Open Access

Influence of bamboo dieback on arboreal diversity in a subtropical forest fragment

  • Elivane Salete Capellesso1Email author,
  • Rafael Weirich1,
  • Giamarco Dariva1,
  • Tanise Luisa Sausen2 and
  • Elisabete Maria Zanin3
Revista Chilena de Historia Natural201689:1

DOI: 10.1186/s40693-016-0054-x

Received: 25 August 2015

Accepted: 10 February 2016

Published: 8 March 2016

Abstract

Background

The vegetation structure and dynamics in subtropical forest fragments is influenced by the bamboo density. After the reproductive events followed by the death of the bamboos, is critical to understanding community structure and regeneration processes over time. The aim of this study was to evaluate temporally the influence of height and density of Merostachys multiramea on the richness, density and diversity of tree species after the event of bamboo dieback. The study was conducted in subtropical forest in southern Brazil, characterized by intense fragmentation of habitats, which facilitates the establishment of bamboo species.

Results

We observed an increase in bamboo height over time, as well as an increase in the number of individuals between the fourth and sixth years of study. The number of M. multiramea individuals did not influence the density of regenerated individuals, but residuals analysis for estimated species richness showed the influence of bamboo on regeneration process. Six year after the bamboos death we observed a higher similarity in density of individuals between the sampling units.

Conclusions

The results of this study demonstrated distinct phytosociological structures during the different years of study, indicating that six years after the bamboos death, the vegetation structure has a higher similarity in the evaluated forest fragments in Southern Brazil, indicating a possible stabilization in the forest structure.

Keywords

Merostachys multiramea Regeneration dynamic Gaps Forest structure Seedlings

Background

In native forests, the gaps formations in the forest structure that arise from bamboo dieback characterize an environmental disturbance, which has a direct influence on the initial process of regeneration [1, 2]. Bamboo dieback is an important small-scale dynamic process in forest renovation, because it influences the germination rate, mortality and the development of forest species [3], increases tree species richness [4], and is associated with changes in environmental conditions, especially in light and temperature [5].

Merostachys multiramea Hack. is a south Brazil native species of bamboo, which displays cyclical and massive flowering every 31–33 years [6]. The last reproductive event in a subtropical forest in southern Brazil was observed between 2006 and 2008 [7]. Following bamboo dieback, the formation of gaps of different sizes was observed within the forest, which had a direct effect on the light intensity reaching the forest understory and on temperature [5], which influences the regeneration of tree seedlings [5, 8, 9].

Bamboo dieback events are responsible for alterations in the availability of resources within a few years, and they promote the development of individuals that are already established, and the establishment of new individuals in formed clearings [1, 10]. The presence of bamboo has a direct effect on the dynamics of native species [7]; furthermore, death of bamboos modifies environmental conditions and affects the process of forest regeneration [5]. Studies that have taken a temporal approach to the natural regeneration process following bamboo dieback events are extremely important to understand the processes of dynamic competition and the long-term structure of subtropical forests.

The aims of this study were to evaluate the temporal variation, and the influence of height and density of M. multiramea on the richness and density of tree species, and to monitor whether clearings influence tree regeneration and the establishment of M. multiramea. We expect that as M. multiramea increase in density and height, tree species richness decrease, creating a distinct forest structure over the years.

Methods

Study area and data collection

This study, performed in area of subtropical forests in Southern Brazil (Fig. 1), began in 2008, two years after bamboo flowering and fruiting, followed by death and fall. For the study design, 25 sampling units of 10 × 10 m were demarcated. The description of the abiotic conditions in the study areas after the M. multiramea reproductive event followed by death and fall can be found at Budke et al. [5].
Fig. 1

Location map of the study area in southern Brazil, South America

This study consisted of surveys conducted in 2008 [5], 2010 [7] and in 2012, which corresponded to two, four and six years after M. multiramea dieback occurred in 2006. All surveys evaluated tree regeneration between 30 cm to 1 m in height, including tree diameter at soil level and height. To measure the density of M. multiramea, we measured the number of individuals and their height.

Data analysis

To evaluate the differences in the bamboo density and height between years, we performed a one-way analysis of variance (ANOVA) for the individual’s number and height between years of the study, 2008, 2010 and 2012.

