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Update Air Quality Modeling and Monitoring in the Owens Valley Planning Area for the PM10 National Ambient Air Quality Standards Ann Logan Great Basin Unified Air Pollution Control District

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  • Update

    Air Quality Modeling and Monitoring in the Owens Valley Planning Area

    for the PM10 National Ambient Air Quality Standards

    Ann LoganGreat Basin Unified Air Pollution Control District

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    Average Exceedance (µg/m³) Exceedance Day Count

    Owens Valley Planning Area (OVPA) PM10 NAAQS Exceedances 2000-2019

    *2019 January – June data only

    NAAQS PM10 Violation= 150 μg/m3 for 24-hour periodNAAQS PM10 Attainment= 3-yr Average ≤ 1

  • YearAverage

    Exceedance (µg/m³)

    Maximum Exceedance

    (µg/m³)

    Exceedance Day Count

    2000 922 10,549 38

    2001 1,247 13,611 42

    2002 710 6,703 44

    2003 1,005 10,933 37

    2004 734 4,472 34

    2005 619 3,989 26

    2006 831 6,847 33

    2007 261 508 14

    2008 311 815 16

    2009 330 1,507 20

    2010 589 4,571 29

    2011 428 3,444 21

    2012 489 3,916 24

    2013 265 529 15

    2014 349 950 10

    2015 320 1,487 14

    2016 245 530 16

    2017 416 2,165 17

    2018 262 728 8

    2019* 280 451 4 *2019 January – June data only

    OVPA PM10 NAAQS Exceedances2000-2019

  • Site (Data Period) Peak Count (max # in a year)2018 Count

    3-yr Average(2016-2018)

    Dirty Socks (2001 - 2018) 44 3 4.33

    Keeler (1993 - 2018) 23 2 5

    Lizard Tail (2010 - 2018) 16 3 5.33

    Lone Pine (1993 - 2018) 7 1 1

    Mill Site (2012-2018) 6 1 1

    North Beach (2000-2018 10 3 4

    Olancha (1993 - 2018) 12 2 3.33

    Shell Cut (2003 - 2018) 20 5 7.67

    Stanley (2004 - 2018) 6 1 1

    PM10 NAAQS Exceedances by Site

    NAAQS PM10 Attainment= 3-yr Average ≤ 1

  • PM10 NAAQS Exceedances Source Identification

    Identification of emissive sources accomplished by review of• Evaluation of hourly PM10 data and corresponding wind

    speeds/directions• Dust Camera Review• Field Observations• Field Investigation (source mapping, ect)• Sand Flux Monitoring Data Evaluation• Owens Lake Yesterday (daily model with virtual sand flux)• Annual Modeling

  • WIND DIRECTION SCREENING

  • PM10 Pollution Roses

    2016- 2019

    Pollution Rose data includes all hours 1/1/2016-3/31/2019PM10 Federal Exceedance Data 2016-2018

  • Owens Lake Modeling

    Modeling System• CALPUFF Modeling System• Critical Inputs

    Source Areas Configuration Emissions (PM10 = Kf x sand flux) Meteorological Data

    • Source areas and sand motion data influence model results more than the K-factors and dispersion model options

    Results• Model calculates PM10 impacts to shoreline/community

    receptors for each source area• Lone Violator = source area that contributes at least 130µg/m³ to any

    shoreline/community receptor on any day• Watch Areas = source area that contributes at least 80µg/m³ to any

    shoreline/community receptor on any day• Model run yearly since the 2016 SIP to assist in determination

    if additional areas need to be ordered for control

    Model purpose is to temporarily and spatially resolve source area emissions

    Sand Flux Monitoring Network

  • SOURCE AREAS

    2014-2016 Areas 2016-2017 Areas 2017-2018 Areas

    Lone (acres)

    Watch (acres)

    Lone (acres)

    Watch (acres)

    Lone (acres)

    Watch (acres)

    Uncontrolled Lakebed

    Eligible ESA Areas (deferred) 210 0 514 91 301 26

    Unordered Lakebed 0 0 38 98 73 14

    Controlled Lakebed

    Shallow Flood Wetness Cover Refinement Field Test 456 31 25 38 10 0

    Minimum Dust Control Efficiency DCAs 0 0 0 0 0 43

    Phase 9/10 Areas (Pre-Phase and During Construction)

    1199 89 358 225 0 0

    Keeler DunesUncontrolled 412 102 385 239 106 210

    Controlled 90 10 67 0 67 0

    Individual Source Area 24-hour contribution at shoreline or community receptorLone > 130 ug/m3Watch > 80 ug/m3

    * Model includes Keeler Dunes but does not include most other off lake sources areas

    Owens Lake Modeling Results 2014-2018

  • Monitoring and Modeling Primary Sources Contributing to PM10 NAAQS Exceedances

  • To ensure continued progress towards NAAQS PM10 Attainment

    1. Maintain Current Level of Control• Avoid emissions from current controls (transition

    areas, test areas, breakdowns/variances)• Ensure any refinement of BACM criteria keeps

    necessary control efficiency in all conditions• No backsliding

    2. Work to Address Currently Emissive Areas• Annual Additional BACM Contingency

    Determination (future dust control orders)• Keeler Dunes Dust Control Project• Environmentally Sensitive Areas• Off lake sources

    3. Avoid Creation of New Sources • Groundwater pumping impacts to stable

    vegetated dunes and stable salt crust areas• Other anthropogenic activities/sources

    Owens Lake Stable Vegetated Dune Systems and Stable Salt Crust Areas

  • PM10 Pollution Rose 2016-2019

    Lone Pine

  • PM10 Pollution Rose 2016-2019

    North Beach

  • PM10 Pollution Rose 2016-2019

    Lizard Tail

  • PM10 Pollution Rose 2016-2019

    Keeler

  • PM10 Pollution Rose 2016-2019

    Mill

  • PM10 Pollution Rose 2016-2019

    Shell Cut

  • PM10 Pollution Rose 2016-2019

    Dirty Socks

  • PM10 Pollution Rose 2016-2019

    Stanley

    Update�Air Quality Modeling and Monitoring �in the Owens Valley Planning Area�for the PM10 National Ambient Air Quality Standards Owens Valley Planning Area (OVPA) �PM10 NAAQS Exceedances 2000-2019OVPA PM10 NAAQS Exceedances�2000-2019PM10 NAAQS Exceedances by SiteSlide Number 5WIND DIRECTION SCREENINGSlide Number 7Slide Number 8Slide Number 9Slide Number 10Slide Number 11PM10 Pollution Rose 2016-2019�Lone PinePM10 Pollution Rose 2016-2019 �North BeachPM10 Pollution Rose 2016-2019 �Lizard TailPM10 Pollution Rose 2016-2019 �KeelerPM10 Pollution Rose 2016-2019 �MillPM10 Pollution Rose 2016-2019 �Shell CutPM10 Pollution Rose 2016-2019 �Dirty SocksPM10 Pollution Rose 2016-2019 �Stanley