CheneBelgiqueV1, PascalFrancis, Corpus, bibRecord, 000131

Effects of liming on forest soil algal communities

Identifieur interne : 000131 ( PascalFrancis/Corpus ); précédent : 000130; suivant : 000132

Effects of liming on forest soil algal communities

Auteurs : Igor Kostikov ; Monique Carnol ; Jean-Francois Duliere ; Lucien Hoffmann

Source :

Archiv für Hydrobiologie. Supplementband, Algological studies [ 0342-1120 ] ; 2001.

RBID : Pascal:01-0434787

Descripteurs français

Pascal (Inist)
- Chaulage, Groupement végétal, pH, Facteur édaphique, Cation échangeable, Diversité espèces, Biodisponibilité, Nutriment, Algae, Quercus petraea, Picea abies, Dolomite, Chaux, Sol brun acide, Haute Ardenne.

English descriptors

KwdEn :
- Algae, Bioavailability, Brown acid soil, Dolomite, Edaphic factor, Exchangeable cation, Lime, Liming amendment, Nutrient, Picea abies, Plant community, Quercus petraea, Species diversity, pH.

Abstract

The effects of the application of dolomite lime (5 t ha^-1) on soil algal communities were investigated in sessile oak (Quercus petraea (MATT.) LIEB.) and Norway spruce (Picea abies (L.) KARST.) plots situated in the Belgian Ardenne. Chlorophyta (60 taxa) were by far the most diverse group, followed by Xanthophyceae (10 taxa), Bacillariophyceae (3 taxa), Cyanophyceae (2 taxa) and Euglenophyceae (1 taxon). In both forest types, liming lead to a significant increase in soil pH, exchangeable magnesium and calcium. In the limed Quercus plots available phosphorus and soil solution nitrate concentrations were also increased. The soil algal diversity was similar in oak and spruce control plots and in limed spruce plots. However, in the limed oak plots a significantly higher algal diversity was observed. On the basis of a CCA analysis, three clusters of plots could be distinguished: a) Picea control plots, b) limed Picea and control Quercus plots, c) limed Quercus plots. Both soil pH and nutrient availability seem to be important in determining algal species composition in these forest soils.

