • Spatial and emission
• Will likely augment with an emission density layer to facilitate analysis
• Meteorology • Terrain
• What methods do I need to use to conduct the analysis?• ARCGIS• First step – compare monitoring site(s) with modeling domain.
Visual inspection of an emission density map (tpy/km) shows that there are only a few sites that match with the modeling domain for the brewery:
• Rochester• Metro Region
(Potentially high)
• Next step – compare distribution and patterns of Rochester & Metro to Brewery
• Distance between center and points • Band Correlation Statistic
• Compares sites through covariance and correlation
• Spatial Autocorrelation • Compares each site to theoretical distribution to evaluate whether a site is
random or clustered
• If it looks favorable – conduct remaining analysis • Meteorology • Terrain
Rochester Ellenbecker Bros. Brewery
Metro Site
1 = Rochester; 2 = Metro Monitor; 3 = Ellenbecker Bros. Brewery Site.
• Similar comparison with meteorology and terrain
• How do I present the findings?
•Submit as a memorandum with the protocol •Follow the stepped format • Include summary of analysis with relevant tables and figures
•See case study for example
• Feedback is critical • Guidance, Working Practices Memorandum or Work Group
• Each have merit
• Recognize that most firms have GIS talent in-house • May not have all extensions needed
• Analytical tasks in this Case Study are fundamental GIS tasks • Analysis only supports the selection of a monitor – does not
account for a background concentration • Separate analysis
• Current data set is point-source based • Can be augmented to account for other sources • Typically as a modifier