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Variations of tree ring width and chemical composition of wood of pine growing in the area nearby chemical factories

Barbara Sensuła

Barbara Sensuła

Silesian University of Technology, Institute of Physics – Center for Science and EducationGliwice, Poland
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Sensuła, Barbara
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Sławomir Wilczyński

Sławomir Wilczyński

Department of Forest Protection, Entomology and Forest Climatology, University of Agriculture in KrakowKraków, Poland
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Wilczyński, Sławomir
, 
Laurence Monin

Laurence Monin

Musée Royal de l’Afrique centrale, Département Sciences de la Terre, Laboratoire de GéochimieTervuren, Belgium
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Monin, Laurence
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Mohammed Allan

Mohammed Allan

Université de Liège, Département de Géologie, UR AGEs - Argiles, Géochimie et Environnements sédimentaires, Quartier AgoraLiege (Sart Tilman), France
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Allan, Mohammed
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Anna Pazdur

Anna Pazdur

Silesian University of Technology, Institute of Physics – Center for Science and EducationGliwice, Poland
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Pazdur, Anna
 y 
Nathalie Fagel

Nathalie Fagel

Université de Liège, Département de Géologie, UR AGEs - Argiles, Géochimie et Environnements sédimentaires, Quartier AgoraLiege (Sart Tilman), France
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Fagel, Nathalie
  
04 nov 2017
Variations of tree ring width and chemical composition of wood of pine growing in the area nearby chemical factories's Cover Image
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Categoría del artículo: Conference Proceedings of the 12International Conference “Methods of Absolute Chronology” May 11-13, 2016, Gliwice-Paniówki, Poland
Publicado en línea: 04 nov 2017
Páginas: 226 - 239
Recibido: 14 may 2016
Aceptado: 28 mar 2017
DOI: https://doi.org/10.1515/geochr-2015-0064
Palabras clave
© 2017 B. Sensuła.
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 3.0 License.

Fig. 1

National level of carbon emissions from the 1850–2011 period (the emission estimates are expressed in thousand metric tons of carbon, per capita emission estimates are expressed in metric tons of carbon)
National level of carbon emissions from the 1850–2011 period (the emission estimates are expressed in thousand metric tons of carbon, per capita emission estimates are expressed in metric tons of carbon)

Fig. 2

Sampling sites (A, B, C, N, S, T) in the vicinity ot the nitrogen factory: Grupa Azoty ZAK (ZAK) and chemical factory Blachownia Holding s.a (Blachownia) in the southern part of Poland; and dominant wind direction.
Sampling sites (A, B, C, N, S, T) in the vicinity ot the nitrogen factory: Grupa Azoty ZAK (ZAK) and chemical factory Blachownia Holding s.a (Blachownia) in the southern part of Poland; and dominant wind direction.

Fig. 3

Site tree-ring width chronologies (lines), site indexed chronologies (grey area), and negative exponential fit curves. In the bracket there is a reduction period of time.
Site tree-ring width chronologies (lines), site indexed chronologies (grey area), and negative exponential fit curves. In the bracket there is a reduction period of time.

Fig. 4

Decrease of the level of air pollution (PM, SO2, NOx and CO) in Opole voivodship (R-right axes) and increase of trees indexed chronologies since 1970s (L-left axes). Sampling sites: A, B, C, N, S, T.
Decrease of the level of air pollution (PM, SO2, NOx and CO) in Opole voivodship (R-right axes) and increase of trees indexed chronologies since 1970s (L-left axes). Sampling sites: A, B, C, N, S, T.

Fig. 5

The dendrogram of site indexed chronologies. Sampling sites: A, B, C, N, S, T.
The dendrogram of site indexed chronologies. Sampling sites: A, B, C, N, S, T.

Fig. 6

The number of partial population which occurred site pointer years.
The number of partial population which occurred site pointer years.

Fig. 7

Comparison of trace elements component (Na, Mg, Fe, Ni, Cu, Zn, Pb) in two wood profiles and total wet deposition or concentration in the rain of these elements.
Comparison of trace elements component (Na, Mg, Fe, Ni, Cu, Zn, Pb) in two wood profiles and total wet deposition or concentration in the rain of these elements.

Fig. 8

Radial variations (grey area) of element concentrations (Na, Mg, Fe, Ni, Cu, Zn, Pb) in pine wood from area nearby chemical factories.
Radial variations (grey area) of element concentrations (Na, Mg, Fe, Ni, Cu, Zn, Pb) in pine wood from area nearby chemical factories.

Selected dendrochronological statistics_ MTRW (mean tree-ring width), MRI (mean relative radial increment), and MCI (mean change of index) were calculated for 3 periods: (a) before reduction, (b) during reduction, (c) during recovery; rbt – the mean between-tree series correlation, EPS – the expressed population signal is a statistic for examining the common variability in chronology; rbt and EPS were calculated for 2 periods of time: (d) 1940–2012 (total common period, n=73) and (e) 1962–1989 (common reduction period, n=28)

SiteMTRW (mm)MRI (%)MCIrbtEPS
a / b / ca / b / ca / b / cd / ed / e
A3.91 / 1.50 / 0.37100 / 61 / 1380.24 / 0.13 / 0.260.417 / 0.3610.935 / 0.918
B2.77 / 0.93 / 1.61100 / 56 / 1640.16 / 0.14 / 0.310.532 / 0.4210.958 / 0.935
C1.92 / 0.69 / 1.3697 / 53 / 1830.18 / 0.13 / 0.440.499 / 0.3550.952 / 0.916
N2.41 / 1.31 / 1.4398 / 78 / 1320.17 / 0.15 / 0.270.397 / 0.3190.930 / 0.903
S1.61 / 1.40 / 1.5297 / 94 / 1190.17 / 0.19 / 0.220.436 / 0.4240.939 / 0.937
T3.02 / 0.91 / 1.3698 / 58 / 1880.18 / 0.13 / 0.420.497 / 0.3710.952 / 0.921

Sampling site – geographical coordinates, elevation and forest type (FMB – fresh mixed broadleaved forest)_

Site codeLat. N; Lon. EElevation (m)Forest site type
A50°19’; 18°15’192FMB
B50°20’; 18°18’209FMB
C50°20’; 18°19’218FMB
N50°22’; 18°23’218FMB
S50°18’; 18°20’215FMB
T50°18’; 18°17’207FMB
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