@article{BernhardtRoemermannBaetenCravenetal.2015, author = {Bernhardt-R{\"o}mermann, Markus and Baeten, Lander and Craven, Dylan and De Frenne, Pieter and Hedl, Radim and Lenoir, Jonathan and Bert, Didier and Brunet, Jorg and Chudomelova, Marketa and Decocq, Guillaume and Dierschke, Hartmut and Dirnboeck, Thomas and D{\"o}rfler, Inken and Heinken, Thilo and Hermy, Martin and Hommel, Patrick and Jaroszewicz, Bogdan and Keczynski, Andrzej and Kelly, Daniel L. and Kirby, Keith J. and Kopecky, Martin and Macek, Martin and Malis, Frantisek and Mirtl, Michael and Mitchell, Fraser J. G. and Naaf, Tobias and Newman, Miles and Peterken, George and Petrik, Petr and Schmidt, Wolfgang and Standovar, Tibor and Toth, Zoltan and Van Calster, Hans and Verstraeten, Gorik and Vladovic, Jozef and Vild, Ondrej and Wulf, Monika and Verheyen, Kris}, title = {Drivers of temporal changes in temperate forest plant diversity vary across spatial scales}, series = {Global change biology}, volume = {21}, journal = {Global change biology}, number = {10}, publisher = {Wiley-Blackwell}, address = {Hoboken}, issn = {1354-1013}, doi = {10.1111/gcb.12993}, pages = {3726 -- 3737}, year = {2015}, abstract = {Global biodiversity is affected by numerous environmental drivers. Yet, the extent to which global environmental changes contribute to changes in local diversity is poorly understood. We investigated biodiversity changes in a meta-analysis of 39 resurvey studies in European temperate forests (3988 vegetation records in total, 17-75years between the two surveys) by assessing the importance of (i) coarse-resolution (i.e., among sites) vs. fine-resolution (i.e., within sites) environmental differences and (ii) changing environmental conditions between surveys. Our results clarify the mechanisms underlying the direction and magnitude of local-scale biodiversity changes. While not detecting any net local diversity loss, we observed considerable among-site variation, partly explained by temporal changes in light availability (a local driver) and density of large herbivores (a regional driver). Furthermore, strong evidence was found that presurvey levels of nitrogen deposition determined subsequent diversity changes. We conclude that models forecasting future biodiversity changes should consider coarse-resolution environmental changes, account for differences in baseline environmental conditions and for local changes in fine-resolution environmental conditions.}, language = {en} } @misc{HeinkenRaudnitschka2002, author = {Heinken, Thilo and Raudnitschka, Dorit}, title = {Do wild ungulates contribute to the dispersal of vascular plants in central European forests by epizoochory?}, url = {http://nbn-resolving.de/urn:nbn:de:kobv:517-opus-5850}, year = {2002}, abstract = {The external dispersal ("epizoochory") of vascular plant diaspores (seeds and fruits) by roe deer and wild boar, i.e. the most common wild large mammals with a large home range in central Europe, was investigated in a 6.5-km² forest area in NE Germany dominated by mesic deciduous forests. The study involved brushing out the diaspores from the coats and hooves of 25 shot roe deer and nine wild boar. The results were compared with the forest vegetation of the study area. Whilst wild boar transported large amounts of various diaspores in the coat, the significance of roe deer for epizoochory was low due to their sleek fur and different behaviour compared to wild boar. Altogether, 55 vascular plant species were transported externally. Since only a limited number of seeds came from woodland habitats, the open landscape was at least as important as a source of attached seeds as the forest vegetation. Thus, most plant species occurring in the studied forest area, especially characteristic woodland herbs, showed no adaptations to epizoochorous dispersal, although being very abundant in the herb layer. We conclude that hoofed game play a particular role concerning the dispersal of ruderal and grassland species in the agricultural landscape of central Europe. However, the actual spread of some herb species in forests of northern Germany, e.g. Agrostis capillaris, Brachypodium sylvaticum, Deschampsia flexuosa, Galium aparine and Urtica dioica, may be mainly facilitated by wild ungulates. Though dispersal by large mammals is an important mechanism for long-distance dispersal of plants in general, our results suggest that most of the characteristic herb species of mesic deciduous forests have only low epizoochorous dispersal potentials. The implications for nature conservation and silviculture are discussed.