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The Roots: How Do Seedlings of Native Tree Species React to the Competition

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The Roots: How Do Seedlings of Native Tree Species React to the Competition Back to the roots: how do seedlings of native tree species react to the competition by exotic species? Heike Kawaletz, Inga Mölder, Peter Annighöfer, André Terwei, Stefan Zerbe, Christian Ammer To cite this version: Heike Kawaletz, Inga Mölder, Peter Annighöfer, André Terwei, Stefan Zerbe, et al.. Back to the roots: how do seedlings of native tree species react to the competition by exotic species?. Annals of Forest Science, Springer Nature (since 2011)/EDP Science (until 2010), 2014, 71 (3), pp.337-347. 10.1007/s13595-013-0347-z. hal-01101538 HAL Id: hal-01101538 https://hal.archives-ouvertes.fr/hal-01101538 Submitted on 8 Jan 2015 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Annals of Forest Science (2014) 71:337–347 DOI 10.1007/s13595-013-0347-z ORIGINAL PAPER Back to the roots: how do seedlings of native tree species react to the competition by exotic species? Heike Kawaletz & Inga Mölder & Peter Annighöfer & André Terwei & Stefan Zerbe & Christian Ammer Received: 25 April 2013 /Accepted: 15 November 2013 /Published online: 6 December 2013 # INRA and Springer-Verlag France 2013 Abstract mixtures. In addition to ontogeny, competition affected bio- & Context Identifying the traits of exotic species may explain mass allocation patterns. Under root competition by the exotic their invasiveness and help control the negative impacts of species, the native species preferentially allocated their bio- these species on native ecosystems. In this study, we investi- mass to the roots. A higher allocation to the roots was mainly gated root competition as an important driver for the compet- achieved at the expense of leaf and branch biomass. itiveness of two exotic tree species in the seedling stage. & Conclusion Root competition of P. serotina and R. & Aims In a pot experiment, carried out in Central Europe, we pseudoacacia may be a reason for the lack of Q. robur and studied the effect of root competition of two exotic tree species C. betulus in the seedling stage in natural environments where (Prunus serotina Ehrh. and Robinia pseudoacacia L.) on all four species occur. biomass allocation of two native ones (Quercus robur L. and Carpinus betulus L.). Keywords Biomass allocation . Balanced growth & Methods Seedlings of these species were exposed to intra- hypothesis . Pot experiment . Prunus serotina . Robinia and interspecific mixtures with and without the effect of root pseudoacacia competition. For this, belowground plastic partitions were installed in the pots. & Results Competition intensity in the pots increased over 1 Introduction time, irrespective of mixture type. However, this increase was much higher for the native species if mixed with the In natural ecosystems, nutrients and other resources that are exotic species compared to monocultures or inter-native needed for tree growth, regeneration, and reproduction are usually limited. According to Goldberg (1990), a species is Handling Editor: Gilbert Aussenac competitive if it combines two attributes: (1) being effective in Contribution of the co-authors Heike Kawaletz: designing the experiment, acquiring resources to maintain its own fitness, i.e., reducing writing the paper, running the data analysis resource availability of competitors while increasing the own Inga Mölder: supervising the work, coordinating the research project biomass, and (2) keeping growth and survival as high as Peter Annighöfer, André Terwei: writing the paper Stefan Zerbe, Christian Ammer: supervising the work, coordinating the possible if resource availability decreases. For both strategies, research project plasticity in biomass allocation is essential. Besides the effects of ontogeny, i.e., plant size, biomass allocation is therefore to a H. Kawaletz (*) : P. Annighöfer : C. Ammer Department of Silviculture and Forest Ecology of the Temperate considerable amount driven by resource availability (Schall Zones, University of Göttingen, Büsgenweg 1, 37077 Göttingen, et al. 2012). As suggested by the balanced growth hypothesis Germany (Shipley and Meziane 2002), under restricted resource avail- e-mail: [email protected] ability, plants increase the efficiency in resource uptake and/or I. Mölder allocate more biomass to those compartments, which are Energieagentur Region Göttingen e.V., Berliner Str. 2, involved in the acquisition of the primarily limiting resource. 