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Registro Completo |
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Biblioteca(s): |
Embrapa Florestas. |
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Data corrente: |
02/10/2008 |
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Data da última atualização: |
02/10/2008 |
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Autoria: |
MENDES, S. M.; RUIZ-CAMACHO, N.; FREITAS, H.; LAVELLE, P.; SOUSA, J. P. |
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Título: |
Bioindicators and biological indexes of soil quality. Improving the application of IBQS index in assessing effects of management practices on Mediterranean areas using soil epigeal macrofauna. |
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Ano de publicação: |
2008 |
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Fonte/Imprenta: |
In: INTERNATIONAL COLLOQUIUM ON SOIL ZOOLOGY, 15; INTERNATIONAL COLLOQUIUM ON APTERYGOTA, 12., 2008, Curitiba. Biodiversity, conservation and sustainabele management of soil animal: abstracts. Colombo: Embrapa Florestas. Editors: George Gardner Brown; Klaus Dieter Sautter; Renato Marques; Amarildo Pasini. 1 CD-ROM. |
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Idioma: |
Inglês |
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Conteúdo: |
Monitoring soil quality can be done using several approaches, namely through the use of soil
quality indices based on biological indicators. Among these, the ?Indice Biotique de la Qualité
du Sol? (IBQS) uses the concept of indicator species associated to a typology of sites/treatments
under assessment to rank their soil quality. In order to evaluate the application of IBQS
methodology to Mediterranean landscapes, its resolution power and applicability to soil epigeal
macrofauna data, a case-study, implemented in a Portuguese cork-oak forest (?Montado?) was
analysed. Five areas were established following a chronosequence of a disturbance regime
(time since understory clearing), comprising a non disturbed control area plus four areas with
different times since shrub was cut (1 year, 2 years, 3-4 years and 4-5 years); in the same farm,
three more areas were defined: an area with cattle grazing and two areas where the understory
cut residues were incorprated into soil at different times, implying a strong soil mobilization. At
each area, nine pitfall traps were settled, following a nested design. Sampling took place in
Autumn 2003. Biological material was identified to family/order and to species level; when this
was not possible, morphospecies was used.
Over 240 species/morphospecies were identified. When using the traditional IBQS formula,
areas where shrub is incorporated into the soil (the more disturbed areas) presented the highest
IBQS values, followed by areas with traditional ?Montado? use; the lowest value was obtained
for grazing. However, using a correction factor (indicator species contribution for explaining the
variability observed on a PCA) to the formula, developed under this study, IBQS values for areas
representing the traditional and sustainable use of ?Montados? are higher than the ones obtained
for other areas. Regarding the taxonomical discriminatory power of IBQS when calculated based
on data at different taxonomic level, the shift from species to higher taxonomical levels suggested
a loss of resolution, with values calculated at species level allowing a better discrimination
between the different areas.
Overall analysis showed that IBQS is sensitive to the abundance of specific taxa, especially of
opportunistic species, able to reach high abundances in disturbed areas, and originating a
biased ranking of soil quality values. This is a common phenomenon when evaluating pitfall trap
data, what could lead to a strong bias in IBQS values. The application of the developed correction
factor to IBQS formula originates a more ecologically relevant ranking, suggesting that its
application could be useful in bypassing questions arisen from using pitfall data in calculating
IBQS values. MenosMonitoring soil quality can be done using several approaches, namely through the use of soil
quality indices based on biological indicators. Among these, the ?Indice Biotique de la Qualité
du Sol? (IBQS) uses the concept of indicator species associated to a typology of sites/treatments
under assessment to rank their soil quality. In order to evaluate the application of IBQS
methodology to Mediterranean landscapes, its resolution power and applicability to soil epigeal
macrofauna data, a case-study, implemented in a Portuguese cork-oak forest (?Montado?) was
analysed. Five areas were established following a chronosequence of a disturbance regime
(time since understory clearing), comprising a non disturbed control area plus four areas with
different times since shrub was cut (1 year, 2 years, 3-4 years and 4-5 years); in the same farm,
three more areas were defined: an area with cattle grazing and two areas where the understory
cut residues were incorprated into soil at different times, implying a strong soil mobilization. At
each area, nine pitfall traps were settled, following a nested design. Sampling took place in
Autumn 2003. Biological material was identified to family/order and to species level; when this
was not possible, morphospecies was used.
Over 240 species/morphospecies were identified. When using the traditional IBQS formula,
areas where shrub is incorporated into the soil (the more disturbed areas) presented the highest
IBQS values, followed by areas with tradi... Mostrar Tudo |
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Categoria do assunto: |
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Marc: |
LEADER 03596naa a2200169 a 4500
001 1315006
005 2008-10-02
008 2008 bl uuuu u00u1 u #d
100 1 $aMENDES, S. M.
245 $aBioindicators and biological indexes of soil quality. Improving the application of IBQS index in assessing effects of management practices on Mediterranean areas using soil epigeal macrofauna.