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

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A03		`1`		`@0 Arch. Hydrobiol. Suppl.bd., Algol. stud.`
A05				`@2 138`
A08	`01`	`1`	`ENG`	`@1 Effects of liming on forest soil algal communities`
A11	`01`	`1`		`@1 KOSTIKOV (Igor)`
A11	`02`	`1`		`@1 CARNOL (Monique)`
A11	`03`	`1`		`@1 DULIERE (Jean-Francois)`
A11	`04`	`1`		`@1 HOFFMANN (Lucien)`
A14	`01`			`@1 Taras Sevcenko Kiev National University @2 Kiev @3 UKR @Z 1 aut.`
A14	`02`			`@1 University of Liège, Institute of Botany, Sart Tilman @2 Liège @3 BEL @Z 2 aut. @Z 4 aut.`
A14	`03`			`@1 University Mons-Hainaut, Faculté des Sciences-Biologie végétale @2 Mons @3 BEL @Z 3 aut.`
A20				`@1 161-178`
A21				`@1 2001`
A23	`01`			`@0 ENG`
A43	`01`			`@1 INIST @2 7491B @5 354000096096120110`
A44				`@0 0000 @1 © 2001 INIST-CNRS. All rights reserved.`
A45				`@0 2 p.1/4`
A47	`01`	`1`		`@0 01-0434787`
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A61				`@0 A`
A64	`01`	`1`		`@0 Archiv für Hydrobiologie. Supplementband, Algological studies`
A66	`01`			`@0 DEU`
C01	`01`		`ENG`	@0 The effects of the application of dolomite lime (5 t ha^-1) on soil algal communities were investigated in sessile oak (Quercus petraea (MATT.) LIEB.) and Norway spruce (Picea abies (L.) KARST.) plots situated in the Belgian Ardenne. Chlorophyta (60 taxa) were by far the most diverse group, followed by Xanthophyceae (10 taxa), Bacillariophyceae (3 taxa), Cyanophyceae (2 taxa) and Euglenophyceae (1 taxon). In both forest types, liming lead to a significant increase in soil pH, exchangeable magnesium and calcium. In the limed Quercus plots available phosphorus and soil solution nitrate concentrations were also increased. The soil algal diversity was similar in oak and spruce control plots and in limed spruce plots. However, in the limed oak plots a significantly higher algal diversity was observed. On the basis of a CCA analysis, three clusters of plots could be distinguished: a) Picea control plots, b) limed Picea and control Quercus plots, c) limed Quercus plots. Both soil pH and nutrient availability seem to be important in determining algal species composition in these forest soils.
C02	`01`	`X`		`@0 002A14B04B`
C02	`02`	`X`		`@0 002A33A02`
C03	`01`	`X`	`FRE`	`@0 Chaulage @5 01`
C03	`01`	`X`	`ENG`	`@0 Liming amendment @5 01`
C03	`01`	`X`	`SPA`	`@0 Encalado @5 01`
C03	`02`	`X`	`FRE`	`@0 Groupement végétal @5 02`
C03	`02`	`X`	`ENG`	`@0 Plant community @5 02`
C03	`02`	`X`	`SPA`	`@0 Comunidad vegetal @5 02`
C03	`03`	`X`	`FRE`	`@0 pH @5 03`
C03	`03`	`X`	`ENG`	`@0 pH @5 03`
C03	`03`	`X`	`SPA`	`@0 pH @5 03`
C03	`04`	`X`	`FRE`	`@0 Facteur édaphique @5 04`
C03	`04`	`X`	`ENG`	`@0 Edaphic factor @5 04`
C03	`04`	`X`	`SPA`	`@0 Factor edáfico @5 04`
C03	`05`	`X`	`FRE`	`@0 Cation échangeable @5 05`
C03	`05`	`X`	`ENG`	`@0 Exchangeable cation @5 05`
C03	`05`	`X`	`SPA`	`@0 Catión intercambiable @5 05`
C03	`06`	`X`	`FRE`	`@0 Diversité espèces @5 06`
C03	`06`	`X`	`ENG`	`@0 Species diversity @5 06`
C03	`06`	`X`	`SPA`	`@0 Diversidad especies @5 06`
