TY  - JOUR
A1  - Schall, Peter
A1  - Gossner, Martin M.
A1  - Heinrichs, Steffi
A1  - Fischer, Markus
A1  - Boch, Steffen
A1  - Prati, Daniel
A1  - Jung, Kirsten
A1  - Baumgartner, Vanessa
A1  - Blaser, Stefan
A1  - Böhm, Stefan
A1  - Buscot, Francois
A1  - Daniel, Rolf
A1  - Goldmann, Kezia
A1  - Kaiser, Kristin
A1  - Kahl, Tiemo
A1  - Lange, Markus
A1  - Müller, Jörg Hans
A1  - Overmann, Jörg
A1  - Renner, Swen C.
A1  - Schulze, Ernst-Detlef
A1  - Sikorski, Johannes
A1  - Tschapka, Marco
A1  - Türke, Manfred
A1  - Weisser, Wolfgang W.
A1  - Wemheuer, Bernd
A1  - Wubet, Tesfaye
A1  - Ammer, Christian
T1  - The impact of even-aged and uneven-aged forest management on regional biodiversity of multiple taxa in European beech forests
JF  - Journal of applied ecology : an official journal of the British Ecological Society
N2  - 1. For managed temperate forests, conservationists and policymakers favour fine-grained uneven-aged (UEA) management over more traditional coarse-grained even-aged (EA) management, based on the assumption that within-stand habitat heterogeneity enhances biodiversity. There is, however, little empirical evidence to support this assumption. We investigated for the first time how differently grained forest management systems affect the biodiversity of multiple above- and below-ground taxa across spatial scales. 2. We sampled 15 taxa of animals, plants, fungi and bacteria within the largest contiguous beech forest landscape of Germany and classified them into functional groups. Selected forest stands have been managed for more than a century at different spatial grains. The EA (coarse-grained management) and UEA (fine-grained) forests are comparable in spatial arrangement, climate and soil conditions. These were compared to forests of a nearby national park that have been unmanaged for at least 20years. We used diversity accumulation curves to compare -diversity for Hill numbers D-0 (species richness), D-1 (Shannon diversity) and D-2 (Simpson diversity) between the management systems. Beta diversity was quantified as multiple-site dissimilarity. 3. Gamma diversity was higher in EA than in UEA forests for at least one of the three Hill numbers for six taxa (up to 77%), while eight showed no difference. Only bacteria showed the opposite pattern. Higher -diversity in EA forests was also found for forest specialists and saproxylic beetles. 4. Between-stand -diversity was higher in EA than in UEA forests for one-third (all species) and half (forest specialists) of all taxa, driven by environmental heterogeneity between age-classes, while -diversity showed no directional response across taxa or for forest specialists. 5. Synthesis and applications. Comparing EA and uneven-aged forest management in Central European beech forests, our results show that a mosaic of different age-classes is more important for regional biodiversity than high within-stand heterogeneity. We suggest reconsidering the current trend of replacing even-aged management in temperate forests. Instead, the variability of stages and stand structures should be increased to promote landscape-scale biodiversity.
KW  - beta diversity
KW  - forest specialists
KW  - gamma diversity
KW  - heterogeneity
KW  - Hill numbers
KW  - saproxylic beetles
KW  - spatial grain
KW  - species accumulation curve
KW  - species richness
KW  - species turnover
Y1  - 2017
U6  - https://doi.org/10.1111/1365-2664.12950
SN  - 0021-8901
SN  - 1365-2664
VL  - 55
IS  - 1
SP  - 267
EP  - 278
PB  - Wiley
CY  - Hoboken
ER  - 
TY  - THES
A1  - Naaf, Tobias
T1  - Floristic homogenization and impoverishment : herb layer changes over two decades in deciduous forest patches of the Weser-Elbe region (NW Germany)
T1  - Floristische Homogenisierung und Verarmung : Krautschichtveränderungen über 20 Jahre in Laubwaldfragmenten des Elbe-Weser-Dreiecks (NW-Dtl.)
