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  • 8/6/2019 NOx Impact on Air Quality, Human Health and Ecosystems in TIER II III Ship Emission Scenarios for Baltic Sea

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    NOx impact on Air Quality,

    Human Health and EcosystemsinTIER II / III Ship Emission

    Scenarios for Baltic Sea

    J.Soares, M. Sofiev, J.-P.Jalkanen

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    Outlook

    Introduction

    Goal of the study

    Methodology of the analysis Main outcome

    Summary

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    Goal of the study

    Goal: to evaluate the impact of NOx ship emissionreduction measures in the Baltic Sea Area

    Health impact: NOx concentrations

    Health impact: NOx exposure

    Ecosystem impact: NOx deposition

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    Methodology: input data and modelling tool

    A modelling study analysing three main emissionscenarious:

    3 emission scenarios:

    current emissions (2007)

    NOx, SOx, CO & NH3

    Anthropogenic in-land and ship traffic

    Tier II: 10% NOx reduction of 2045 ship emission in the BSA, the reststays the same

    Tier III: 80% NOx reduction of 2045 ship emission in the BSA, the rest

    stays the same

    Working tool: SILAM dispersion model with embedded

    inorganic chemistry scheme

    Model output: concentrations & depositions over Europe(20km grid size)

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    Methodology: processing the model output

    Aggregation of the concentration and deposition maps

    Lower and upper percentiles for all species

    Directive 2008/50/EC: 200 g/m3 for 1 hour-average should not be

    exceeded more than 18 times a calendar year: 99.8%

    Ratios, absolute and relative differences in concentrations and

    depositions between the three emission cases

    Average over the computed period

    Exposure estimation: E = n * t * C [gs/m3]

    n = the number of people (source: Gridded Population of

    the World, http://sedac.ciesin.columbia.edu/gpw.)

    t = time [s]

    C = concentration [g/m3] (source: SILAM)

    http://sedac.ciesin.columbia.edu/gpwhttp://sedac.ciesin.columbia.edu/gpw
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    Tool: Chemical Transport Model SILAM

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    Model simulations outcome: air quality

    impact

    Tier II/Tier III , NO2 cnc ave June-

    August(gN/m3)

    0

    0,2

    0,4

    0,6

    0,8

    1

    1,2

    currentemissions TIER II TIER III

    NO2concentra

    tions[g/m3)

    NO2annualaverageconcentrationovertheBSA

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    Model simulations outcome: ecosystemsimpact

    Tier II/Tier III, NTotal annual ave dep (gN/m2.h)

    0

    2

    4

    6

    8

    10

    12

    currentemissions TIER II TIER III

    NO2deposition[g/m2.h

    )

    NTotalannualaveragedepositionovertheBSA

    Tier II / Tier III deposition, average whole period

    NTotal N-SIA,

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    0

    10

    20

    30

    40

    50

    60

    TIER II TIER III

    NO2

    exposure(gs/m3)

    NO2annualaverageexposureovertheBSA

    Exposure: Tier II vs Tier III

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    Summary of modelling results

    NOx emission by 2045 if the traffic doubles :Tier II - 80% increase, Tier III - 60% reduction.Tier II III impact:

    2-3 times decrease of NOx concentrations over the sea area

    Minor impact over land

    Moderate impact on deposition (tens of %)

    Substantial impact on chemical processes over sea: growth of zero-ammonium nitrate area

    Reduction of N-SIA production, down to zero over central part of BalticProper

    NOx near coastal areas are and will be dominated by theautomobile traffic and energy sector emission

    Current NO2 limit values stated in the EU Legislation are not and willnot be exceeded in the Baltic Sea area (at regional scale)

    Vegetation: 30 g/m3 at annual level

    Human health: 200 g/m3, 99.8th percentile

    Human health: 40 g/m3 at annual level

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    Summary of exposure estimates

    Estimated using the in-land population map and SILAMcomputed concentrations

    People at the ferries are ignored

    Main changes in NO2 concentrations are over sea area rather than

    inland

    Harbour emission is largely missing in the present EMEP

    ship emission

    These two factors resulted in limited difference between

    the exposure estimates within Tier II and Tier III

    Estimates made for NO2 show some 10%-15% difference