1 PAMS IN THE OZONE TRANSPORT REGION March 2, 2011 MEDEP Monitoring Meeting Tom Downs, CCM Chief Meteorologist Maine DEP-BAQ 207-287-7026

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Presentation transcript:

1 PAMS IN THE OZONE TRANSPORT REGION March 2, 2011 MEDEP Monitoring Meeting Tom Downs, CCM Chief Meteorologist Maine DEP-BAQ

2 Overview of NESCAUM PAMS Workgroup’s Efforts Reviewed: EPA guidance –Focused on linking common species to emission sources. –Anticipated that major sources would become SIP focused Past EPA PAMS Analyses –Often focused on redundancies and how the network can be reduced

3 TYPE 1 – UPWIND/background site TYPE 2 – MAXIMUM EMISSIONS site TYPE 3 – MAXIMUM OZONE concentration site TYPE 4 – Extreme DOWNWIND site 1or4? 1/3 1/4 1/3 1or4? 1/3 1/4 1/3

4 Overview of NESCAUM PAMS Workgroup’s Efforts Also Reviewed: Detection limits Common species –Are some species too often below MDL to be useful? –Are there species that should be added? Carbonyls – data quality, are they worth the cost? Is the newer, more sensitive or less expensive analytical techniques? (Synspec – gets more compounds including more biogenics) Data analyses by state

5 DATA PROCESSING Summary statistics calculated –Average concentrations (by site and by classification) –Percent of data below minimum detect levels –Percent data recovery rates QA checks –Check for qualifier flags and delete obvious invalid data –Check for units consistency and convert to correct units if necessary –Box plots to identify outliers? –Concern with the frequency of below minimum detects?

6 Overview of NESCAUM PAMS Workgroup’s Preliminary Findings Concluded: Data analysis should also be done regionally PAMS data critical for regional modeling efforts State survey found that many (but not all) states don’t know or trust their carbonyl data quality. States still submitted data to AQS as required. – Known problems with acrolein – EPA pulled data from AQS – Suspected quality problems with other carbonyls – OAQPS looking into. Will look at Regional Network Needs Under New Ozone NAAQS Implementation rule

7 Should we analyze all VOC species in future data analyses? On the ftp site - analyses for each site comparing trends for the full suite of VOC’s vs. a reduced (“focused”) PAMS species list of 23 and 7 compounds Preliminary analyses are also included –% unidentified VOC’s –Benzene/tolulene ratios –Ranking of VOC’s

8 Sub-Grouping of 54 Target PAMS Compounds 23 Target Compounds 7 Target Compounds

9 ALL hourly sites TYPE 1 sites TYPE 2 sites TYPE 3 sites TYPE 4 sites Rankings of VOC’s during hours of an Ozone event day (8-hr > 70 ppb) Only in the 23 target compounds list In both the 23 and 7 target compounds lists Only in the 7 target compounds list

10 Cape Elizabeth, Maine PAMS SITE - Benzene SAS JMP statistical software used Annual Box and Whisker Plots by Site and Key Species Philadelphia PAMS SITE - Benzene Comparative line drawn at 2ppbC

11 TYPE 1 SITE Type 1 (Upwind) Site Trends

12 TYPE 1 SITE Type 1 (Upwind) Site Trends

13 TYPE 2 SITE Type 2 (High Emission) Site Trends

14 TYPE 2 SITE Type 2 (High Emission) Site Trends

15 TYPE 3 SITE Type 3 (High Ozone) Site Trends

16 TYPE 3 SITE Type 3 (High Ozone) Site Trends

17 TYPE 4 SITE Type 4 (Downwind) Site Trends

18 As VOCs Emissions are Reduced, There are More Below Detection Limits

19 NO/NOy Trends(?)

20 Aging Ratios – Benzene/Toluene

21 Wind Directions During High Ozone

22

23

24 NESCAUM PAMS Workgroup Data NESCAUM PAMS ftp data archive: ftp://airbeat.org/PAMS/ MEDEP links to PAMS data sets and analyses files : UM_PAMS_DATA/ UM_PAMS_DATA/ and UM_PAMS_ANALYSES/