37073 Göttingen, Germany Numerous studies showed an effect of aboveground (shoot) competition on biomass partitioning (e.g., Horn 1971; Nilsson A. Terwei : S. Zerbe Faculty of Science and Technology, Free University and Albrektson 1993;Fengetal.2007). In case of strong of Bozen-Bolzano, piazza Università 5, 39100 Bolzano, Italy shading, plants allocate more biomass to the aboveground 338 H. Kawaletz et al. organs, especially to the leaves, in order to maximize photo- and is not able to successfully compete with species casting synthesis (van Hees 1997;Ammer2003;Hofmannand deep shade. C. betulus is a late successional, shade-tolerant Ammer 2008). Although belowground (root) competition is species and is often associated with Q. robur in Querco- as important as aboveground interactions (Wilson 1988; Carpinetum forests that can be found on the most fertile soils Casper and Jackson 1997; Cahill 2003), there is less informa- in temperate Europe (Ellenberg 1988). tion on how tree species change biomass allocation patterns in Actually, in a pot experiment containing mixtures of exotic response to belowground competition (Haase 2009). Howev- P. serotina and R. pseudoacacia and the two native species Q. er, according to the balanced growth hypothesis, biomass will robur and C. betulus, strongly changed biomass production be allocated to the roots if nutrients or water becomes the was observed (Kawaletz et al. 2013). In the regarding exper- limiting factor for growth (e.g., Ibrahim et al. 1998;Bloor iment, the competition and growth response of the four spe- et al. 2008;Kleczewskietal.2012). By changing biomass cies in monocultures and mixtures were studied under con- allocation patterns, plants therefore respond to changes in trolled conditions. Whereas biomass production of the species resource availability, which may be interpreted as an adapta- in different inter- and intraspecific competitive situations was tion to stress (e.g., Shipley and Meziane 2002; Delagrange the main focus of a previous article (Kawaletz et al. 2013), et al. 2004;Curtetal.2005). According to Weiner (2004), biomass allocation pattern is addressed in the present study. plasticity in biomass allocation is important for plant survival, We tested the following hypotheses: (1) competition by exotic e.g., under competitive situations. In environments of low soil P. s ero ti na and R. pseudoacacia on native Q. robur and C. water or nutrient availability, the proportion of root biomass betulus under open field conditions is much stronger than that may therefore be treated as a measure of competition of intraspecific or inter-native interference and (2) the propor- pressure from neighboring plants (Aerts et al. 1991; tion of root biomass of a seedling increases with increasing Cahill 2003; Bloor et al. 2008). root competition intensity. In many ecosystems, invasive exotic species are able to alter the environmental conditions such as the nutrient and hydrologic cycle (Mack et al. 2000) and may negatively affect 2Methods the abundance or survival of native species due to a higher biomass production (e.g., Morrison and Mauck 2007;Pyšek 2.1 Experimental setup and Richardson 2008; Lamarque et al. 2011). The high bio- mass production in the early stages, indicating a strong com- A controlled pot experiment was conducted under outdoors petitiveness in the regeneration phase, leads to resource de- conditions in Göttingen, Germany (see also Kawaletz et al. pletion, hampering the growth of neighboring plants. 2013). The experimental site was located at 170 m above sea The two North American tree species black cherry (Prunus level. The climate is temperate with an average annual pre- serotina Ehrh.) and black locust (Robinia pseudoacacia L.) cipitation of 644.9 mm and most of the rain falling in June have managed to successfully spread throughout Europe. (81.3 mm). The average monthly temperature ranges from 4.8 Both species are among the 18 most invasive terrestrial plant to 13 °C, with a mean annual temperature of about 8.7 °C species (DAISIE Project 2009). They are considered to be (Wetterstation Göttingen 2013). under the most aggressive exotic tree species in European Four tree species were used for the pot experiment: pedun- forests and are regarded as strong competitors of native tree culate oak (Q. robur) and hornbeam (C. betulus)werechosen species (e.g., Kleinbauer et al. 2010; Vanhellemont et al. as native species; black cherry (P. s ero ti na ) and black locust 2010). P. serotina was one of the first North American tree (R. pseudoacacia) represented the exotic species in the exper- species that was introduced to Europe (Starfinger et al. 2003). iment. The seedlings of each tree species were obtained from a It is able to alter biodiversity if it occurs in monospecific nursery in Germany (Münchehof, Lower Saxony) to minimize stands that impede native tree regeneration (Closset-Kopp transport-induced damages. In spring 2010, the 1-year-old et al. 2007). Due to its ability to fix nitrogen, R. pseudoacacia seedlings were planted in pots with a volume of 65 l (diameter, especially is a threat for the identity and integrity of nutrient- 54 cm; height, 33 cm). Prior to planting, each pot was filled poor sites where it can change soil conditions and alter species with 5 cm coarse gravel to ensure drainage and with fertilized compositions (Rice et al.
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