Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution

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Standard

Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution. / Klumpp, A.; Ansel, W.; Klumpp, G.; Vergne, P.; Sifakis, N.; Sanz, M.J.; Rasmussen, S.; Ro-Poulsen, Helge; Ribas, A.; Penuelas, J.; Kambezidis, H.; He, S.; Garrec, J.P.; Calatayud, V.

I: Atmospheric Environment, Bind 40, Nr. 38, 2006, s. 7437-7448.

Publikation: Bidrag til tidsskriftTidsskriftartikelForskningfagfællebedømt

Harvard

Klumpp, A, Ansel, W, Klumpp, G, Vergne, P, Sifakis, N, Sanz, MJ, Rasmussen, S, Ro-Poulsen, H, Ribas, A, Penuelas, J, Kambezidis, H, He, S, Garrec, JP & Calatayud, V 2006, 'Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution', Atmospheric Environment, bind 40, nr. 38, s. 7437-7448. https://doi.org/10.1016/j.atmosenv.2006.07.001

APA

Klumpp, A., Ansel, W., Klumpp, G., Vergne, P., Sifakis, N., Sanz, M. J., Rasmussen, S., Ro-Poulsen, H., Ribas, A., Penuelas, J., Kambezidis, H., He, S., Garrec, J. P., & Calatayud, V. (2006). Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution. Atmospheric Environment, 40(38), 7437-7448. https://doi.org/10.1016/j.atmosenv.2006.07.001

Vancouver

Klumpp A, Ansel W, Klumpp G, Vergne P, Sifakis N, Sanz MJ o.a. Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution. Atmospheric Environment. 2006;40(38):7437-7448. https://doi.org/10.1016/j.atmosenv.2006.07.001

Author

Klumpp, A. ; Ansel, W. ; Klumpp, G. ; Vergne, P. ; Sifakis, N. ; Sanz, M.J. ; Rasmussen, S. ; Ro-Poulsen, Helge ; Ribas, A. ; Penuelas, J. ; Kambezidis, H. ; He, S. ; Garrec, J.P. ; Calatayud, V. / Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution. I: Atmospheric Environment. 2006 ; Bind 40, Nr. 38. s. 7437-7448.

Bibtex

@article{3b16bfe06c3711dcbee902004c4f4f50,
title = "Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution",
abstract = "Within the scope of a biomonitoring study conducted in twelve urban agglomerations in eight European countries, the ozone-sensitive bioindicator plant Nicotiana tabacum cv. Bel-W3 was employed in order to assess the occurrence of phytotoxic ozone effects at urban, suburban, rural and traffic-exposed sites. The tobacco plants were exposed to ambient air for biweekly periods at up to 100 biomonitoring sites from 2000 to 2002. Special emphasis was placed upon methodological standardisation of plant cultivation, field exposure and injury assessment. Ozone-induced leaf injury showed a clearly increasing gradient from northern and northwestern Europe to central and southern European locations. The strongest ozone impact occurred at the exposure sites in Lyon and Barcelona, while in Edinburgh, Sheffield, Copenhagen and D{\"u}sseldorf only weak to moderate ozone effects were registered. Between-site differences within local networks were relatively small, but seasonal and inter-annual differences were strong due to the variability of meteorological conditions and related ozone concentrations.The 2001 data revealed a significant relationship between foliar injury degree and various descriptors of ozone pollution such as mean value, AOT20 and AOT40. Examining individual sites of the local monitoring networks separately, however, yielded noticeable differences. Some sites showed no association between ozone pollution and ozone-induced effects, whereas others featured almost linear relationships. This is because the actual ozone flux into the leaf, which is modified by various environmental factors, rather than ambient ozone concentration determines the effects on plants. The advantage of sensitive bioindicators like tobacco Bel-W3 is that the impact of the effectively absorbed ozone dose can directly be measured.",
author = "A. Klumpp and W. Ansel and G. Klumpp and P. Vergne and N. Sifakis and M.J. Sanz and S. Rasmussen and Helge Ro-Poulsen and A. Ribas and J. Penuelas and H. Kambezidis and S. He and J.P. Garrec and V. Calatayud",
note = "Keywords: Air quality; Bioindicators; Tobacco Bel-W3; AOT40; Urban air pollution",
year = "2006",
doi = "10.1016/j.atmosenv.2006.07.001",
language = "English",
volume = "40",
pages = "7437--7448",
journal = "Atmospheric Environment",
issn = "1352-2310",
publisher = "Pergamon Press",
number = "38",

}

RIS

TY - JOUR

T1 - Ozone pollution and ozone biomonitoring in European cities Part II. Ozone-induced plant injury and its relationship with descriptors of ozone pollution

AU - Klumpp, A.