C03	`07`	`X`	`FRE`	`@0 Biodisponibilité @5 07`
C03	`07`	`X`	`ENG`	`@0 Bioavailability @5 07`
C03	`07`	`X`	`SPA`	`@0 Biodisponibilidad @5 07`
C03	`08`	`X`	`FRE`	`@0 Nutriment @5 08`
C03	`08`	`X`	`ENG`	`@0 Nutrient @5 08`
C03	`08`	`X`	`SPA`	`@0 Nutriente @5 08`
C03	`09`	`X`	`FRE`	`@0 Algae @2 NS @5 10`
C03	`09`	`X`	`ENG`	`@0 Algae @2 NS @5 10`
C03	`09`	`X`	`SPA`	`@0 Algae @2 NS @5 10`
C03	`10`	`X`	`FRE`	`@0 Quercus petraea @2 NS @5 11`
C03	`10`	`X`	`ENG`	`@0 Quercus petraea @2 NS @5 11`
C03	`10`	`X`	`SPA`	`@0 Quercus petraea @2 NS @5 11`
C03	`11`	`X`	`FRE`	`@0 Picea abies @2 NS @5 12`
C03	`11`	`X`	`ENG`	`@0 Picea abies @2 NS @5 12`
C03	`11`	`X`	`SPA`	`@0 Picea abies @2 NS @5 12`
C03	`12`	`X`	`FRE`	`@0 Dolomite @5 15`
C03	`12`	`X`	`ENG`	`@0 Dolomite @5 15`
C03	`12`	`X`	`SPA`	`@0 Dolomita @5 15`
C03	`13`	`X`	`FRE`	`@0 Chaux @5 16`
C03	`13`	`X`	`ENG`	`@0 Lime @5 16`
C03	`13`	`X`	`SPA`	`@0 Cal @5 16`
C03	`14`	`X`	`FRE`	`@0 Sol brun acide @2 NT @5 24`
C03	`14`	`X`	`ENG`	`@0 Brown acid soil @2 NT @5 24`
C03	`14`	`X`	`SPA`	`@0 Suelo pardo ácido @2 NT @5 24`
C03	`15`	`X`	`FRE`	`@0 Haute Ardenne @2 NG @4 INC @5 84`
C07	`01`	`X`	`FRE`	`@0 Thallophyta @2 NS`
C07	`01`	`X`	`ENG`	`@0 Thallophyta @2 NS`
C07	`01`	`X`	`SPA`	`@0 Thallophyta @2 NS`
C07	`02`	`X`	`FRE`	`@0 Fagaceae @2 NS`
C07	`02`	`X`	`ENG`	`@0 Fagaceae @2 NS`
C07	`02`	`X`	`SPA`	`@0 Fagaceae @2 NS`
C07	`03`	`X`	`FRE`	`@0 Dicotyledones @2 NS`
C07	`03`	`X`	`ENG`	`@0 Dicotyledones @2 NS`
C07	`03`	`X`	`SPA`	`@0 Dicotyledones @2 NS`
C07	`04`	`X`	`FRE`	`@0 Angiospermae @2 NS`
C07	`04`	`X`	`ENG`	`@0 Angiospermae @2 NS`
C07	`04`	`X`	`SPA`	`@0 Angiospermae @2 NS`
C07	`05`	`X`	`FRE`	`@0 Spermatophyta @2 NS`
C07	`05`	`X`	`ENG`	`@0 Spermatophyta @2 NS`
C07	`05`	`X`	`SPA`	`@0 Spermatophyta @2 NS`
C07	`06`	`X`	`FRE`	`@0 Coniferales @2 NS`
C07	`06`	`X`	`ENG`	`@0 Coniferales @2 NS`
C07	`06`	`X`	`SPA`	`@0 Coniferales @2 NS`
C07	`07`	`X`	`FRE`	`@0 Gymnospermae @2 NS`
C07	`07`	`X`	`ENG`	`@0 Gymnospermae @2 NS`
C07	`07`	`X`	`SPA`	`@0 Gymnospermae @2 NS`
C07	`08`	`X`	`FRE`	`@0 Propriété chimique @5 33`
C07	`08`	`X`	`ENG`	`@0 Chemical properties @5 33`
C07	`08`	`X`	`SPA`	`@0 Propiedad química @5 33`
C07	`09`	`X`	`FRE`	`@0 Arbre forestier feuillu @5 41`
C07	`09`	`X`	`ENG`	`@0 Hardwood forest tree @5 41`
C07	`09`	`X`	`SPA`	`@0 Arbol forestal frondoso @5 41`
C07	`10`	`X`	`FRE`	`@0 Arbre forestier résineux @5 42`
C07	`10`	`X`	`ENG`	`@0 Softwood forest tree @5 42`
C07	`10`	`X`	`SPA`	`@0 Arbol forestal resinoso @5 42`
C07	`11`	`X`	`FRE`	`@0 Amendement minéral @5 50`
C07	`11`	`X`	`ENG`	`@0 Mineral amendment @5 50`
C07	`11`	`X`	`SPA`	`@0 Enmienda inorgánica @5 50`
C07	`12`	`X`	`FRE`	`@0 Belgique @2 NG @5 60`
C07	`12`	`X`	`ENG`	`@0 Belgium @2 NG @5 60`
C07	`12`	`X`	`SPA`	`@0 Belgica @2 NG @5 60`
C07	`13`	`X`	`FRE`	`@0 Europe @2 NG`
C07	`13`	`X`	`ENG`	`@0 Europe @2 NG`
C07	`13`	`X`	`SPA`	`@0 Europa @2 NG`
C07	`14`	`X`	`FRE`	`@0 Sol forestier @2 NT @5 61`
C07	`14`	`X`	`ENG`	`@0 Forest soil @2 NT @5 61`
C07	`14`	`X`	`SPA`	`@0 Suelo forestal @2 NT @5 61`
N21				`@1 302`

