Atmospheric pollutant effects on Mediterranean ecosystems in … · 2019. 11. 29. · Atmospheric...

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Atmospheric pollutant effects on Mediterranean ecosystems in Spain PARTICULARITIES FOR RISK ASSESSMENT EMEP – WGE 5 th Joint session Héctor García-Gómez, Rocío Alonso, Victoria Bermejo, Susana Elvira, Isaura Rábago, Javier Sanz, Raquel Ruiz, Ignacio González-Fernández Geneva, 9-13 th Sept. 2019

Transcript of Atmospheric pollutant effects on Mediterranean ecosystems in … · 2019. 11. 29. · Atmospheric...

Page 1: Atmospheric pollutant effects on Mediterranean ecosystems in … · 2019. 11. 29. · Atmospheric pollutant effects on Mediterranean ecosystems in Spain PARTICULARITIES FOR RISK ASSESSMENT

Atmospheric pollutant effects

on Mediterranean ecosystems in SpainPARTICULARITIES FOR RISK ASSESSMENT

EMEP – WGE 5th Joint session

Héctor García-Gómez, Rocío Alonso, Victoria Bermejo, Susana Elvira, Isaura Rábago, Javier Sanz, Raquel Ruiz, Ignacio González-Fernández

Geneva, 9-13th Sept. 2019

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Spanish participation in scientific ICP/TFs

Contributionfrom Spain

5th EMEP/WGE Joint session, 2019

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Spanish participation in scientific ICP/TFs

Contributionfrom Spain

5th EMEP/WGE Joint session, 2019

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Risk assessment in Mediterranean region

Tropospheric ozone (O3)

Eutrophication (N deposition)

AOT40 forests (Apr-Sept) 2013

ppb h

≤ 5000

5000 - 10000

10000 - 15000

15000 - 25000

> 25000

Large risk for vegetation Low to moderate risk

5th EMEP/WGE Joint session, 2019

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Risk assessment in Mediterranean region

Major scientific concerns

5th EMEP/WGE Joint session, 2019

Risk assessment methodologies within the Air Convention should

represent adequately Mediterranean

ecosystems and crops:

1. Sensitivity of Mediterranean ecosystems,

species and cultivars (CLO3 and CLN)

2. Deposition of pollutants

(POD and N deposition)

3. Mediterranean climate (drought, climate change context)

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Risk assessment - Tropospheric ozone

Risk assessment methodologies within the Air Convention should

represent adequately Mediterranean

ecosystems and crops:

1. Sensitivity of Mediterranean ecosystems,

species and cultivars (CLO3 and CLN)

2. Deposition of pollutants

(POD and N deposition)

3. Mediterranean climate (drought, climate change framework)

Major scientific concerns

5th EMEP/WGE Joint session, 2019

O3

do

se (

PO

D0)

Without soil moisture factorWith soil moisture factor

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Risk assessment - Tropospheric ozone

Manual on methodologies and criteria for modelling and

mapping critical loads and levels, and air pollution effects, risks and trends

(Mapping Manual – Ch. 3)

Chapter 3

Same methodology…

but some critical differences.

PAWSWP

Vol. Soil Moisture

Undefined depth

Sp.-specific parametrization

SMI3

(from ECMWF)

Depth 28-72 cm(50cm-centered)

Generic parametrization

5th EMEP/WGE Joint session, 2019

Modelling soil moisture effect on POD

GOAL: Improving O3 dose modelling in water-limited areas of Europe

Soil moisture collaborative exercise – ICP-Veg + EMEP MSC-W

O3 risk assessment based on the phytotoxic ozone dose (PODy)

Workplan item 1.4.2

Model DO3SE (Deposition of Ozone and Stomatal Exchange)

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Risk assessment - Tropospheric ozone

Participants: ICP Vegetation – ICP Forest – EMEP MSC-W Collaboration of experts from Spain (leading), Italy, Sweden, Switzerland and UK

Coverage: Long-term field data on soil moisture fromWater-limited areas: Italy and SpainParallel exercises: Switzerland and Sweden

