national air toxics trends stations (natts) overview · llas county, fl tampa, fl u th dekalb, ga...
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National Air Toxics Trends Stations (NATTS) Overview
Beth Landis, OAQPS/AQAD
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AcknowledgmentsNATTS N t k A t R t W it• NATTS Network Assessment Report Writers
– Regi Oommen, ERG– Joe Fanjoy, ERG
• NATTS Network Assessment WorkgroupNATTS Network Assessment Workgroup – Mike Jones, EPA/OAQPS– Dennis Mikel, EPA/OAQPS– David Shelow, EPA/OAQPS
Barbara Driscoll EPA/OAQPS– Barbara Driscoll, EPA/OAQPS– Ted Palma, EPA/OAQPS– Laurie Trinca, EPA/OAQPS– Donnette Sturdivant, EPA R4
M t i C dill EPA R5– Motria Caudill, EPA R5– Bilal Qazzaz, EPA R5– Adam Eisele, EPA R8– Eric Stevenson, Bay Area Air Quality Management District– Stephanie McCarthy, Kentucky DEP
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Background
• NATTS Network Created to Generate Long-Term, Quality Assured, Standardized Ambient Air Toxics y ,Data to:– Identify Trends in Air Toxic Concentrations
Evaluate the Effectiveness of National Hazardous Air– Evaluate the Effectiveness of National Hazardous Air Pollutant (HAP) Reduction Efforts
– Ground Truth Air Quality and Human Exposure ModelsDi t I t i t S R t M d l– Direct Input into Source-Receptor Models
– Assess Population Exposure and Background-Level Concentrations
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NATTS Sites & Years Established
(7)(7)(20)
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Minimum Required NATTS AnalytesVOCs Carbonyls PM10 Metals
Acrolein Formaldehyde Nickel compounds
Benzene Acetaldehyde Arsenic compounds
Chloroform Cadmium compounds
1 3 b t di PAH M d1,3-butadiene PAHs Manganese compounds
Vinyl Chloride Benzo(a)pyrene* Beryllium compounds
Perchloroethylene Naphthalene* Lead compoundsy p p
Carbon Tetrachloride
Trichloroethylene TSP Hexavalent Chromium*
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* Not an original Core HAP
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NATTS Network Assessment• Review of the NATTS Network Required in the Final
Draft of the National Monitoring Strategy, Air Toxics Component (U S EPA 2004)Component (U.S. EPA, 2004)– “Although the longevity of trends sites typically extends over
a decade or more, the NATTS must be evaluated, and modified as needed on 6 year intervals to assure continuedmodified as needed, on 6-year intervals to assure continued relevancy, consistent with the procedures established under the National Strategy”
• Network is Older than 6 Years, However Many of the Original Sites did Not Begin to Fully Sample the Initial Core HAPs Consistently until 2005Core HAPs Consistently until 2005
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Scope of AssessmentP li l t ti t b dd d i th• Policy-relevant questions to be addressed using the assessment:
– Is the network design appropriate/optimal to achieve the goals and objectives?objectives?
– Are the NATTS goal and objectives still relevant?– Are the data collected adequate to meet the program goals?– What changes to the current network design would be appropriate to
improve the NATTS
• Assessment examined whether data collected of complete and adequate quality to meet program level data quality objectiveadequate quality to meet program-level data quality objective (DQO):
– “To be able to detect a 15 percent difference (trend) between the annual mean concentrations of successive 3-year periods within acceptable levels of decision error.”
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Draft Network Assessment Outline
• NATTS network sites• Network requirementsq• MQO scoring• AQS reportingg• Statistical overview of data (preliminary)• Trends results (preliminary)• Site operator interviews• Observations and recommendations
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Preliminary Comparison of 2010 MDLs with Target MDL,5th and 95th percentile observations for Lead
10.0
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95 Percentile Concentration = 16.3 ng/m
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National Summary Statistics (Preliminary)
Analyte Site Type%
Detections
Arithmetic Mean*
(µg/m3)Analyte Site Type
%
Detections
Arithmetic
Mean*(µg/m3)Detections (µg/m3)
Acetaldehyde
Urban 100% 1.88 ± 0.05
Rural 98% 1.57 ± 0.06
All Sites 99% 1.79 ± 0.04
Detections Mean (µg/m3)
Formaldehyde
Urban 100% 2.99 ± 0.07
Rural 100% 3.05 ± 0.11
All Sites 100% 3.01 ± 0.06
Benzene
Urban 100% 1.14 ± 0.02
Rural 80% 0.64 ± 0.03
All Sites 95% 1.01 ± 0.02
Urban 84% 0.129 ± 0.006
Lead (PM10) (ng/m3)
Urban 99% 5.62 ± 0.29
Rural 99% 2.61 ± 0.19
All Sites 99% 4.81 ± 0.22
Urban 87% 0.395 ± 0.135
Butadiene, 1,3-
Urban 84% 0.129 0.006
Rural 19% 0.011 ± 0.003
All Sites 68% 0.100 ± 0.005
Urban 97% 0.587 ± 0.004
Tetrachloroethylene
Urban 87% 0.395 0.135
Rural 25% 0.043 ± 0.013
All Sites 72% 0.308 ± 0.102
Urban 55% 0.076 ± 0.023
Carbon Tetrachloride Rural 66% 0.368 ± 0.012
All Sites 89% 0.534 ± 0.005
Chloroform
Urban 86% 0.2221 ± 0.015
Rural 40% 0.042 ± 0.003
Trichloroethylene Rural 13% 0.010 ± 0.003
All Sites 45% 0.060 ± 0.018
Vinyl chloride
Urban 20% 0.006 ± 0.001
Rural 13% 0.005 ± 0.001
10
All Sites 75% 0.177 ± 0.012
y
All Sites 18% 0.006 ± 0.001
* In calculations involving non-detects (ND), a value of 0 was used (similar to school air toxics approach)
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Inter-comparison of Sites Close in Proximity
Paired Sites
# Pollutants, #
PollutantsPaired Sites no sig. diff.