Format Inist (serveur)

NO :	PASCAL 01-0434787 INIST
ET :	Effects of liming on forest soil algal communities
AU :	KOSTIKOV (Igor); CARNOL (Monique); DULIERE (Jean-Francois); HOFFMANN (Lucien)
AF :	Taras Sevcenko Kiev National University/Kiev/Ukraine (1 aut.); University of Liège, Institute of Botany, Sart Tilman/Liège/Belgique (2 aut., 4 aut.); University Mons-Hainaut, Faculté des Sciences-Biologie végétale/Mons/Belgique (3 aut.)
DT :	Publication en série; Niveau analytique
SO :	Archiv für Hydrobiologie. Supplementband, Algological studies; ISSN 0342-1120; Allemagne; Da. 2001; Vol. 138; Pp. 161-178; Bibl. 2 p.1/4
LA :	Anglais
EA :	The effects of the application of dolomite lime (5 t ha^-1) on soil algal communities were investigated in sessile oak (Quercus petraea (MATT.) LIEB.) and Norway spruce (Picea abies (L.) KARST.) plots situated in the Belgian Ardenne. Chlorophyta (60 taxa) were by far the most diverse group, followed by Xanthophyceae (10 taxa), Bacillariophyceae (3 taxa), Cyanophyceae (2 taxa) and Euglenophyceae (1 taxon). In both forest types, liming lead to a significant increase in soil pH, exchangeable magnesium and calcium. In the limed Quercus plots available phosphorus and soil solution nitrate concentrations were also increased. The soil algal diversity was similar in oak and spruce control plots and in limed spruce plots. However, in the limed oak plots a significantly higher algal diversity was observed. On the basis of a CCA analysis, three clusters of plots could be distinguished: a) Picea control plots, b) limed Picea and control Quercus plots, c) limed Quercus plots. Both soil pH and nutrient availability seem to be important in determining algal species composition in these forest soils.
CC :	002A14B04B; 002A33A02
FD :	Chaulage; Groupement végétal; pH; Facteur édaphique; Cation échangeable; Diversité espèces; Biodisponibilité; Nutriment; Algae; Quercus petraea; Picea abies; Dolomite; Chaux; Sol brun acide; Haute Ardenne
FG :	Thallophyta; Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae; Propriété chimique; Arbre forestier feuillu; Arbre forestier résineux; Amendement minéral; Belgique; Europe; Sol forestier
ED :	Liming amendment; Plant community; pH; Edaphic factor; Exchangeable cation; Species diversity; Bioavailability; Nutrient; Algae; Quercus petraea; Picea abies; Dolomite; Lime; Brown acid soil
EG :	Thallophyta; Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae; Chemical properties; Hardwood forest tree; Softwood forest tree; Mineral amendment; Belgium; Europe; Forest soil
SD :	Encalado; Comunidad vegetal; pH; Factor edáfico; Catión intercambiable; Diversidad especies; Biodisponibilidad; Nutriente; Algae; Quercus petraea; Picea abies; Dolomita; Cal; Suelo pardo ácido
LO :	INIST-7491B.354000096096120110
ID :	01-0434787