Stages:1 Soil moisture estimation

1.1 Evaluation of modeled SMI1.2 Sensitivity analysis

2 Parametrization of fSWC

3 Mapping PODy

Soil moisture exercise ICP-Veg + EMEP MSC-W

5th EMEP/WGE Joint session, 2019

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Wetter yearsDrier years

Autumn + WinterSpring + Summer

Risk assessment - Tropospheric ozone

1.1 Evaluation of modeled SMI by comparison with field data

Spanish case study (2010 – 2015)

Intra-annual analysisInter-annual analysis

5th EMEP/WGE Joint session, 2019

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Risk assessment - N deposition

Dry deposition importance in low-precipitation areas

Up to 65% in Eastern-Spain pine forests (Sanz et al., 2002)56-81% of in Quercus ilex forests (Àvila et al., 2017; García-Gómez et al., 2018)

Dry deposition and seasonality

First rains of autumn → ephemeral inputs of N into the soil coming from the dry deposition accumulated over the summer → lixiviation of N (García-Gómez et al., 2016)

Modelled dry deposition

Potential infra-estimation; lack of esclerophylous evergreen vegetation

5th EMEP/WGE Joint session, 2019

More information (summary):ICP Forests 2018 Executive report

0

5

10

15

20

25 EIM + DO3SEEMEP model

PERI-URBAN FORESTS RURALFOREST

Dry

de

po

siti

on

(kg

N h

a-1

y-1)

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Initial steps → Gathering experts

Dry deposition (different approximations)Canopy uptake and in-canopy processesMediterranean seasonality

What can be done?

Sharing knowledge and expertise to improve methodology and applicationWorking on reducing uncertaintiesComparison among approximation and with EMEP model values

… any other proposals of collaboration

http://icp-forests.net/group/dry-deposition

Discussion group on dry deposition and canopyuptake of nutrients (mainly N).Data: Level II; research results; bibliographic reviewParticipation: Ask for Group Membership.

Dry Deposition Group (ICP Forests)

Risk assessment - N deposition

5th EMEP/WGE Joint session, 2019

Closer collaboration with EMEP experts?

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Uncertainty on dry deposition modelling and field estimation

Uncertainty on how seasonality can affect modellled CLeutN calculations (SMB)

Risk assessment - N deposition

5th EMEP/WGE Joint session, 2019

Lack of data from N addition studies and/or gradientstudies on major habitat types of the Mediterraneanregion.

+Uncertainty in empirical empirical CL (CLemp) for Mediterranean habitats

CIEMAT group is starting contacts with different research groups to collect relevant information for CLemp.

+

Workplan item 1.1.1.14Validation and revision of

empirical critical loads

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Spanish contribution to scientific ICP/TFs

Gracias

Thank you

Merci

Acknowledgements:

EDEN-MED (CGL2017-84687-C2-1-R) MINECO-FEDER

Comunidad de Madrid (Spain) and Structural Funds

2014-2020 (ERDF and ESF) for the financial support

(project AGRISOST-CM S2018/BAA-4330)

Cargas y Niveles Críticos, MITECO

5th EMEP/WGE Joint session, 2019

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20 kg N ha-1 y-1

10 kg N ha-1 y-1

-20

-15

-10

-5

0

5

10

15

2 3 4 5 6 7

D¡f

fere

nce

wit

h E

IM+D

O3

SE (

kg h

a-1

y-1)

LAI

IM

EMEP

CBM

EMEP

mo

de

l –EI

M+D

O3

SE m

od

el

Dry

de

po

siti

on

(

kg N

ha

-1y-1

)

LAI

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Risk assessment - Tropospheric ozone

WITH SOIL MOISTURE

WITHOUT SOIL MOISTURE

Manual on methodologies and criteria for modelling and mapping critical loads and levels, and air pollution effects, risks and trends (Mapping Manual):

Methodology for O3 risk assessment → Estimation of phytotoxic O3 dose (POD)

Model DO3SE (Deposition of Ozone and Stomatal Exchange)

gs = gmax × flight × max { fmin , ( ftemp × fVPD × fSWP × fphen ) }

GOAL: Improving O3 dose modelling in water-limited areas of Europe

Soil moisture collaborative exercise – ICP-Veg + EMEP MSC-W

Soil moisture

O3

do

se (

PO

D)

5th EMEP/WGE Joint session, 2019