}, language = {en} } @article{SchoepkeHeinzePaetzigetal.2019, author = {Sch{\"o}pke, Benito and Heinze, Johannes and P{\"a}tzig, Marlene and Heinken, Thilo}, title = {Do dispersal traits of wetland plant species explain tolerance against isolation effects in naturally fragmented habitats?}, series = {Plant ecology : an international journal}, volume = {220}, journal = {Plant ecology : an international journal}, number = {9}, publisher = {Springer}, address = {Dordrecht}, issn = {1385-0237}, doi = {10.1007/s11258-019-00955-8}, pages = {801 -- 815}, year = {2019}, abstract = {The effects of habitat fragmentation and isolation on plant species richness have been verified for a wide range of anthropogenically fragmented habitats, but there is currently little information about their effects in naturally small and isolated habitats. We tested whether habitat area, heterogeneity, and isolation affect the richness of wetland vascular plant species in kettle holes, i.e., small glacially created wetlands, in an agricultural landscape of 1 km(2) in NE Germany. We compared fragmentation effects with those of forest fragments in the same landscape window. Since wetland and forest species might differ in their tolerance to isolation, and because isolation effects on plant species may be trait dependent, we asked which key life history traits might foster differences in isolation tolerance between wetland and forest plants. We recorded the flora and vegetation types in 83 isolated sites that contained 81 kettle holes and 25 forest fragments. Overall, the number of wetland species increased with increasing area and heterogeneity, i.e., the number of vegetation types, while area was not a surrogate for heterogeneity in these naturally fragmented systems. Isolation did not influence the number of wetland species but decreased the number of forest species. We also found that seeds of wetland species were on average lighter, more persistent and better adapted to epizoochory, e.g., by waterfowl, than seeds of forest species. Therefore, we suggest that wetland species are more tolerant to isolation than forest species due to their higher dispersal potential in space and time, which may counterbalance the negative effects of isolation.}, language = {en} } @article{CaronDeFrenneBrunetetal.2015, author = {Caron, Maria Mercedes and De Frenne, Pieter and Brunet, J{\"o}rg and Chabrerie, Olivier and Cousins, Sara A. O. and Decocq, Guillaume and Diekmann, Martin and Graae, Bente Jessen and Heinken, Thilo and Kolb, Annette and Lenoir, Jonathan and Naaf, Tobias and Plue, Jan and Selvi, Federico and Wulf, Monika and Verheyen, Kris}, title = {Divergent regeneration responses of two closely related tree species to direct abiotic and indirect biotic effects of climate change}, series = {Forest ecology and management}, volume = {342}, journal = {Forest ecology and management}, publisher = {Elsevier}, address = {Amsterdam}, issn = {0378-1127}, doi = {10.1016/j.foreco.2015.01.003}, pages = {21 -- 29}, year = {2015}, abstract = {Changing temperature and precipitation can strongly influence plant reproduction. However, also biotic interactions might indirectly affect the reproduction and recruitment success of plants in the context of climate change. Information about the interactive effects of changes in abiotic and biotic factors is essential, but still largely lacking, to better understand the potential effects of a changing climate