We obtained the structural variables of the tree regeneration component in all sample units, including individual density, species richness, Shannon diversity and Pielou equability. To evaluate the differences between years, a one-way ANOVA were performed. To assess similarity in density of individuals between sample units, we calculated the Bray-Curtis similarity index, within and between different surveys, followed by Principal Coordinate Analysis (PCoA), by visually comparing the similarity between the surveys.

The relationship between density of seedlings of tree species and that of M. multiramea Hack. was evaluated by linear regression. We used the residuals of this analysis to perform another linear regression, with species richness as the dependent variable, thus eliminating the effect of the density of tree regeneration on the observed richness. All analyses were performed using PAST [11].

Results

Relationship between plant density and the height of M. multiramea over time

The density of M. multiramea Hack. increased in the period between two and four years, followed by a decline after six years (Fig. 2), after the reproductive event. We observed differences in density between four and six years after the reproductive event. Height of M. multiramea individuals progressively increased over the time, with 2012 being significantly different from that in other years (F = 254, df = 2, p ≤ 0.001).
Fig. 2

a Density of Merostachys multiramea and b Height of Merostachys multiramea after two, four and six years of bamboo death

Temporal variation and the influence of M. multiramea richness and tree density

We observed a difference in the density of individuals of tree species after six years of study, differing from second and fourth years (Table 1). The richness of species remained stable throughout the study period. The second year of study showed a higher diversity, followed by the fourth year and the sixth year (Table 1).
Table 1

Tree species richness, density of tree seedlings, diversity and equitability observed after two, four and six years of bamboo death in a subtropical forest in Southern Brazil

 

2y

4y

6y

Species richness

56 ab

64 a

62 b

Density of tree seedlings

1446 a

1188 a

3117 b

Shannon diversity (H’)

2.61

2.42

2.13

Pielou equability (J’)

0.64

0.58

0.51

Different letters indicate differences between areas and years

We did not observe significant relationship between density of tree seedlings and density of M. multiramea Hack. (R 2  = 0.01, p = 0.53) (Fig. 3a). However, the analysis of residues revealed a positive linear relationship with the estimated species richness (R 2  = 0.17, p = 0.035) (Fig. 3b).
Fig. 3

a Regression analysis between the density of Merostachys multiramea and the density of tree seedlings; b regression analysis between their residual and species richness observed between samples units surveys conducted six years after the bamboo death

Forest structure after bamboo dieback

Six years after M. multiramea reproductive event and dieback, we observed differences between species composition and their respective density, demonstrating distinct phytosociological structures during the different years of study (Fig. 4). After two and four years of study was observed a superposition of sample units indicating a vegetation structural similarity in the 2008 and 2010 surveys after the death of M. multiramea. However, the sample units corresponding to six years were different from previous assessments (2008 and 2010) and demonstrated an overlap, indicating that in 2012, sample units have a similar vegetation structure.
Fig. 4

Principal Coordinates Analysis (PCoA) between samples units surveys of tree regeneration performed two, four and six years after the Merostachys multiramea death

Discussion

We expected that M. multiramea Hack. would show an increase in number and height of individuals, but this pattern was observed only for height throughout the study, with the number of individuals decreased over the years of the study. The vegetation structure did not change in the first four years (2010) after the death and clearing of M. multiramea, partially contradicting the hypothesis of this study. We expected that species richness would decrease with time. Differences in the composition and density of species were already observed six years after the death and clearing of bamboo (in 2012). This structural variation only in the last survey might be associated with the process of stabilization between bamboo and the forest vegetation in the study area. This hypothesis is supported by Taylor et al. [12], who state that the dead bamboo stalks remain in the area for 3–6 years, which ultimately inhibits seedling establishment. The responses of vegetation after the death and clearing of bamboo represent a continuous process and therefore, should be studied for many years [13]. Muñoz and Gonzáles [14], Montti et al. [9] and Muñoz et al. [15] observed that the positive effects of death of bamboo on tree regeneration are restricted to a short period of time, and other environmental factors might be associated with the temporal pattern of regeneration.

