Assessing ecosystem function of restoration plantings in south-eastern Australia

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Assessing ecosystem function of restoration plantings in south-eastern Australia. / Munro, N.T.; Wood, J.; Lindenmayer, D.B. et al.
in: Forest Ecology and Management, Jahrgang 282, 15.10.2012, S. 36-45.

Publikation: Beiträge in ZeitschriftenZeitschriftenaufsätzeForschungbegutachtet

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Munro NT, Wood J, Lindenmayer DB, Fischer J. Assessing ecosystem function of restoration plantings in south-eastern Australia. Forest Ecology and Management. 2012 Okt 15;282:36-45. doi: 10.1016/j.foreco.2012.06.048

Bibtex

@article{59d76ec8926e405eb48c07cdbc4de9a5,
title = "Assessing ecosystem function of restoration plantings in south-eastern Australia",
abstract = "We used the Landscape Function Analysis (LFA) (sensu Tongway and Hindley, 2004) to assess the development of ecosystem function in revegetation, particularly in relation to the basic ecological functions of soil stability, water infiltration and nutrient cycling. We compared these three LFA indices between two types of revegetation plantings, remnants, and cleared agricultural land (paddocks), in an agricultural landscape in south-eastern Australia. We differentiated between 'woodlot plantings' (planted with overstorey eucalypts only) and 'ecological plantings' (planted with many indigenous species of trees and shrubs). Remnant and paddock sites indicated the goal and starting point of restoration, respectively. Sites in remnant vegetation scored highest for all three functional attributes, whereas paddocks had high scores for soil stability, but low scores for water infiltration and nutrient cycling. Contrary to our expectations, soil stability, water infiltration and nutrient cycling did not differ between ecological plantings and woodlot plantings, and increased with age of planting (2-26. years) only for the nutrient cycling index. Although LFA provided an overview of some key functional differences between site types, it may be too coarse as a tool to measure restoration success. Specifically, the three functions considered by the LFA were strongly influenced by a single variable relating to perennial vegetation cover, but were essentially unaffected by more subtle differences between site types, such as quantity of leaf litter or cover of grasses. We also caution that Landscape Function Analysis derives surrogates of very basic functional attributes which may not be sufficiently sensitive to accurately reflect more complex ecological functions such as habitat provision for wildlife.",
keywords = "Ecosystems Research, Landscape Function Analysis, Planting, Reafforestation, Revegetation, Structural complexity",
author = "N.T. Munro and J. Wood and D.B. Lindenmayer and J. Fischer",
note = "Copyright 2012 Elsevier B.V., All rights reserved.",
year = "2012",
month = oct,
day = "15",
doi = "10.1016/j.foreco.2012.06.048",
language = "English",
volume = "282",
pages = "36--45",
journal = "Forest Ecology and Management",
issn = "0378-1127",
publisher = "Elsevier B.V.",

}

RIS

TY - JOUR

T1 - Assessing ecosystem function of restoration plantings in south-eastern Australia

AU - Munro, N.T.

AU - Wood, J.

AU - Lindenmayer, D.B.

AU - Fischer, J.

N1 - Copyright 2012 Elsevier B.V., All rights reserved.

PY - 2012/10/15

Y1 - 2012/10/15

N2 - We used the Landscape Function Analysis (LFA) (sensu Tongway and Hindley, 2004) to assess the development of ecosystem function in revegetation, particularly in relation to the basic ecological functions of soil stability, water infiltration and nutrient cycling. We compared these three LFA indices between two types of revegetation plantings, remnants, and cleared agricultural land (paddocks), in an agricultural landscape in south-eastern Australia. We differentiated between 'woodlot plantings' (planted with overstorey eucalypts only) and 'ecological plantings' (planted with many indigenous species of trees and shrubs). Remnant and paddock sites indicated the goal and starting point of restoration, respectively. Sites in remnant vegetation scored highest for all three functional attributes, whereas paddocks had high scores for soil stability, but low scores for water infiltration and nutrient cycling. Contrary to our expectations, soil stability, water infiltration and nutrient cycling did not differ between ecological plantings and woodlot plantings, and increased with age of planting (2-26. years) only for the nutrient cycling index. Although LFA provided an overview of some key functional differences between site types, it may be too coarse as a tool to measure restoration success. Specifically, the three functions considered by the LFA were strongly influenced by a single variable relating to perennial vegetation cover, but were essentially unaffected by more subtle differences between site types, such as quantity of leaf litter or cover of grasses. We also caution that Landscape Function Analysis derives surrogates of very basic functional attributes which may not be sufficiently sensitive to accurately reflect more complex ecological functions such as habitat provision for wildlife.

AB - We used the Landscape Function Analysis (LFA) (sensu Tongway and Hindley, 2004) to assess the development of ecosystem function in revegetation, particularly in relation to the basic ecological functions of soil stability, water infiltration and nutrient cycling. We compared these three LFA indices between two types of revegetation plantings, remnants, and cleared agricultural land (paddocks), in an agricultural landscape in south-eastern Australia. We differentiated between 'woodlot plantings' (planted with overstorey eucalypts only) and 'ecological plantings' (planted with many indigenous species of trees and shrubs). Remnant and paddock sites indicated the goal and starting point of restoration, respectively. Sites in remnant vegetation scored highest for all three functional attributes, whereas paddocks had high scores for soil stability, but low scores for water infiltration and nutrient cycling. Contrary to our expectations, soil stability, water infiltration and nutrient cycling did not differ between ecological plantings and woodlot plantings, and increased with age of planting (2-26. years) only for the nutrient cycling index. Although LFA provided an overview of some key functional differences between site types, it may be too coarse as a tool to measure restoration success. Specifically, the three functions considered by the LFA were strongly influenced by a single variable relating to perennial vegetation cover, but were essentially unaffected by more subtle differences between site types, such as quantity of leaf litter or cover of grasses. We also caution that Landscape Function Analysis derives surrogates of very basic functional attributes which may not be sufficiently sensitive to accurately reflect more complex ecological functions such as habitat provision for wildlife.

KW - Ecosystems Research

KW - Landscape Function Analysis

KW - Planting

KW - Reafforestation

KW - Revegetation

KW - Structural complexity

UR - http://www.scopus.com/inward/record.url?scp=84864411891&partnerID=8YFLogxK

UR - https://www.mendeley.com/catalogue/ee3676ec-dbb7-3284-9ea9-58cb493bbce7/

U2 - 10.1016/j.foreco.2012.06.048

DO - 10.1016/j.foreco.2012.06.048

M3 - Journal articles

AN - SCOPUS:84864411891

VL - 282

SP - 36

EP - 45

JO - Forest Ecology and Management

JF - Forest Ecology and Management

SN - 0378-1127

ER -

DOI