on plant populations. Here we analyze the regeneration from seeds of Acer platanoides and Acer pseudoplatanus, two currently secondary forest tree species from seven regions along a 2200 km-wide latitudinal gradient in Europe. We assessed the germination, seedling survival and growth during two years in a common garden experiment where temperature, precipitation and competition with the understory vegetation were manipulated. A. platanoides was more sensitive to changes in biotic conditions while A. pseudoplatanus was affected by both abiotic and biotic changes. In general, competition reduced (in A. platanoides) and warming enhanced (in A. pseudoplatanus) germination and survival, respectively. Reduced competition strongly increased the growth of A. platanoides seedlings. Seedling responses were independent of the conditions experienced by the mother tree during seed production and maturation. Our results indicate that, due to the negative effects of competition on the regeneration of A. platanoides, it is likely that under stronger competition (projected under future climatic conditions) this species will be negatively affected in terms of germination, survival and seedling biomass. Climate-change experiments including both abiotic and biotic factors constitute a key step forward to better understand the response of tree species' regeneration to climate change. (C) 2015 Elsevier B.V. All rights reserved.}, language = {en} } @article{DittmannHeinkenSchmidt2018, author = {Dittmann, Thea and Heinken, Thilo and Schmidt, Marcus}, title = {Die W{\"a}lder von Magdeburgerforth (Fl{\"a}ming, Sachsen-Anhalt)}, series = {Tuexenia : Mitteilungen der Floristisch-Soziologischen Arbeitsgemeinschaft}, journal = {Tuexenia : Mitteilungen der Floristisch-Soziologischen Arbeitsgemeinschaft}, number = {38}, publisher = {Floristisch-Soziologische Arbeitsgemeinschaft}, address = {G{\"o}ttingen}, issn = {0722-494X}, doi = {10.14471/2018.38.009}, pages = {11 -- 42}, year = {2018}, abstract = {In einem rund 2.200 ha großen Waldgebiet bei Magdeburgerforth (Fl{\"a}ming, Sachsen-Anhalt) wurden 1948 bis 1950 von Harro Passarge 120 Vegetationsaufnahmen sowie eine Vegetationskartierung erstellt. Das Gebiet zeichnet sich durch eine große Vielfalt an Waldtypen aus den Verb{\"a}nden Agrostio-Quercion petraeae, Alnion glutinosae, Alnion incanae, Carpinion betuli, Dicrano-Pinion und Quercion roboris aus. Daher und weil viele der heute in W{\"a}ldern wirksamen Prozesse (z. B. Stickstoffeintrag, Klimawandel) vor 60 Jahren noch nicht sp{\"u}rbar waren, bietet sich das Gebiet f{\"u}r eine Wiederholungsuntersuchung besonders an. Da die Aufnahmefl{\"a}chen von Passarge nicht punktgenau verortet waren, wurden im Jahr 2014 in einem {\"u}ber die Forstabteilungen und die Vegetationskarte definierten Suchraum immer die der Erstaufnahme {\"a}hnlichsten Waldbest{\"a}nde erfasst. Insgesamt konnten 97 (81 \%) der Aufnahmen wiederholt werden. Vegetationsver{\"a}nderungen werden mithilfe einer NMDS-Ordination, der Gegen{\"u}berstellung von α -Diversit{\"a}t, Zeigerwerten und Waldbindungskategorien f{\"u}r die beiden Aufnahmezeitpunkte sowie {\"u}ber die Identifikation von Gewinner- und Verlierer-Arten analysiert. Auch wenn methodenbedingt bei der Wiederholungsuntersuchung nur die jeweils geringstm{\"o}gliche Vegetationsver{\"a}nderung abgebildet wird, konnten Ergebnisse erzielt werden, die mit denen quasi permanenter Plots {\"u}bereinstimmen. Die beobachteten allgemeinen Trends (Eutrophierung, Sukzession nach Nutzungswandel, Verlust lichtliebender und magerkeitszeigender Arten, Ausbreitung von stickstoffliebenden Arten und mesophilen Waldarten, Einwanderung von Neophyten, keine generelle Abnahme der Artenzahl) stimmen gut mit den in zahlreichen Studien aus mitteleurop{\"a}ischen W{\"a}ldern festgestellten {\"u}berein. Durch das von nassen bis trockenen sowie von bodensauer-n{\"a}hrstoffarmen bis zu relativ basenreichen B{\"o}den reichende Standortsspektrum innerhalb des Untersuchungsgebietes konnte aber - deutlicher als in den meisten bisherigen Fallstudien - gezeigt werden, dass sich die Resilienz der W{\"a}lder gegen{\"u}ber Vegetationsver{\"a}nderung je nach Ausgangsgesellschaft stark unterscheidet und jeweils unterschiedliche Treiber wirksam sind. Stellario-Carpinetum und Luzulo-Quercetum erwiesen sich als relativ stabil, und auch in den Feuchtw{\"a}ldern des Circaeo-Alnetum gab es trotz eines Artenwechsels wenig Hinweise auf Umweltver{\"a}nderungen. Dagegen wiesen die W{\"a}lder n{\"a}hrstoffarmer Standorte (Sphagno-Alnetum, Betulo-Quercetum, Dicrano-Pinion) viele Verliererarten und eine starke Eutrophierungstendenz auf. Die in besonderem Maße von historischen Waldnutzungsformen abh{\"a}ngigen thermophilen W{\"a}lder und die Flechten-Kiefernw{\"a}lder gingen weitgehend verloren.}, language = {de} } @misc{DittmannHeinkenSchmidt2018, author = {Dittmann, Thea and Heinken, Thilo and Schmidt, Marcus}, title = {Die W{\"a}lder von Magdeburgerforth (Fl{\"a}ming, Sachsen-Anhalt)}, series = {Postprints der Universit{\"a}t Potsdam : Mathematisch-Naturwissenschaftliche Reihe}, journal = {Postprints der Universit{\"a}t Potsdam : Mathematisch-Naturwissenschaftliche Reihe}, number = {1053}, issn = {1866-8372}, doi = {10.25932/publishup-46005}, url = {http://nbn-resolving.de/urn:nbn:de:kobv:517-opus4-460058}, pages = {11 -- 42}, year = {2018}, abstract = {In einem rund 2.200 ha großen Waldgebiet bei Magdeburgerforth (Fl{\"a}ming, Sachsen-Anhalt) wur-den 1948 bis 1950 von Harro Passarge 120 Vegetationsaufnahmen sowie eine Vegetationskartierung erstellt. Das Gebiet zeichnet sich durch eine große Vielfalt an Waldtypen aus den Verb{\"a}nden Agrostio-Quercion petraeae, Alnion glutinosae, Alnion incanae, Carpinion betuli, Dicrano-Pinion und Quercion roboris aus. Daher und weil viele der heute in W{\"a}ldern wirksamen Prozesse (z. B. Stickstoffeintrag, Klimawandel) vor 60 Jahren noch nicht sp{\"u}rbar waren, bietet sich das Gebiet f{\"u}r eine Wiederholungs-untersuchung besonders an. Da die Aufnahmefl{\"a}chen von Passarge nicht punktgenau verortet waren, wurden im Jahr 2014 in einem {\"u}ber die Forstabteilungen und die Vegetationskarte definierten Such-raum immer die der Erstaufnahme {\"a}hnlichsten Waldbest{\"a}nde erfasst. Insgesamt konnten 97 (81 \%) der Aufnahmen wiederholt werden. Vegetationsver{\"a}nderungen werden mithilfe einer NMDS-Ordination, der Gegen{\"u}berstellung von α-Diversit{\"a}t, Zeigerwerten und Waldbindungskategorien f{\"u}r die beiden Aufnahmezeitpunkte sowie {\"u}ber die Identifikation von Gewinner- und Verlierer-Arten analysiert.Auch wenn methodenbedingt bei der Wiederholungsuntersuchung nur die jeweils geringstm{\"o}gliche Vegetationsver{\"a}nderung abgebildet wird, konnten Ergebnisse erzielt werden, die mit denen quasi-permanenter Plots {\"u}bereinstimmen. Die beobachteten allgemeinen Trends (Eutrophierung, Sukzession nach Nutzungswandel, Verlust lichtliebender und magerkeitszeigender Arten, Ausbreitung von stick-stoffliebenden Arten und mesophilen Waldarten, Einwanderung von Neophyten, keine generelle Ab-nahme der Artenzahl) stimmen gut mit den in zahlreichen Studien aus mitteleurop{\"a}ischen W{\"a}ldern festgestellten {\"u}berein. Durch das von nassen bis trockenen sowie von bodensauer-n{\"a}hrstoffarmen bis zu relativ basenreichen B{\"o}den reichende Standortsspektrum innerhalb des Untersuchungsgebietes konnte aber - deutlicher als in den meisten bisherigen Fallstudien - gezeigt werden, dass sich die Resilienz der W{\"a}lder gegen{\"u}ber Vegetationsver{\"a}nderung je nach Ausgangsgesellschaft stark unterscheidet und jeweils unterschiedliche Treiber wirksam sind. Stellario-Carpinetum und Luzulo-Quercetum erwiesen sich als relativ stabil, und auch in den Feuchtw{\"a}ldern des Circaeo-Alnetum gab es trotz eines Arten-wechsels wenig Hinweise auf Umweltver{\"a}nderungen. Dagegen wiesen die W{\"a}lder n{\"a}hrstoffarmer Standorte (Sphagno-Alnetum, Betulo-Quercetum, Dicrano-Pinion) viele Verliererarten und eine starke Eutrophierungstendenz auf. Die in besonderem Maße von historischen Waldnutzungsformen abh{\"a}ngi-gen thermophilen W{\"a}lder und die Flechten-Kiefernw{\"a}lder gingen weitgehend verloren.