AU - Ansel, W.

AU - Klumpp, G.

AU - Vergne, P.

AU - Sifakis, N.

AU - Sanz, M.J.

AU - Rasmussen, S.

AU - Ro-Poulsen, Helge

AU - Ribas, A.

AU - Penuelas, J.

AU - Kambezidis, H.

AU - He, S.

AU - Garrec, J.P.

AU - Calatayud, V.

N1 - Keywords: Air quality; Bioindicators; Tobacco Bel-W3; AOT40; Urban air pollution

PY - 2006

Y1 - 2006

N2 - Within the scope of a biomonitoring study conducted in twelve urban agglomerations in eight European countries, the ozone-sensitive bioindicator plant Nicotiana tabacum cv. Bel-W3 was employed in order to assess the occurrence of phytotoxic ozone effects at urban, suburban, rural and traffic-exposed sites. The tobacco plants were exposed to ambient air for biweekly periods at up to 100 biomonitoring sites from 2000 to 2002. Special emphasis was placed upon methodological standardisation of plant cultivation, field exposure and injury assessment. Ozone-induced leaf injury showed a clearly increasing gradient from northern and northwestern Europe to central and southern European locations. The strongest ozone impact occurred at the exposure sites in Lyon and Barcelona, while in Edinburgh, Sheffield, Copenhagen and Düsseldorf only weak to moderate ozone effects were registered. Between-site differences within local networks were relatively small, but seasonal and inter-annual differences were strong due to the variability of meteorological conditions and related ozone concentrations.The 2001 data revealed a significant relationship between foliar injury degree and various descriptors of ozone pollution such as mean value, AOT20 and AOT40. Examining individual sites of the local monitoring networks separately, however, yielded noticeable differences. Some sites showed no association between ozone pollution and ozone-induced effects, whereas others featured almost linear relationships. This is because the actual ozone flux into the leaf, which is modified by various environmental factors, rather than ambient ozone concentration determines the effects on plants. The advantage of sensitive bioindicators like tobacco Bel-W3 is that the impact of the effectively absorbed ozone dose can directly be measured.

AB - Within the scope of a biomonitoring study conducted in twelve urban agglomerations in eight European countries, the ozone-sensitive bioindicator plant Nicotiana tabacum cv. Bel-W3 was employed in order to assess the occurrence of phytotoxic ozone effects at urban, suburban, rural and traffic-exposed sites. The tobacco plants were exposed to ambient air for biweekly periods at up to 100 biomonitoring sites from 2000 to 2002. Special emphasis was placed upon methodological standardisation of plant cultivation, field exposure and injury assessment. Ozone-induced leaf injury showed a clearly increasing gradient from northern and northwestern Europe to central and southern European locations. The strongest ozone impact occurred at the exposure sites in Lyon and Barcelona, while in Edinburgh, Sheffield, Copenhagen and Düsseldorf only weak to moderate ozone effects were registered. Between-site differences within local networks were relatively small, but seasonal and inter-annual differences were strong due to the variability of meteorological conditions and related ozone concentrations.The 2001 data revealed a significant relationship between foliar injury degree and various descriptors of ozone pollution such as mean value, AOT20 and AOT40. Examining individual sites of the local monitoring networks separately, however, yielded noticeable differences. Some sites showed no association between ozone pollution and ozone-induced effects, whereas others featured almost linear relationships. This is because the actual ozone flux into the leaf, which is modified by various environmental factors, rather than ambient ozone concentration determines the effects on plants. The advantage of sensitive bioindicators like tobacco Bel-W3 is that the impact of the effectively absorbed ozone dose can directly be measured.

U2 - 10.1016/j.atmosenv.2006.07.001

DO - 10.1016/j.atmosenv.2006.07.001

M3 - Journal article

VL - 40

SP - 7437

EP - 7448

JO - Atmospheric Environment

JF - Atmospheric Environment

SN - 1352-2310

IS - 38

ER -

ID: 1098556