The European MOTTLES project set-up a newgeneration network for ozone(O 3)monitoring in 17 plots in France,Italy and Romania.These monitoring stations allowed:(1)estimating the accumulated exposure AOT40 and stomatal ...The European MOTTLES project set-up a newgeneration network for ozone(O 3)monitoring in 17 plots in France,Italy and Romania.These monitoring stations allowed:(1)estimating the accumulated exposure AOT40 and stomatal O 3 fl uxes(PODY)with an hourly threshold of uptake(Y)to represent the detoxifi cation capacity of trees(POD1,with Y=1 nmol O 3 m^−2 s^−1 per leaf area);and(2)collecting data of forest-response indicators,i.e.crown defoliation and visible foliar O 3-like injury over the time period 2017–2019.The soil water content was the most important parameter aff ecting crown defoliation and was a key factor aff ecting the severity of visible foliar O 3-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 fl ux-based standard and on real plant symptoms is more appropriated than the exposure-based method for protecting vegetation.From fl ux-eff ect relationships,we derived fl ux-based critical levels(CLef)for forest protection against visible foliar O 3-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.展开更多
Correction to:J.For.Res.https://doi.org/10.1007/s11676-020-01191-x In the Original publication of the article,the authors found an error in the text“We recommend CLef of 5 and 12 mmol m−2 POD1 for broadleaved species...Correction to:J.For.Res.https://doi.org/10.1007/s11676-020-01191-x In the Original publication of the article,the authors found an error in the text“We recommend CLef of 5 and 12 mmol m−2 POD1 for broadleaved species and conifers,respectively”under the section abstract and conclusion.展开更多
基金This work was supported by the LIFE fi nancial instrument of the European Union in the framework of the MOTTLES project“Monitoring ozone injury for setting new critical levels”(LIFE15 ENV/IT/000183).
文摘The European MOTTLES project set-up a newgeneration network for ozone(O 3)monitoring in 17 plots in France,Italy and Romania.These monitoring stations allowed:(1)estimating the accumulated exposure AOT40 and stomatal O 3 fl uxes(PODY)with an hourly threshold of uptake(Y)to represent the detoxifi cation capacity of trees(POD1,with Y=1 nmol O 3 m^−2 s^−1 per leaf area);and(2)collecting data of forest-response indicators,i.e.crown defoliation and visible foliar O 3-like injury over the time period 2017–2019.The soil water content was the most important parameter aff ecting crown defoliation and was a key factor aff ecting the severity of visible foliar O 3-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 fl ux-based standard and on real plant symptoms is more appropriated than the exposure-based method for protecting vegetation.From fl ux-eff ect relationships,we derived fl ux-based critical levels(CLef)for forest protection against visible foliar O 3-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.
文摘Correction to:J.For.Res.https://doi.org/10.1007/s11676-020-01191-x In the Original publication of the article,the authors found an error in the text“We recommend CLef of 5 and 12 mmol m−2 POD1 for broadleaved species and conifers,respectively”under the section abstract and conclusion.
