Distribution of ozone and other air pollutants in forests of the Carpathian Mountains in central Europe

Models of ozone distribution and evaluation of its phytotoxic potential in the forests of the Carpathian Mountains of Central Europe are presented. Ozone (O 3) concentrations were monitored during the 1997–1999 growing seasons in 32 forest sites of the Carpathian Mountains. At all sites (elevation b...

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Veröffentlicht in:Environmental pollution (1987) 2002, Vol.116 (1), p.3-25
Hauptverfasser: Bytnerowicz, A, Godzik, B, Frączek, W, Grodzińska, K, Krywult, M, Badea, O, Barančok, P, Blum, O, Černy, M, Godzik, S, Mankovska, B, Manning, W, Moravčik, P, Musselman, R, Oszlanyi, J, Postelnicu, D, Szdźuj, J, Varšavova, M, Zota, M
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container_end_page 25
container_issue 1
container_start_page 3
container_title Environmental pollution (1987)
container_volume 116
creator Bytnerowicz, A
Godzik, B
Frączek, W
Grodzińska, K
Krywult, M
Badea, O
Barančok, P
Blum, O
Černy, M
Godzik, S
Mankovska, B
Manning, W
Moravčik, P
Musselman, R
Oszlanyi, J
Postelnicu, D
Szdźuj, J
Varšavova, M
Zota, M
description Models of ozone distribution and evaluation of its phytotoxic potential in the forests of the Carpathian Mountains of Central Europe are presented. Ozone (O 3) concentrations were monitored during the 1997–1999 growing seasons in 32 forest sites of the Carpathian Mountains. At all sites (elevation between 450 and 1320 m) concentrations of O 3, nitrogen dioxide (NO 2), and sulfur dioxide (SO 2) were measured with passive samplers. In addition, in two western Carpathian locations, Vychodna and Gubałówka, ozone was continuously monitored with ultraviolet (UV) absorption monitors. Highest average hourly O 3 concentrations in the Vychodna and Gubałówka sites reached 160 and 200 μg/m 3 (82 and 102 ppb), respectively (except for the AOT40 values, ozone concentrations are presented as μg/m 3; and at 25 °C and 760 mm Hg, 1 μg O 3/m 3=0.51 ppb O 3). These sites showed drastically different patterns of diurnal O 3 distribution, one with clearly defined peaks in the afternoon and lowest values in the morning, the other with flat patterns during the entire 24-h period. On two elevational transects, no effect of elevation on O 3 levels was seen on the first one, while on the other a significant increase of O 3 levels with elevation occurred. Concentrations of O 3 determined with passive samplers were significantly different between individual monitoring years, monitoring periods, and geographic location of the monitoring sites. Results of passive sampler monitoring showed that high O 3 concentrations could be expected in many parts of the Carpathian range, especially in its western part, but also in the eastern and southern ranges. More than four-fold denser network of monitoring sites is required for reliable estimates of O 3 distribution in forests over the entire Carpathian range (140 points). Potential phytotoxic effects of O 3 on forest trees and understory vegetation are expected on almost the entire territory of the Carpathian Mountains. This assumption is based on estimates of the AOT40 indices for forest trees and natural vegetation. Concentrations of NO 2 and SO 2 in the entire Carpathian range were typical for this part of Europe and below the expected levels of phytotoxicity.
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Ozone (O 3) concentrations were monitored during the 1997–1999 growing seasons in 32 forest sites of the Carpathian Mountains. At all sites (elevation between 450 and 1320 m) concentrations of O 3, nitrogen dioxide (NO 2), and sulfur dioxide (SO 2) were measured with passive samplers. In addition, in two western Carpathian locations, Vychodna and Gubałówka, ozone was continuously monitored with ultraviolet (UV) absorption monitors. Highest average hourly O 3 concentrations in the Vychodna and Gubałówka sites reached 160 and 200 μg/m 3 (82 and 102 ppb), respectively (except for the AOT40 values, ozone concentrations are presented as μg/m 3; and at 25 °C and 760 mm Hg, 1 μg O 3/m 3=0.51 ppb O 3). These sites showed drastically different patterns of diurnal O 3 distribution, one with clearly defined peaks in the afternoon and lowest values in the morning, the other with flat patterns during the entire 24-h period. On two elevational transects, no effect of elevation on O 3 levels was seen on the first one, while on the other a significant increase of O 3 levels with elevation occurred. Concentrations of O 3 determined with passive samplers were significantly different between individual monitoring years, monitoring periods, and geographic location of the monitoring sites. Results of passive sampler monitoring showed that high O 3 concentrations could be expected in many parts of the Carpathian range, especially in its western part, but also in the eastern and southern ranges. More than four-fold denser network of monitoring sites is required for reliable estimates of O 3 distribution in forests over the entire Carpathian range (140 points). Potential phytotoxic effects of O 3 on forest trees and understory vegetation are expected on almost the entire territory of the Carpathian Mountains. This assumption is based on estimates of the AOT40 indices for forest trees and natural vegetation. 