N2  - Human-induced alterations of the environment are causing biotic changes worldwide, including the extinction of species and a mixing of once disparate floras and faunas. One type of biological communities that is expected to be particularly affected by environmental alterations are herb layer plant communities of fragmented forests such as those in the west European lowlands. However, our knowledge about current changes in species diversity and composition in these communities is limited due to a lack of adequate long-term studies. In this thesis, I resurveyed the herb layer communities of ancient forest patches in the Weser-Elbe region (NW Germany) after two decades using 175 semi-permanent plots. The general objectives were (i) to quantify changes in plant species diversity considering also between-community (β) and functional diversity, (ii) to determine shifts in species composition in terms of species’ niche breadth and functional traits and (iii) to find indications on the most likely environmental drivers for the observed changes. These objectives were pursued with four independent research papers (Chapters 1-4) whose results were brought together in a General Discussion. Alpha diversity (species richness) increased by almost four species on average, whereas β diversity tended to decrease (Chapter 1). The latter is interpreted as a beginning floristic homogenization. The observed changes were primarily the result of a spread of native habitat generalists that are able to tolerate broad pH and moisture ranges. The changes in α and β diversity were only significant when species abundances were neglected (Chapters 1 and 2), demonstrating that the diversity changes resulted mainly from gains and losses of low-abundance species. This study is one of the first studies in temperate Europe that demonstrates floristic homogenization of forest plant communities at a larger than local scale. The diversity changes found at the taxonomic level did not result in similar changes at the functional level (Chapter 2). The likely reason is that these communities are functionally “buffered”. Single communities involve most of the functional diversity of the regional pool, i.e., they are already functionally rich, while they are functionally redundant among each other, i.e., they are already homogeneous. Independent of taxonomic homogenization, the abundance of 30 species decreased significantly (Chapter 4). These species included 12 ancient forest species (i.e., species closely tied to forest patches with a habitat continuity > 200 years) and seven species listed on the Red List of endangered plant species in NW Germany. If these decreases continue over the next decades, local extinctions may result. This biotic impoverishment would seriously conflict with regional conservation goals. Community assembly mechanisms changed at the local level particularly at sites that experienced disturbance by forest management activities between the sampling periods (Chapter 3). Disturbance altered community assembly mechanisms in two ways: (i) it relaxed environmental filters and allowed the coexistence of different reproduction strategies, as reflected by a higher diversity of reproductive traits at the time of the resurvey, and (ii) it enhanced light availability and tightened competitive filters. These limited the functional diversity with respect to canopy height and selected for taller species. Thirty-one winner and 30 loser species, which had significantly increased or decreased in abundance, respectively, were characterized by various functional traits and ecological performances to find indications on the most likely environmental drivers for the observed floristic changes (Chapter 4). Winner species had higher seed longevity, flowered later in the season and had more often an oceanic distribution compared to loser species. Loser species tended to have a higher specific leaf area, to be more susceptible to deer browsing and to have a performance optimum at higher soil pH values compared to winner species. Multiple logistic regression analyses indicated that disturbances due to forest management interventions were the primary cause of the species shifts. As one of the first European resurvey studies, this study provides indications that an enhanced browsing pressure due to increased deer densities and increasingly warmer winters are important drivers. The study failed to demonstrate that eutrophication and acidification due to atmospheric deposition substantially drive herb layer changes. The restriction of the sample to the most base-rich sites in the region is discussed as a likely reason. Furthermore, the decline of several ancient forest species is discussed as an indication that the forest patches are still paying off their “extinction debt”, i.e., exhibit a delayed response to forest fragmentation.