}, language = {de} } @misc{Heinken2008, author = {Heinken, Thilo}, title = {Die nat{\"u}rlichen Kiefernstandorte Deutschlands und ihre Gef{\"a}hrdung}, url = {http://nbn-resolving.de/urn:nbn:de:kobv:517-opus-46506}, year = {2008}, abstract = {Nat{\"u}rliche Standorte der Waldkiefer gibt es in Deutschland nur kleinfl{\"a}chig. W{\"a}hrend Kiefernforste anstelle nat{\"u}rlicher Laubw{\"a}lder heute oft landschaftspr{\"a}gend sind, bildet die konkurrenzschwache und lichtbed{\"u}rftige Kiefer ausschließlich auf extrem trockenen oder nassen, n{\"a}hrstoffarmen Standorten naturnahe Schlusswaldgesellschaften. Regionale Schwerpunkte liegen in subkontinentalen Regionen wie dem nordostdeutschen Tiefland und Bayern, ein „nat{\"u}rliches Kiefernareal" l{\"a}sst sich aber kaum abgrenzen. An der Trockengrenze des Waldes finden sich auf Kalk- und Dolomitgesteinen artenreiche Karbonat-Trockenkiefernw{\"a}lder mit Elementen der alpinen Rasen und Kalkmagerrasen in der Bodenvegetation. Diese W{\"a}lder besiedeln steile, s{\"u}dexponierte Felsen und morphodynamisch aktive Bereiche wie Rutschh{\"a}nge und FlussSchotterb{\"o}den im Umkreis der Alpen, kommen aber auch in den Mittelgebirgen vor. Ihr Gegenst{\"u}ck auf sauren Standorten sind die Sand- und Silikat-Kiefernw{\"a}lder der Quarzsande und Sandstein-Verwitterungsb{\"o}den, deren Bodenvegetation durch Zwergstr{\"a}ucher, Moose und Strauchflechten gepr{\"a}gt ist. Hier siedelt die Kiefer in den Tieflagen besonders auf Binnend{\"u}nen und Sandern, aber auch auf K{\"u}stend{\"u}nen der Ostsee, in den Mittelgebirgen z. B. auf den Sandsteinriffen der S{\"a}chsischen Schweiz. Der dritte Wuchsbereich nat{\"u}rlicher Kiefernw{\"a}lder sind saure, n{\"a}hrstoffarme Moore, die ganz {\"u}berwiegend von Regenwasser gespeist werden. Auch die Kiefern-Moorw{\"a}lder sind in Nordostdeutschland und Bayern am h{\"a}ufigsten. Von diesen Standorten ausgehend, wo ihr Platz kaum von anderen Baumarten streitig gemacht wird, tritt die Waldkiefer immer wieder als Pionier auf weniger extremen Standorten auf. In der Naturlandschaft kam dies etwa nach Waldbr{\"a}nden oder St{\"u}rmen vor, doch der Mensch f{\"o}rderte die Kiefer durch Auflichtung der W{\"a}lder, Waldweide und Streunutzung stark. Auch die damit verbundene N{\"a}hrstoffverarmung macht eine exakte Abgrenzung nat{\"u}rlicher Kiefernstandorte unm{\"o}glich. Die schlechtw{\"u}chsigen und forstwirtschaftlich nicht interessanten, {\"a}sthetisch aber sehr ansprechenden nat{\"u}rlichen Kiefernbest{\"a}nde sind heute vor allem durch Stickstoff-Immissionen gef{\"a}hrdet. Trotz ihrer oft kargen Erscheinung besitzen sie einen hohen Wert f{\"u}r die Biodiversit{\"a}t und den Artenschutz. Neben bodenbewohnenden Flechten und regionalen Relikt-Endemiten ist vor allem die in den letzten Jahrzehnten zunehmend gef{\"a}hrdete Vielfalt an Mykorrhiza-Pilzen hervorzuheben, die der Kiefer das Leben auf extrem n{\"a}hrstoffarmen Standorten {\"u}berhaupt erm{\"o}glichen. Abschließend werden m{\"o}gliche Schutz- bzw. Regenerationsmaßnahmen wie das Abplaggen flechtenreicher Kiefernstandorte vorgestellt.}, language = {de} } @book{Heinken2008, author = {Heinken, Thilo}, title = {Dicrano-Pinion : Sand- und Silikat-Kiefernw{\"a}lder}, series = {Synopsis der Pflanzengesellschaften Deutschlands}, volume = {10}, journal = {Synopsis der Pflanzengesellschaften Deutschlands}, publisher = {Floristisch-Soziologische Arbeitsgemeinschaft}, address = {G{\"o}ttingen}, issn = {1433-8440}, pages = {88 S. : Ill.}, year = {2008}, language = {de} } @article{HeinkenWeber2013, author = {Heinken, Thilo and Weber, Ewald}, title = {Consequences of habitat fragmentation for plant species do we know enough?