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Ozone (O 3) concentrations were monitored during the 1997–1999 growing seasons in 32 forest sites of the Carpathian Mountains. At all sites (elevation between 450 and 1320 m) concentrations of O 3, nitrogen dioxide (NO 2), and sulfur dioxide (SO 2) were measured with passive samplers. In addition, in two western Carpathian locations, Vychodna and Gubałówka, ozone was continuously monitored with ultraviolet (UV) absorption monitors. Highest average hourly O 3 concentrations in the Vychodna and Gubałówka sites reached 160 and 200 μg/m 3 (82 and 102 ppb), respectively (except for the AOT40 values, ozone concentrations are presented as μg/m 3; and at 25 °C and 760 mm Hg, 1 μg O 3/m 3=0.51 ppb O 3). These sites showed drastically different patterns of diurnal O 3 distribution, one with clearly defined peaks in the afternoon and lowest values in the morning, the other with flat patterns during the entire 24-h period. On two elevational transects, no effect of elevation on O 3 levels was seen on the first one, while on the other a significant increase of O 3 levels with elevation occurred. Concentrations of O 3 determined with passive samplers were significantly different between individual monitoring years, monitoring periods, and geographic location of the monitoring sites. Results of passive sampler monitoring showed that high O 3 concentrations could be expected in many parts of the Carpathian range, especially in its western part, but also in the eastern and southern ranges. More than four-fold denser network of monitoring sites is required for reliable estimates of O 3 distribution in forests over the entire Carpathian range (140 points). Potential phytotoxic effects of O 3 on forest trees and understory vegetation are expected on almost the entire territory of the Carpathian Mountains. This assumption is based on estimates of the AOT40 indices for forest trees and natural vegetation. 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Ozone (O 3) concentrations were monitored during the 1997–1999 growing seasons in 32 forest sites of the Carpathian Mountains. At all sites (elevation between 450 and 1320 m) concentrations of O 3, nitrogen dioxide (NO 2), and sulfur dioxide (SO 2) were measured with passive samplers. In addition, in two western Carpathian locations, Vychodna and Gubałówka, ozone was continuously monitored with ultraviolet (UV) absorption monitors. Highest average hourly O 3 concentrations in the Vychodna and Gubałówka sites reached 160 and 200 μg/m 3 (82 and 102 ppb), respectively (except for the AOT40 values, ozone concentrations are presented as μg/m 3; and at 25 °C and 760 mm Hg, 1 μg O 3/m 3=0.51 ppb O 3). These sites showed drastically different patterns of diurnal O 3 distribution, one with clearly defined peaks in the afternoon and lowest values in the morning, the other with flat patterns during the entire 24-h period. On two elevational transects, no effect of elevation on O 3 levels was seen on the first one, while on the other a significant increase of O 3 levels with elevation occurred. Concentrations of O 3 determined with passive samplers were significantly different between individual monitoring years, monitoring periods, and geographic location of the monitoring sites. Results of passive sampler monitoring showed that high O 3 concentrations could be expected in many parts of the Carpathian range, especially in its western part, but also in the eastern and southern ranges. More than four-fold denser network of monitoring sites is required for reliable estimates of O 3 distribution in forests over the entire Carpathian range (140 points). Potential phytotoxic effects of O 3 on forest trees and understory vegetation are expected on almost the entire territory of the Carpathian Mountains. This assumption is based on estimates of the AOT40 indices for forest trees and natural vegetation. Concentrations of NO 2 and SO 2 in the entire Carpathian range were typical for this part of Europe and below the expected levels of phytotoxicity.</abstract><cop>Oxford</cop><pub>Elsevier Ltd</pub><pmid>11808553</pmid><doi>10.1016/S0269-7491(01)00187-7</doi><tpages>23</tpages></addata></record>
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identifier ISSN: 0269-7491
ispartof Environmental pollution (1987), 2002, Vol.116 (1), p.3-25
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subjects Air Pollutants - analysis
Animal, plant and microbial ecology
Applied ecology
Applied sciences
Atmospheric pollution
Biological and medical sciences
Ecotoxicology, biological effects of pollution
Effects of pollution and side effects of pesticides on plants and fungi
Environmental Monitoring
Europe
Exact sciences and technology
Fundamental and applied biological sciences. Psychology
Geography
Geostatistical models
Landscape
Nitrogen dioxide
Oxidants, Photochemical - analysis
Ozone
Ozone - analysis
Plants
Pollution
Pollution sources. Measurement results
Sulfur dioxide
Trees
title Distribution of ozone and other air pollutants in forests of the Carpathian Mountains in central Europe
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