The height increment of bamboos might have caused partial or total closure of the gaps formed after death and clearing of bamboo, affecting light conditions and temperature, which can positively influence the regeneration process. The increased height of individuals of M. multiramea was associated with an increase in the density of regenerating tree individuals. Additionally, Campanello et al. [8] reported that woody invasion might increase after the death of bamboo, since the opening of gaps caused by bamboo dieback causes changes in the area microclimate, which plays a major role in establishment, development and reproduction in natural environments [5, 16]. However, Montti et al. [17] observed that the increase in height in two species of bamboo negatively affected the survival of tree species in the cleared areas.

The increase in the density of bamboo was directly associated with the decrease in the density and density of individual trees, due to competition with the tree species [13]. Following the decrease in the density of bamboo, tree regeneration increased, as was observed after six years of study. Species richness did not change throughout the study, similar to the findings of Montti et al. [9], studying the dynamics of Chusquea ramosissima in an Argentinian forest. Regression analysis showed no significant relationship between density of tree species and density of M. multiramea Hack. However, analysis of residual revealed a negative relationship between the density of M. multiramea and species richness, indicating an effect of bamboo on the vegetation structure.

The diversity index assessed in this study demonstrated a reduction in diversity over time, corroborating the results of Holz and Veblen [13], performed on the border between Chile and Argentina. This temporal reduction in diversity might be directly related to variations in environmental conditions associated with the gaps caused by M. multiramea dieback. Following bamboo dieback, more light can provide more suitable conditions for germination and seedling banks, maintaining their presence in the area. However, Montti et al. [17] suggest that reducing the diversity, to encourage successful growth of tree species after flowering bamboo, appears to be related to a very narrow window during which individuals that are already established can survive and use the very few resources associated with the opening of the gap.

The results of this study indicated that temporal variation in abundance and height of M. multiramea influences the vegetation structure in subtropical forest fragments, with a distinct vegetation structure over the years. The abundance and richness of tree species sampled in the first evaluations (2008 and 2010) suggests that the bamboo death provides abiotic conditions that facilitate to germination of seeds in soil bank bank and seedling establishment. Budke et al. [5], two years after the death of M. multiramea, observed a positive relationship between trees density with moisture, and negative with the opening canopy. The higher canopy openness after the death of M. multiramea was associated with the establishment, mainly of pioneer species such as Cupania vernalis Cambess., Sebastiania brasiliensis Spreng., Dalbergia frutesens (Vell.) Britton e Calyptranthes concinna DC.

Additionally, it can be inferred that the wide variation observed in the abundance of tree species between two to six years, can be associated with the presence of certain species with a high individual density, especially four years after the bamboos death. In this context there are the species Actinostemon concolor Spreng., Pilocarpus pennatifolius Lem. and Trichilia elegans A. Juss., characterized by high establishment rate in study areas and shade tolerance. Thus, similar vegetation structure observed after six years (2012) it was caused by high density of shade tolerant species, features of understory and dependent on the establishment and growth of M. multiramea individuals.

Conclusions

We can conclude that the disturbance caused by the death and clearing of bamboo, leading to the opening of gaps, is responsible for changes in the environment, and influences the growth of M. multiramea and the tree species, with a marked temporal pattern. The increase in height of individuals of M. multiramea is responsible for changes in the environmental conditions in the understory, and characterizes a process of competition for space, which does reduce the establishment of some species. However, due to a reduction in the density of bamboo over time and a consequent reduction in the competition for space, the density of regenerating individuals increases significantly, independent of the bamboo height, and is responsible for the observed differences in vegetation structure in subtropical forests dominated by bamboo.

Declarations

Acknowledgement

The authors thanks to the “Programa de Pós-Graduação em Ecologia” and to the Department of Biological Sciences of Universidade Regional Integrada do Alto Uruguai e das Missões –URI for financial support to our study.

Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.

