Construction TRB 2007 Final Revised

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    UC Davis-Caltrans Air Quality Project 1

    Construction Emissions: Using Project Data to

    Improve Regional Inventories

    Douglas Eisinger, Ph.D.

    Deb Niemeier, Ph.D., P.E.

    UC Davis-Caltrans Air Quality Project

    Presented at the 86th Annual Meeting of theTransportation Research Board, Workshop 135

    Guidelines on Conducting Project Level Air

    Quality AnalysisWashington, D.C. January 21, 2007

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    Outline

    1. Motivation: Need Local Activity Data

    2. Setting the Context: Example Project

    3. Top-Down Regional Emissions

    4. Bottom-up Regional Emissions Number and type of construction projects per year

    Equipment and use per project Emissions

    5. Sacramento Example: Bottom-up Inventory

    6. Comparison: Top-Down vs. Bottom-up

    7. Some Observations8. Conclusions

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    1. Motivation: Need Local Activity Data

    Powerpoint From Caltrans Training Exercise

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    2. Setting the Context: Example Project

    1.7 mile long I-80 auxiliary lane addition in Sacramento

    6 month project, four construction stages: Land clearing

    Roadway grading and excavation

    Drainage/utilities/sub-grade

    Paving

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    Sacramento Project:Year 2008 NOx Emissions

    Analysis inputs Total disturbed project area: 8 acres

    Soil moved: 300 yd3 per day (imports and exports)

    Model-Assigned Equipment by phaseSign

    Boards Bulldozer Scrapper Excavator Grader

    Rubber

    tired

    loader Compactor Trencher Paver

    Paving

    Equip Roller

    Clearing 3 1 1

    Grading 3 1 1 1 1

    Drainage/

    Utilities/

    Sub-grade

    3 1 1 1 1

    Paving 3 1 1 2

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    Modeled with Sacramento area air district tool

    Total project NOx emissions: 3.5 tons

    But emissions would be about 10-15% lesswith solar sign boards

    (instead of diesel-powered sign boards)

    Lets look at building a regionalinventory

    Sacramento Project:Year 2008 NOx Emissions

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    3. Sacramento NOx Emissions: Top-Down

    Diesel Construction (19 tpd)

    All Other Sources (219 tpd)

    Diesel-powered construction is 8% of annual averageNOx emissions (2008)

    Basis: regional equipment populations, activity, and

    OFFROAD emission factors

    Note: transportation construction is not separated

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    Top Down: Estimating TransportationConstruction NOx

    Need to disaggregate total construction emissions

    Possible approaches Road construction PM emissions are 58% of all

    construction and demolition PM emissions

    ARB construction equipment population surveys: SIC Group 161 (highway / street construction) is 12%

    SIC Group 162 (includes bridge, tunnel, elevated highway) is 38%

    SIC 161 + 162 equal 50% of all construction equipment

    Possible range 12-58% of all construction =transportation construction

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    4. Bottom Up Regional Emissions

    Data needs: Equipment and use per project

    Number of construction projects

    Emission factors

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    Equipment and Use Per Project (1 of 2):California Statewide Data

    UCD created data set ofCaltrans projects for

    years 2000-2005

    Established six majorconstruction categories

    Project Type N

    1. Resurface ExistingHighway 38% 716

    2. Pavement Rehabilitation /Widening 24% 453

    3. Construct Freeway / ExtraLane 11% 215

    4. Landscaping 11% 215

    5. Construct median, thriebeam barrier 9% 170

    6. Construct, ReconstructBridge 6% 118

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    Equipment and Use Per Project (2 of 2)

    Collected daily reports(diaries) for 30 projects

    Built data set of equipment

    activity by project

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    Year 2008 NOx Emissions for Average Project

    Equipment Category Hrs/Project NOxEFs* Tons/Project % ofNOx

    Rollers 688 390 0.296 11%

    Rubber Tire Loaders 376 593 0.246 9%

    Graders 257 734 0.208 8%

    Generator Set 278 658 0.202 8%

    Scrapers 113 1,494 0.187 7%

    Tractors / Loaders /Backhoes 436 360 0.173 7%

    Subtotal for top six 2149 1.3 50%Total (entire project) 6149 2.7 100%

    *EFs: gms/equip piece/hr (from OFFROAD2007)

    Wide range by project type:

    0.3

    10.7 tons

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    5. Sacramento Example: Bottom-Up Inventorya. Number of Projects

    Caltrans data: 57 Caltrans projects / year

    SACOG data: 63 other transportation projects / year

    Total: 120 projects per year

    Source: average of 2004-2006 project datafrom Caltrans and SACOG.