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Pascal:01-0434787

Le document en format XML

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<author><name sortKey="Kostikov, Igor" sort="Kostikov, Igor" uniqKey="Kostikov I" first="Igor" last="Kostikov">Igor Kostikov</name>
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<term>Dolomite</term>
<term>Edaphic factor</term>
<term>Exchangeable cation</term>
<term>Lime</term>
<term>Liming amendment</term>
<term>Nutrient</term>
<term>Picea abies</term>
<term>Plant community</term>
<term>Quercus petraea</term>
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<front><div type="abstract" xml:lang="en">The effects of the application of dolomite lime (5 t ha<sup>-1</sup>
) on soil algal communities were investigated in sessile oak (Quercus petraea (MATT.) LIEB.) and Norway spruce (Picea abies (L.) KARST.) plots situated in the Belgian Ardenne. Chlorophyta (60 taxa) were by far the most diverse group, followed by Xanthophyceae (10 taxa), Bacillariophyceae (3 taxa), Cyanophyceae (2 taxa) and Euglenophyceae (1 taxon). In both forest types, liming lead to a significant increase in soil pH, exchangeable magnesium and calcium. In the limed Quercus plots available phosphorus and soil solution nitrate concentrations were also increased. The soil algal diversity was similar in oak and spruce control plots and in limed spruce plots. However, in the limed oak plots a significantly higher algal diversity was observed. On the basis of a CCA analysis, three clusters of plots could be distinguished: a) Picea control plots, b) limed Picea and control Quercus plots, c) limed Quercus plots. Both soil pH and nutrient availability seem to be important in determining algal species composition in these forest soils.</div>
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<fA14 i1="02"><s1>University of Liège, Institute of Botany, Sart Tilman</s1>
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<sZ>4 aut.</sZ>
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<fA14 i1="03"><s1>University Mons-Hainaut, Faculté des Sciences-Biologie végétale</s1>
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<fA61><s0>A</s0>
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<fA64 i1="01" i2="1"><s0>Archiv für Hydrobiologie. Supplementband, Algological studies</s0>
</fA64>
<fA66 i1="01"><s0>DEU</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>The effects of the application of dolomite lime (5 t ha<sup>-1</sup>
) on soil algal communities were investigated in sessile oak (Quercus petraea (MATT.) LIEB.) and Norway spruce (Picea abies (L.) KARST.) plots situated in the Belgian Ardenne. Chlorophyta (60 taxa) were by far the most diverse group, followed by Xanthophyceae (10 taxa), Bacillariophyceae (3 taxa), Cyanophyceae (2 taxa) and Euglenophyceae (1 taxon). In both forest types, liming lead to a significant increase in soil pH, exchangeable magnesium and calcium. In the limed Quercus plots available phosphorus and soil solution nitrate concentrations were also increased. The soil algal diversity was similar in oak and spruce control plots and in limed spruce plots. However, in the limed oak plots a significantly higher algal diversity was observed. On the basis of a CCA analysis, three clusters of plots could be distinguished: a) Picea control plots, b) limed Picea and control Quercus plots, c) limed Quercus plots. Both soil pH and nutrient availability seem to be important in determining algal species composition in these forest soils.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>002A14B04B</s0>
</fC02>
<fC02 i1="02" i2="X"><s0>002A33A02</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Chaulage</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Liming amendment</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Encalado</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Groupement végétal</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Plant community</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Comunidad vegetal</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>pH</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>pH</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>pH</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Facteur édaphique</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Edaphic