}, series = {Perspectives in plant ecology, evolution and systematics}, volume = {15}, journal = {Perspectives in plant ecology, evolution and systematics}, number = {4}, publisher = {Elsevier}, address = {Jena}, issn = {1433-8319}, doi = {10.1016/j.ppees.2013.05.003}, pages = {205 -- 216}, year = {2013}, abstract = {Habitat fragmentation is one of the most important causes for the decline of plant species. However, plants differing in phylogeny, habitat requirements and biology are likely to respond differently to habitat fragmentation. We ask whether case studies on the effects of habitat fragmentation conducted so far allow generalizations about its effects on the fitness and genetic diversity of populations of endangered plant species. We compared the characteristics of plant species endangered in Germany whose sensitivity to habitat fragmentation had been studied with those of the endangered species that had not been studied. We found strong discrepancies between the two groups with regard to their taxonomy and traits relevant to their sensitivity to habitat fragmentation. Monocots, graminoids, clonal, abiotically pollinated and self compatible species were underrepresented among the studied species, and most study species were from a few habitat types, in particular grasslands. We conclude that our current knowledge of the effects of habitat fragmentation on plant populations is not sufficient to provide widely applicable guidelines for species management. The selection of species studied so far has been biased toward species from certain habitats and species exhibiting traits that probably make them vulnerable to habitat fragmentation. Future studies should include community-wide approaches in different habitats, e.g. re-visitation studies in which the species pool is assessed at different time intervals, and population-biological studies of species from a wide range of habitats, and of different life forms and growth strategies. A more representative picture of the effects of habitat fragmentation would allow a better assessment of threats and more specific recommendations for optimally managing populations of endangered plants.}, language = {en} } @misc{WulfHeinken2008, author = {Wulf, Monika and Heinken, Thilo}, title = {Colonization of recent coniferous versus deciduous forest stands by vascular plants at the local scale}, url = {http://nbn-resolving.de/urn:nbn:de:kobv:517-opus-46080}, year = {2008}, abstract = {Questions: 1. Are there differences among species in their preference for coniferous vs. deciduous forest? 2. Are tree and shrub species better colonizers of recent forest stands than herbaceous species? 3. Do colonization patterns of plant species groups depend on tree species composition? Location: Three deciduous and one coniferous recent forest areas in Brandenburg, NE Germany. Methods: In 34 and 21 transects in coniferous and deciduous stands, respectively, we studied the occurrence and percentage cover of vascular plants in a total of 150 plots in ancient stands, 315 in recent stands and 55 at the ecotone. Habitat preference, diaspore weight, generative dispersal potential and clonal extension were used to explain mechanisms of local migration. Regression analysis was conducted to test whether migration distance was related to species' life-history traits. Results: 25 species were significantly associated with ancient stands and ten species were significantly more frequent in recent stands. Tree and shrub species were good colonizers of recent coniferous and deciduous stands. In the coniferous stands, all herbaceous species showed a strong dispersal limitation during colonization, whereas in the deciduous stands generalist species may have survived in the grasslands which were present prior to afforestation. Conclusions: The fast colonization of recent stands by trees and shrubs can be explained by their effective dispersal via wind and animals. This, and the comparably efficient migration of herbaceous forest specialists into recent coniferous stands, implies that the conversion of coniferous into deciduous stands adjacent to ancient deciduous forests is promising even without planting of trees.}, language = {en} }