Authors’ Affiliations

(1)
Ecology Post-Graduate Program, Universidade Regional Integrada do Alto Uruguai e das Missões – URI
(2)
Plant Ecology and Systematics Laboratory – ECOSSIS, Universidade Regional Integrada do Alto Uruguai e das Missões – URI
(3)
Geoprocessing and Environmental Planning Laboratory, Universidade Regional Integrada do Alto Uruguai e das Missões – URI

References

  1. González ME, Veblen TT, Donoso C, Valeria L. Tree regeneration responses in a lowland Nothofagus-dominated forest after bamboo dieback in south-central Chile. Plant Ecol. 2002;161:59–73.View ArticleGoogle Scholar
  2. Rother DC, Rodrigues RR, Pizo MA. Effects of bamboo stands on seed rain and seed limitation in a rainforest. Forest Ecol Manag. 2009;257:252–63.View ArticleGoogle Scholar
  3. Whitmore TC. Canopy gaps and the two major groups of forest tree. Ecology. 1989;70:536–8.View ArticleGoogle Scholar
  4. Brokaw N, Busing RT. Niche versus chance and tree diversity in forest gaps. Tree. 2000;15:375–6.Google Scholar
  5. Budke JC, Alberti MA, Zanardi C, Baratto C, Zanin EM. Bamboo dieback and tree regeneration responses in a subtropical forest of South America. Forest Ecol Manag. 2010;260:1345–9.View ArticleGoogle Scholar
  6. Schmitt R, Longhi-Wagner HM. A tribo bambuseae (Poaceae: Bambusoideae) no Rio Grande do Sul, Brasil. Braz J Biosci. 2009;7:71–128.Google Scholar
  7. Santos SC, Budke JC, Muller A. Regeneração de espécies arbóreas sob a influência de Merostachys multiramea Hack. (Poaceae) em uma floresta subtropical. Acta Bot Bras. 2012;26:252–63.View ArticleGoogle Scholar
  8. Campanello PI, Gatti MG, Ares A, Montti L, Goldstein G. Tree regeneration and microclimate in a liana and bamboo-dominated semideciduous Atlantic Forest. Forest Ecol Manag. 2007;252:108–17.View ArticleGoogle Scholar
  9. Montti L, Campanello PI, Gatti MG, Blundo C, Austin AT, Sala OE, Goldstein G. Understory bamboo flowering provides a very narrow light window of opportunity for canopy-tree recruitment in a neotropical forest of Missiones, Argentina. Forest Ecol Manag. 2011;262:1360–9.View ArticleGoogle Scholar
  10. Giordano CV, Sánchez RA, Austin AT. Gregarious bamboo flowering opens a window of opportunity for regeneration in a temperate forest of Patagonia. New Phytol. 2009;181:880–9.View ArticlePubMedGoogle Scholar
  11. Hammer Ø, Harper DAT, Ryan PD. PAST: paleontological statistics software package for education and data analysis. Palaeontol Electron. 2001;4:9.Google Scholar
  12. Taylor AH, Jinyan H, Shiquiang Z. Canopy tree development and undergrowth bamboo dynamics in old-growth Abies-Betula forests in southwestern China: a 12-year study. Forest Ecol Manag. 2004;200:347–60.View ArticleGoogle Scholar
  13. Holz CA, Veblen TT. Tree regeneration responses to Chusquea montana bamboo die-off in a subalpine Nothofagus forest in the southern Andes. J Veg Sci. 2006;17:19–28.Google Scholar
  14. Muñoz AA, Gonzáles ME. Patrones de regeneración arbórea en claros a una década de la floración y muerte masiva de Chusquea quila (Poaceae) en un remanente de bosque antiguo del valle central en el centro-sur de Chile. Rev Chil Hist Nat. 2009;82:185–98.View ArticleGoogle Scholar
  15. Muñoz AA, Gonzáles ME, Celedón C, Veblen TT. Respuesta inicial de la regeneración arbórea luego de la floración y muerte de Chusquea culeou (Poaceae) en bosques andinos del centro-sur de Chile. Bosque. 2012;33(2):153–62.View ArticleGoogle Scholar
  16. Martins SV, Rodrigues RR. Gap-phase regeneration in a semideciduous mesophytic forest, south-eastern Brazil. Plant Ecol. 2002;163:51–62.View ArticleGoogle Scholar
  17. Montti L, Villagra M, Campanello PI, Gatti MG, Goldstein G. Functional traits enhance invasiveness of bamboos over co-occurring tree saplings in the semideciduous Atlantic Forest. Acta Oecol. 2013;54:1–9.Google Scholar

Copyright

© Capellesso et al. 2016