factor</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Factor edáfico</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Cation échangeable</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Exchangeable cation</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Catión intercambiable</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Diversité espèces</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Species diversity</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Diversidad especies</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Biodisponibilité</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Bioavailability</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Biodisponibilidad</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Nutriment</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Nutrient</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Nutriente</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Algae</s0>
<s2>NS</s2>
<s5>10</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Algae</s0>
<s2>NS</s2>
<s5>10</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Algae</s0>
<s2>NS</s2>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Quercus petraea</s0>
<s2>NS</s2>
<s5>11</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Quercus petraea</s0>
<s2>NS</s2>
<s5>11</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Quercus petraea</s0>
<s2>NS</s2>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Picea abies</s0>
<s2>NS</s2>
<s5>12</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Picea abies</s0>
<s2>NS</s2>
<s5>12</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Picea abies</s0>
<s2>NS</s2>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Dolomite</s0>
<s5>15</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Dolomite</s0>
<s5>15</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Dolomita</s0>
<s5>15</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Chaux</s0>
<s5>16</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG"><s0>Lime</s0>
<s5>16</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA"><s0>Cal</s0>
<s5>16</s5>
</fC03>
<fC03 i1="14" i2="X" l="FRE"><s0>Sol brun acide</s0>
<s2>NT</s2>
<s5>24</s5>
</fC03>
<fC03 i1="14" i2="X" l="ENG"><s0>Brown acid soil</s0>
<s2>NT</s2>
<s5>24</s5>
</fC03>
<fC03 i1="14" i2="X" l="SPA"><s0>Suelo pardo ácido</s0>
<s2>NT</s2>
<s5>24</s5>
</fC03>
<fC03 i1="15" i2="X" l="FRE"><s0>Haute Ardenne</s0>
<s2>NG</s2>
<s4>INC</s4>
<s5>84</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE"><s0>Thallophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG"><s0>Thallophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA"><s0>Thallophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE"><s0>Fagaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG"><s0>Fagaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA"><s0>Fagaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="ENG"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="SPA"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="FRE"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="ENG"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="SPA"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="FRE"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="ENG"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="SPA"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="FRE"><s0>Coniferales</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="ENG"><s0>Coniferales</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="SPA"><s0>Coniferales</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="FRE"><s0>Gymnospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="ENG"><s0>Gymnospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="SPA"><s0>Gymnospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="FRE"><s0>Propriété chimique</s0>
<s5>33</s5>
</fC07>
<fC07 i1="08" i2="X" l="ENG"><s0>Chemical properties</s0>
<s5>33</s5>
</fC07>
<fC07 i1="08" i2="X" l="SPA"><s0>Propiedad química</s0>
<s5>33</s5>
</fC07>
<fC07 i1="09" i2="X" l="FRE"><s0>Arbre forestier feuillu</s0>
<s5>41</s5>
</fC07>
<fC07 i1="09" i2="X" l="ENG"><s0>Hardwood forest tree</s0>
<s5>41</s5>
</fC07>
<fC07 i1="09" i2="X" l="SPA"><s0>Arbol forestal frondoso</s0>
<s5>41</s5>
</fC07>
