
bioRxiv preprint doi: https://doi.org/10.1101/2020.04.30.070268; this version posted April 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY 4.0 International license. 1 The mistletoe Struthanthus flexicaulis reduces dominance and increases diversity of plants 2 in campo rupestre 3 Graziella França Monteiro 1,2*, Milton Barbosa1, Yasmine Antonini 2, Marcela Fortes de 4 Oliveira Passos 2,3, Samuel Novais 1, G. Wilson Fernandes 1*. 5 6 7 1 Ecologia Evolutiva & Biodiversidade/DGEE, Universidade Federal de Minas Gerais, Belo 8 Horizonte – Minas Gerais, 30270-971, Brazil. 9 2 Laboratório de Biodiversidade/DEBIO/ICEB/Universidade Federal de Ouro Preto, Ouro 10 Preto – Minas Gerais, 35400-000, Brazil. 11 3 Graduate Program in Applied Ecology /DBI-Universidade Federal de Lavras/UFLA, Lavras 12 – Minas Gerais, 37200-000, Brazil. 13 14 *Corresponding author: [email protected] 15 16 17 18 19 20 21 22 1 bioRxiv preprint doi: https://doi.org/10.1101/2020.04.30.070268; this version posted April 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY 4.0 International license. 23 ABSTRACT 24 The interaction between hemiparasites and their host plants is an important structuring 25 mechanism for plant communities. The mistletoe Struthanthus flexicaulis (Loranthaceae) is 26 widely distributed in the campo rupestre ecosystem and likely has an important role in 27 structuring the communities of which its hosts are part. The main goals of this study were to 28 investigate the effects of parasitism by S. flexicaulis on host plants in a degraded area of 29 campo rupestre and to determine how parasitism affects characteristics of the structure of this 30 plant community over time. We found that parasitized plants had smaller crowns and branch 31 growth, and suffered lower mortality compared to non-parasitized plants. Parasitism by S. 32 flexicaulis decreased dominance and increased the diversity and evenness of plants in the 33 community over time. Parasitism leads to competition with the host for water and nutrients, 34 which may decrease the performance of the host and, consequently, leading to host death. 35 The high mortality of the most abundant plant species led to a restructured woody plant 36 community. These results reinforce the importance of parasitic plants as key species for 37 maintaining species diversity in plant communities. 38 39 Key words: plant-plant interaction; parasitism; community structure, Espinhaço Mountain 40 Chain 41 42 43 44 45 46 47 48 49 2 bioRxiv preprint doi: https://doi.org/10.1101/2020.04.30.070268; this version posted April 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY 4.0 International license. 50 51 52 53 INTRODUCTION 54 Identifying the factors that control the distribution, abundance and diversity of species 55 is important to understand the structuring of ecological communities. Communities are 56 structured according to climatic and historical variations (e.g. dispersion and speciation, 57 migration and extinction), local physical conditions and interactions among species [1, 2]. 58 On a local scale, abiotic factors have an important influence on the structuring of plant 59 communities, such as the availability of water and soil nutrients [34] in addition to 60 interactions with other organisms, such as microbes and arbuscular mycorrhizal fungi [5, 6, 61 7]. In turn, the distribution of plant communities strongly affects the community structure of 62 other organisms that directly depend on them as resources, such as herbivores and parasitic 63 plants [8, 9, 10]. 64 Among parasitic plants, hemiparasites are those capable of photosynthesis, but 65 depend on their hosts for water and nutrients [11]. The susceptibility to attack by 66 hemiparasitic plants (determined by chemical, physiological and physical processes at the 67 parasite-host interface) varies between plant species, and therefore, local abundance and the 68 degree of susceptibility of plants in a community are key factors for the successful 69 colonization of hemiparasites in the environment [12, 13, 14]. In addition, the seeds of the 70 hemiparasitic plants are mostly dispersed by birds, which can lead to a differential deposition 71 of seeds on the host plants according to the preferences of the birds for certain perches [15, 72 16, 17]. Generally, larger plants with more branched tops are more attractive perches for 3 bioRxiv preprint doi: https://doi.org/10.1101/2020.04.30.070268; this version posted April 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY 4.0 International license. 