Pollutants, sig. diff.
LA & Rubidoux, CA 12 6
Pinellas CountyPinellas County & Tampa, FL 6 12
Providence, RI& Roxbury, MA 11 7
Richmond, VA & 8 10
Inter-comparison sites
Richmond, VA & DC 8 10
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Results of DQO Trends AnalysisPollutant Pollutant Group Units of Measure
Number of Sites
Used in Averaging2005-2007 2008-2010 %Difference
Tetrachloroethylene VOC μg/m3 12 0.39 0.22 -42.6%
Hexavalent Chromium Hexavalent Chromium ng/m3 12 0.026 0.016 -37.4%
Lead (PM10) PM10 Metal ng/m3 12 4.63 3.02 -34.6%
Trichloroethylene VOC μg/m3 15 0.057 0.038 -33.5%
Nickel (PM10) PM10 Metal ng/m3 11 1.85 1.25 -32.4%
Cadmium (PM10) PM10 Metal ng/m3 14 0.27 0.19 -28.6%
B di 1 3 VOC / 3 12 0 119 0 086 28 3% asin
g
Butadiene, 1,3- VOC μg/m3 12 0.119 0.086 -28.3%
Beryllium (PM10) PM10 Metal ng/m3 12 0.056 0.043 -22.2%
Formaldehyde Carbonyl μg/m3 12 2.87 2.34 -18.6%
Benzene VOC μg/m3 14 1.07 0.87 -18.2%
Acetaldehyde Carbonyl μg/m3 13 1 93 1 62 -15.9%
Dec
rea
Acetaldehyde Carbonyl μg/m 13 1.93 1.62 15.9%
Manganese (PM10) PM10 Metal ng/m3 13 6.20 5.30 -14.6%
Arsenic (PM10) PM10 Metal ng/m3 8 0.89 0.78 -12.2%
Carbon tetrachloride VOC μg/m3 10 0.57 0.62 8.7%
Vinyl chloride VOC μg/m3 13 0.0029 0.0034 15.9% easi
ng
Chloroform VOC μg/m3 15 0.21 0.24 16.5%
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Incr
e
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Observations & Recommendations• DQO trends analysis indicates 13 pollutants decreasing and 3 increasing
– Important to continue monitoring to determine if increase is due to lowering of MDLs (fewer substitutions for NDs), or is an actual trend
• High MDLs accounted for majority of datasets excluded from trends analysis– NATTS participants should use report to determine if any data excluded from trends analysis and
what can be done to prevent this in the future (e.g., working with labs to lower MDLs)
• Many data reporting issues identified and resolved due to careful review of data in AQS for use in the assessment
– More frequent review of NATTS data by OAQPS & regional office
• Important to monitor pollutants with chronic health benchmark levels & NATA risk drivers
– Continue encouraging reporting of all monitoring data
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Observations & Recommendations (cont.)
• NATTS Proficiency Testing (PT) program has been extremely beneficial in improving laboratory performance
– Increase proficiency testing samples to twice annuallyp y g p y
• Many sites and laboratories operating sampling and analytical equipment purchased prior to 2001
– Work with regional offices to re-task residual funds for equipment upgrades
• Some sampling and analysis methods approved for the NATTs program have not been revised in over 10 years
– Refine sampling and analytical methods (e.g. TO methods)
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Future Plans for Network Assessment• Determine whether:
– Sites should be added or removedRequired analytes should be added or removed– Required analytes should be added or removed
– Determination of target MDLs should be modified– Program-level DQOs should be refined– MQOs should be refined– Current analytical and/or method precision calculations
should be revised
• Use assessment findings to update NATTS TAD
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Going Forward…P d Ti liProposed Timeline:• Now through early June - conference calls with NACAA monitoring steering
committee, regions & states to review document & address comments• June 18th - comments due from stakeholdersJune 18 comments due from stakeholders• July 9th - comments incorporated & next draft completed
Ongoing:W kl /bi kl i i h NATTS k b i dd i• Weekly/bi-weekly meetings with NATTS workgroup to begin addressing addition/reduction of sites & pollutants, MDLs, DQOs & MQOs, etc.
• Reinitiate quarterly air toxics calls with regions & states to review document & other NATTS issues
We are currently seeking S/L volunteers to join the NATTS Network Assessment Workgroup. If interested, please contact Beth Landis (landis elizabeth@epa gov)([email protected])
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