260 $c2008
520 $aMonitoring soil quality can be done using several approaches, namely through the use of soil quality indices based on biological indicators. Among these, the ?Indice Biotique de la Qualité du Sol? (IBQS) uses the concept of indicator species associated to a typology of sites/treatments under assessment to rank their soil quality. In order to evaluate the application of IBQS methodology to Mediterranean landscapes, its resolution power and applicability to soil epigeal macrofauna data, a case-study, implemented in a Portuguese cork-oak forest (?Montado?) was analysed. Five areas were established following a chronosequence of a disturbance regime (time since understory clearing), comprising a non disturbed control area plus four areas with different times since shrub was cut (1 year, 2 years, 3-4 years and 4-5 years); in the same farm, three more areas were defined: an area with cattle grazing and two areas where the understory cut residues were incorprated into soil at different times, implying a strong soil mobilization. At each area, nine pitfall traps were settled, following a nested design. Sampling took place in Autumn 2003. Biological material was identified to family/order and to species level; when this was not possible, morphospecies was used. Over 240 species/morphospecies were identified. When using the traditional IBQS formula, areas where shrub is incorporated into the soil (the more disturbed areas) presented the highest IBQS values, followed by areas with traditional ?Montado? use; the lowest value was obtained for grazing. However, using a correction factor (indicator species contribution for explaining the variability observed on a PCA) to the formula, developed under this study, IBQS values for areas representing the traditional and sustainable use of ?Montados? are higher than the ones obtained for other areas. Regarding the taxonomical discriminatory power of IBQS when calculated based on data at different taxonomic level, the shift from species to higher taxonomical levels suggested a loss of resolution, with values calculated at species level allowing a better discrimination between the different areas. Overall analysis showed that IBQS is sensitive to the abundance of specific taxa, especially of opportunistic species, able to reach high abundances in disturbed areas, and originating a biased ranking of soil quality values. This is a common phenomenon when evaluating pitfall trap data, what could lead to a strong bias in IBQS values. The application of the developed correction factor to IBQS formula originates a more ecologically relevant ranking, suggesting that its application could be useful in bypassing questions arisen from using pitfall data in calculating IBQS values.
700 1 $aRUIZ-CAMACHO, N.
700 1 $aFREITAS, H.
700 1 $aLAVELLE, P.
700 1 $aSOUSA, J. P.
773 $tIn: INTERNATIONAL COLLOQUIUM ON SOIL ZOOLOGY, 15; INTERNATIONAL COLLOQUIUM ON APTERYGOTA, 12., 2008, Curitiba. Biodiversity, conservation and sustainabele management of soil animal: abstracts. Colombo: Embrapa Florestas. Editors: George Gardner Brown; Klaus Dieter Sautter; Renato Marques; Amarildo Pasini. 1 CD-ROM.
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Registro original: |
Embrapa Florestas (CNPF) |
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Registro Completo
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Biblioteca(s): |
Embrapa Caprinos e Ovinos. |
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Data corrente: |
24/04/2008 |
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Data da última atualização: |
08/05/2024 |
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Tipo da produção científica: |
Documentos |
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Autoria: |
SOUSA NETO, J. M. de; HOLANDA JUNIOR, E. V.; CAMPOS, R. T.; FRANÇA, F. M. C. |
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Afiliação: |
Jaime Martins de Sousa Neto, Cocepat; EVANDRO VASCONCELOS HOLANDA JUNIOR, CNPC; Robério Telmo Campos, Universidade Federal do Ceará (UFC) - Fortaleza, CE; Francisco Mavignier Cavalcante França, Bolsista FUNCAP junto ao INDI/FIEC. |
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Título: |
Estudo da viabilidade econômica da produção de carne ovina na região dos Inhamuns cearence: um estudo de caso. |
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Ano de publicação: |
2007 |
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Fonte/Imprenta: |
Sobral: Embrapa Caprinos, 2007. |
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Páginas: |
35 p. |
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Série: |
(Embrapa Caprinos. Documentos, 72). |
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Idioma: |
Português |
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Palavras-Chave: |
Brasil; Ceará; Ovino de corte; Tauá; Viabilidade economica. |
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Thesagro: |
Análise Econômica; Custo de Produção; Produção de Carne. |
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Categoria do assunto: |
L Ciência Animal e Produtos de Origem Animal |
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URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/CNPC/20873/1/doc72.pdf
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Marc: |
LEADER 00781nam a2200253 a 4500
001 1526512
005 2024-05-08
008 2007 bl uuuu u0uu1 u #d
100 1 $aSOUSA NETO, J. M. de
245 $aEstudo da viabilidade econômica da produção de carne ovina na região dos Inhamuns cearence$bum estudo de caso.$h[electronic resource]
260 $aSobral: Embrapa Caprinos$c2007
300 $a35 p.
490 $a(Embrapa Caprinos. Documentos, 72).
650 $aAnálise Econômica
650 $aCusto de Produção
650 $aProdução de Carne
653 $aBrasil
653 $aCeará
653 $aOvino de corte
653 $aTauá
653 $aViabilidade economica
700 1 $aHOLANDA JUNIOR, E. V.
700 1 $aCAMPOS, R. T.
700 1 $aFRANÇA, F. M. C.
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