73 birds, leading to a greater abundance of hemiparasitic plants on these hosts [15, 18, 16, 19, 74 20]. 75 Once the hemiparasitic plants are established, they can affect the host plant both 76 directly and indirectly [21, 22, 23, 9] and, consequently, affect the structure of plant 77 communities [14]. Directly, the hemiparasite decreases the growth and branching of the host 78 plant [23], as they obtain water and nutrients directly from the xylem, decreasing the 79 resources available for the metabolism of the host itself [11, 24, 25], which may ultimately 80 lead to death [19, 26, 9]. Indirectly, the parasite can make the host plant more susceptible to 81 attack by natural enemies [23] and to environmental stress [12, 11], which can also accelerate 82 the death of the host. Therefore, once the most abundant plant species in the environment are 83 more frequently parasitized, the hemiparasitic plant can play an important role in the 84 structuring of plant communities, since by promoting a higher mortality of individuals of 85 dominant species, it would lead to greater uniformity in the number of individuals among 86 plant species in the community [11, 27, 28, 29, 30, 31]. 87 Loranthaceae is one of the most representative families of parasitic plants in Brazil, 88 with 10 genera and approximately 100 species described [32, 14]. In the Cerrado biome, 36 89 species have been described, all of which are hemiparasites [33]. Among them, the mistletoe 90 Struthanthus flexicaulis is a common generalist hemiparasite in campos rupestres, with more 91 than 60 species recorded as hosts within at least 24 families of woody plants [25, 9]. The 92 campo rupestre ecosystem is subject to significant anthropic pressure such as mining and 93 road construction [3, 34], and in degraded areas the native pioneer shrub, Baccharis 94 dracunculifolia, whose populations form patches, often dominates the plant community [3, 95 10]. 4 bioRxiv preprint doi: https://doi.org/10.1101/2020.04.30.070268; this version posted April 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY 4.0 International license. 96 Casual observations indicated a high incidence of the mistletoe S. flexicaulis on the 97 patches of B. dracunculifolia, therefore representing an excellent experimental model to test 98 whether the plant community can be shaped by the presence of a plant parasite. This study 99 aimed to evaluate the factors related to the host plants that affect the distribution and 100 abundance of this important and widespread mistletoe, and the effects of hemiparasitism on 101 host plants in a degraded area of campo rupestre, in southeastern Brazil. We tested whether 102 the presence of the S. flexicaulis affects the structure of this community over time. First, we 103 determined the effect of the frequency and architecture of the woody host plants on parasitism 104 by S. flexicaulis. Predictions of the following hypotheses were tested: (1) More common 105 plant species in the environment are more attacked by the S. flexicaulis; (i) more abundant 106 host plants would present a greater intensity of infection (number of parasites per host) by S. 107 flexicaulis; (2) Structurally more complex host plants would be more parasitized by S. 108 flexicaulis; (i) host plants with more complex architecture (plant height and crown, number 109 of primary and secondary branches and maximum branching) would present a higher 110 intensity of infection by S. flexicaulis; (ii) Branches in greater diameter classes would be 111 more parasitized by S. flexicaulis compared with smaller diameter classes. In a second step, 112 we determined the impact of parasitism by S. flexicaulis on host plants and the woody plant 113 species community. The predictions of the following hypotheses were tested: (1) Parasitized 114 plants show lower growth and suffered higher mortality than non-parasitized plants: (i) 115 parasitized plants would show lower growth (plant height and crown, number of primary and 116 secondary branches, and maximum branching) over time compared to non-parasitized plants; 117 (ii) parasitized plants would have a higher proportion of individuals killed over time 118 compared to non-parasitized plants; (2) Parasitic plants favor the diversity of woody plants, 119 reducing the abundance of dominant species over time: (i) the dominance of species in the 5 bioRxiv preprint doi: https://doi.org/10.1101/2020.04.30.070268; this version posted April 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity.
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