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    5. Sacramento Example: Bottom-Up Inventoryb. 2008 Regional NOx Emissions Estimate

    Ave. project:

    2.7 tons NOx

    X

    120

    projects/yr

    =289 NOxtons/yr

    Ave. project:253 days

    =1.1 NOx

    tons/day

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    Sacramento Example: Caveats

    Lots of assumptions! Caltrans data set is representative

    Other Caltrans projects are similar to top six categories

    SACOG projects are similar to Caltrans projects

    Average project represents typical project mix for a given year

    Main point illustrate concept,give sense of scale to emissions

    Ave. project:2.7 tons NOx

    X

    120projects/yr

    =289 NOxtons/yr

    Ave. project:253 days

    = 1.1 NOxtons/day

    Ave. project:2.7 tons NOx

    X

    120projects/yr

    =289 NOxtons/yr

    Ave. project:253 days

    = 1.1 NOxtons/day

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    6. Comparison: Top-Down vs. Bottom-UpSacramento 2008 NOx Emissions

    Top-Down (OFFROAD2007)

    All NOx = 238 tpd

    All construction = 19 tpd

    IF THEN

    58% = trans. 11 tpd(PM %)

    50% = trans. 9.5 tpd(SIC 161 + 162)

    12% = trans. 2.3 tpd(SIC 161 only)

    Bottom-Up1.1 tpd = trans.

    In this illustration, top-downemissions are 2-10 X higher

    than bottom-up

    0

    2

    4

    6

    8

    10

    12

    58% of Top Down 50% of Top Down 12% of Top Down Bottom-Up Method

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    7. Some Observations

    Activity varies by project type in Caltrans data

    Project duration: 181 394 days Total projectNOx emissions: 0.3 10.7 tons

    Caveat: data set needs to be expanded to better representindividual project types

    Main point: estimating project emissionsrequires activity data specific to project type

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    Some Observations: Off-Road Modeling Not asMature as On-Road Modeling

    Nov. 2006: California ARB releases OFFROAD2007 8% less equipment than prior model

    Construction equipment useful life doubled from prior model

    Equipment Old New Diff

    Graders 6510 6178 - 5%

    Tractors/Loaders/Backhoes 33,990 28,213 - 17%

    Pavers 2616 2710 + 4%

    Example year 2000 equipment populations (statewide)

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    8. Conclusions

    Activity assumptions are central to emissions estimates

    Inventory tools are still in early development stages

    Bottom-up can quality-check top-down inventories

    Sacramento illustration includes lots of assumptions but results imply:

    Lots of uncertainty in regional inventories

    Need to disaggregate sources to quality-check findings

    Need better project and regional activity data

    (spatial, temporal, fleet mix)

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    Acknowledgments

    The study team thanks the following individuals for

    their assistance:

    Song Bai, U.C. Davis

    Mike Brady, Caltrans

    Jos Luis Cceres, SACOG

    Zhen Dai, California Air Resources Board/UCD

    Gordon Garry, SACOG

    Justin Kable, Port of Oakland/UCD

    Robert OLoughlin, Federal Highway Administration

    Jeff Pulverman, Caltrans Sharon Tang, Caltrans

    Ru Wang, U.C. Davis

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    For Q & A

    Top Five NOx Emitters by Construction Equipment Type

    OFFROAD2007 Caltrans Data

    Rollers Graders Scrapers Excavators Generator Set Crawler Tractors Skid Steer Loaders Rubber Tire Loaders Tractors/Loaders/Backhoes

    Main point: construction activity in modeldoes not characterize road construction per se