<fC07 i1="10" i2="X" l="FRE"><s0>Arbre forestier résineux</s0>
<s5>42</s5>
</fC07>
<fC07 i1="10" i2="X" l="ENG"><s0>Softwood forest tree</s0>
<s5>42</s5>
</fC07>
<fC07 i1="10" i2="X" l="SPA"><s0>Arbol forestal resinoso</s0>
<s5>42</s5>
</fC07>
<fC07 i1="11" i2="X" l="FRE"><s0>Amendement minéral</s0>
<s5>50</s5>
</fC07>
<fC07 i1="11" i2="X" l="ENG"><s0>Mineral amendment</s0>
<s5>50</s5>
</fC07>
<fC07 i1="11" i2="X" l="SPA"><s0>Enmienda inorgánica</s0>
<s5>50</s5>
</fC07>
<fC07 i1="12" i2="X" l="FRE"><s0>Belgique</s0>
<s2>NG</s2>
<s5>60</s5>
</fC07>
<fC07 i1="12" i2="X" l="ENG"><s0>Belgium</s0>
<s2>NG</s2>
<s5>60</s5>
</fC07>
<fC07 i1="12" i2="X" l="SPA"><s0>Belgica</s0>
<s2>NG</s2>
<s5>60</s5>
</fC07>
<fC07 i1="13" i2="X" l="FRE"><s0>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="13" i2="X" l="ENG"><s0>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="13" i2="X" l="SPA"><s0>Europa</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="14" i2="X" l="FRE"><s0>Sol forestier</s0>
<s2>NT</s2>
<s5>61</s5>
</fC07>
<fC07 i1="14" i2="X" l="ENG"><s0>Forest soil</s0>
<s2>NT</s2>
<s5>61</s5>
</fC07>
<fC07 i1="14" i2="X" l="SPA"><s0>Suelo forestal</s0>
<s2>NT</s2>
<s5>61</s5>
</fC07>
<fN21><s1>302</s1>
</fN21>
</pA>
</standard>
<server><NO>PASCAL 01-0434787 INIST</NO>
<ET>Effects of liming on forest soil algal communities</ET>
<AU>KOSTIKOV (Igor); CARNOL (Monique); DULIERE (Jean-Francois); HOFFMANN (Lucien)</AU>
<AF>Taras Sevcenko Kiev National University/Kiev/Ukraine (1 aut.); University of Liège, Institute of Botany, Sart Tilman/Liège/Belgique (2 aut., 4 aut.); University Mons-Hainaut, Faculté des Sciences-Biologie végétale/Mons/Belgique (3 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Archiv für Hydrobiologie. Supplementband, Algological studies; ISSN 0342-1120; Allemagne; Da. 2001; Vol. 138; Pp. 161-178; Bibl. 2 p.1/4</SO>
<LA>Anglais</LA>
<EA>The effects of the application of dolomite lime (5 t ha<sup>-1</sup>
) on soil algal communities were investigated in sessile oak (Quercus petraea (MATT.) LIEB.) and Norway spruce (Picea abies (L.) KARST.) plots situated in the Belgian Ardenne. Chlorophyta (60 taxa) were by far the most diverse group, followed by Xanthophyceae (10 taxa), Bacillariophyceae (3 taxa), Cyanophyceae (2 taxa) and Euglenophyceae (1 taxon). In both forest types, liming lead to a significant increase in soil pH, exchangeable magnesium and calcium. In the limed Quercus plots available phosphorus and soil solution nitrate concentrations were also increased. The soil algal diversity was similar in oak and spruce control plots and in limed spruce plots. However, in the limed oak plots a significantly higher algal diversity was observed. On the basis of a CCA analysis, three clusters of plots could be distinguished: a) Picea control plots, b) limed Picea and control Quercus plots, c) limed Quercus plots. Both soil pH and nutrient availability seem to be important in determining algal species composition in these forest soils.</EA>
<CC>002A14B04B; 002A33A02</CC>
<FD>Chaulage; Groupement végétal; pH; Facteur édaphique; Cation échangeable; Diversité espèces; Biodisponibilité; Nutriment; Algae; Quercus petraea; Picea abies; Dolomite; Chaux; Sol brun acide; Haute Ardenne</FD>
<FG>Thallophyta; Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae; Propriété chimique; Arbre forestier feuillu; Arbre forestier résineux; Amendement minéral; Belgique; Europe; Sol forestier</FG>
<ED>Liming amendment; Plant community; pH; Edaphic factor; Exchangeable cation; Species diversity; Bioavailability; Nutrient; Algae; Quercus petraea; Picea abies; Dolomite; Lime; Brown acid soil</ED>
<EG>Thallophyta; Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae; Chemical properties; Hardwood forest tree; Softwood forest tree; Mineral amendment; Belgium; Europe; Forest soil</EG>
<SD>Encalado; Comunidad vegetal; pH; Factor edáfico; Catión intercambiable; Diversidad especies; Biodisponibilidad; Nutriente; Algae; Quercus petraea; Picea abies; Dolomita; Cal; Suelo pardo ácido</SD>
<LO>INIST-7491B.354000096096120110</LO>
<ID>01-0434787</ID>
</server>
</inist>
</record>

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Effects of liming on forest soil algal communities

Effects of liming on forest soil algal communities

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