N2  - Umweltveränderungen beeinträchtigen weltweit die Artenvielfalt. Die Lebensgemeinschaften fragmentierter Lebensräume gelten als besonders anfällig für Veränderungen. In dieser Arbeit wurden Untersuchungen an Krautschichtgemeinschaften historisch alter Waldfragmente im Elbe-Weser-Dreieck nach zwei Jahrzehnten wiederholt. Ziel war es anhand von 175 semi-permanenten Aufnahmeflächen (i) die Veränderungen der Pflanzenartendiversität zu quantifizieren, (ii) Artenverschiebungen in Bezug auf Nischenbreite und funktionale Merkmale festzustellen und (iii) Hinweise auf die verantwortlichen Umweltveränderungen zu finden. Die α-Diversität (Artenzahl) stieg durchschnittlich um vier Arten an. Die β-Diversität (Artenturnover zwischen den Flächen) nahm tendenziell ab. Letzteres wird als Beginn einer floristischen Homogenisierung interpretiert. Diese Studie ist eine der ersten im gemäßigten Europa, die eine floristische Homogenisierung von Waldpflanzengemeinschaften auf einer größeren als der lokalen Ebene aufzeigt. Die Diversitätsveränderungen auf taxonomischer Ebene führten nicht zu ähnlichen Veränderungen auf funktionaler Ebene. Bereits einzelne Gemeinschaften wiesen den Großteil der funktionalen Vielfalt des regionalen Artenpools, also ein Maximum an funktionaler Diversität auf. Gleichzeitig waren sie untereinander funktional redundant, also bereits homogen. Die mit der beginnenden taxonomischen Homogenisierung verbundene floristische Verarmung wird als gering eingestuft, da die Homogenisierung primär das Ergebnis der Zuwanderung häufig vorkommender Standortgeneralisten war. Unabhängig von der Homogenisierung gingen 30 Arten signifikant in ihrer Abundanz zurück, darunter 12 an historisch alte Wälder gebundene Arten sowie sieben Rote-Liste-Arten. Ein weiterer Rückgang oder ein lokales Aussterben dieser Arten stünde im Widerspruch zu regionalen Naturschutzzielen. Nullmodelltests und der Vergleich funktionaler und taxonomischer Diversitätskomponenten lassen auf regionaler Ebene auf eine zeitliche Konstanz der grundlegenden Mechanismen der Artenvergesellschaftung schließen. Auf der lokalen Ebene veränderten sich die Vergesellschaftungsmechanismen erheblich, insbesondere auf forstwirtschaftlich gestörten Standorten. Einerseits ermöglichte dort eine Abschwächung der Umweltfilter die Koexistenz von Arten mit unterschiedlichen Reproduktionsstrategien. Andererseits führte die erhöhte Lichtverfügbarkeit zu einer Verstärkung der Konkurrenzfilter und einer Selektion hochwüchsiger Arten. Gewinner- und Verliererarten wurden anhand funktionaler Merkmale und ihres ökologischen Verhaltens charakterisiert, um Hinweise auf die verantwortlichen Umweltveränderungen zu finden. Gewinnerarten wiesen eine höhere Langlebigkeit der Samen auf, blühten später in der Vegetationsperiode und hatten öfter eine ozeanische Verbreitung. Verliererarten hatten eine höhere spezifische Blattfläche, einen höheren Attraktivitätswert als Wildäsung und ein ökologisches Optimum bei höheren pH-Werten. Logistische Regressionsanalysen zeigen, dass Störung durch forstwirtschaftliche Eingriffe hauptverantwortlich für die Artenverschiebungen war. Zusätzlich liefert diese Wiederholungsstudie als eine der ersten in Europa Hinweise darauf, dass ein erhöhter Äsungsdruck sowie zunehmend mildere Winter entscheidende Einflussfaktoren darstellen. Der Rückgang mehrerer an historisch alte Wälder gebundener Arten wird als Anzeichen für eine verspätete Reaktion auf die Waldfragmentierung diskutiert.
KW  - Beta-Diversität
KW  - Funktionelle Diversität
KW  - Globaler Wandel
KW  - Langzeitveränderung
KW  - Wiederholungsstudie
KW  - beta diversity
KW  - functional diversity
KW  - global change
KW  - long-term change
KW  - resurvey
Y1  - 2011
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:kobv:517-opus-52446
ER  -