Epidemiological derivation of flux-based critical levels for visible ozone injury in European forests
Pierre Sicard , Alessandra De Marco , Elisa Carrari , Laurence Dalstein-Richier , Yasutomo Hoshika , Ovidiu Badea , Diana Pitar , Silvano Fares , Adriano Conte , Ionel Popa , Elena Paoletti
Journal of Forestry Research ›› 2020, Vol. 31 ›› Issue (5) : 1509 -1519.
Epidemiological derivation of flux-based critical levels for visible ozone injury in European forests
The European MOTTLES project set-up a new-generation network for ozone (O3) monitoring in 17 plots in France, Italy and Romania. These monitoring stations allowed: (1) estimating the accumulated exposure AOT40 and stomatal O3 fluxes (PODY) with an hourly threshold of uptake (Y) to represent the detoxification capacity of trees (POD1, with Y = 1 nmol O3 m−2 s−1 per leaf area); and (2) collecting data of forest-response indicators, i.e. crown defoliation and visible foliar O3-like injury over the time period 2017–2019. The soil water content was the most important parameter affecting crown defoliation and was a key factor affecting the severity of visible foliar O3-like injury on the dominant tree species in a plot. The soil water content is thus an essential parameter in the PODY estimation, particularly for water-limited environments. An assessment based on stomatal flux-based standard and on real plant symptoms is more appropriated than the exposure-based method for protecting vegetation. From flux-effect relationships, we derived flux-based critical levels (CLef) for forest protection against visible foliar O3-like injury. We recommend CLef of 5 and 12 mmol m−2 POD1 for broadleaved species and conifers, respectively. Before using PODY as legislative standard in Europe, we recommend using the CLec for ≥ 25% of crown defoliation in a plot: 17,000 and 19,000 nmol mol−1 h AOT40 for conifers and broadleaved species, respectively.
POD / Critical levels / Ozone / Visible injury / Epidemiology
| [1] |
|
| [2] |
|
| [3] |
|
| [4] |
|
| [5] |
|
| [6] |
|
| [7] |
|
| [8] |
|
| [9] |
|
| [10] |
|
| [11] |
|
| [12] |
|
| [13] |
CLRTAP, UNECE Convention on Long-range Transboundary Air Pollution (2017) Mapping critical levels for vegetation”. Chapter III of Manual on methodologies and criteria for modelling and mapping critical loads and levels and air pollution effects, risks and trends. Accessed on 1st May 2020 www.icpmapping.org.lrtap |
| [14] |
|
| [15] |
De Marco A, Sicard P (2019) Why do we still need to derive ozone critical levels for vegetation protection? Opinion paper - IJESNR 21 - October 2019 |
| [16] |
|
| [17] |
|
| [18] |
|
| [19] |
Eichhorn J, Roskams P, Potočić N, Timmermann V, Ferretti M, Mues V et al (2016) Part IV: Visual Assessment of Crown Condition and Damaging Agents. In: UNECE ICP Forests Programme Co-ordinating Centre (ed.): Manual on methods and criteria for harmonized sampling, assessment, monitoring and analysis of the effects of air pollution on forests. Thünen Institute of Forest Ecosystems, Eberswalde, Germany, p 49 |
| [20] |
|
| [21] |
European Council Directive 2008/50/EC of the European Parliament and of the council of 21st May 2008 on ambient air quality and cleaner air for Europe. Official Journal L, 152 (2008), pp 1–44 |
| [22] |
|
| [23] |
|
| [24] |
|
| [25] |
|
| [26] |
|
| [27] |
|
| [28] |
|
| [29] |
|
| [30] |
|
| [31] |
|
| [32] |
|
| [33] |
|
| [34] |
|
| [35] |
|
| [36] |
|
| [37] |
|
| [38] |
|
| [39] |
|
| [40] |
National Emission Ceilings Directive (2016) Directive 2016/2284 of the European Parliament and of the Council of 14 December 2016 on the reduction of national emissions of certain atmospheric pollutants, amending Directive 2003/35/EC and repealing Directive 2001/81/EC. In: EC Official Journal of the European Union L. 344 of 17.12.2016 |
| [41] |
|
| [42] |
|
| [43] |
|
| [44] |
|
| [45] |
|
| [46] |
Schaub M, Calatayud V, Ferretti M, Brunialti G, Lövblad G, Krause G et al. (2010) Monitoring of Ozone Injury. Manual Part X, 22 pp. In: Manual on methods and criteria for harmonized sampling, assessment, monitoring and analysis of the effects of air pollution on forests. UNECE ICP Forests Programme, Hamburg. ISBN: 978-3-926301-03-1 |
| [47] |
Schaub M, Calatayud V, Ferretti M, Brunialti G, Lövblad G, Krause G et al. (2016) Part VIII: monitoring of ozone injury. In: UNECE ICP Forests Programme Coordinating Centre (ed) Manual on methods and criteria for harmonized sampling, assessment, monitoring and analysis of the effects of air pollution on forests. Thünen Institute of Forest Ecosystems, Eberswalde, Germany, 14 pp |
| [48] |
|
| [49] |
|
| [50] |
|
| [51] |
|
| [52] |
|
| [53] |
|
| [54] |
Sicard P, Paoletti E Agathokleous E, Araminienė V, Proietti C, Coulibaly F et al. (2020) Ozone weekend effect in cities: Deep insights for urban air pollution control. Environ Res (in press) |
| [55] |
UNECE, United Nations Economic Commission for Europe (2010) Mapping critical levels for vegetation. Manual on Methodologies and Criteria for Modelling and Mapping Critical Loads & Levels and Air Pollution Effects, Risks and Trends, United Nations Economic Commission for Europe (UNECE) Convention on Long range Transboundary Air Pollution, Geneva, 254 pp |
| [56] |
|
/
| 〈 |
|
〉 |