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Caudex growth and phenology of Cyathea atrovirens (Langsd. & Fisch.) Domin (Cyatheaceae) in secondary forest, southern Brazil/Crescimento do caudice e fenologia de Cyathea atrovirens (Langsd. & Fisch.) Domin (Cyatheaceae) em floresta secundaria, no sul do Brasil.

1. Introduction

Tree ferns represent an important understory component of tropical forests (Page, 1979; Tryon and Tryon, 1982). Cyatheaceae and Dicksoniaceae encompass the vast majority of species of caudex forming ferns (Fernandes, 2003), with ca. 180 species occurring in the Neoptropics (Tryon and Tryon, 1982). Fernandes (1997) reports 20 species in south and southeastern Brazil, six of which occur in the state of Rio Grande do Sul. There are few studies on the phenology of these ferns (Mehltreter and Palacio-Rios, 2003; Mehltreter and GarcIa-Franco, 2008) and most phenological studies in this region have focussed on arboreal angiosperms (Pedroni et al., 2002). Seasonal changes in precipitation (rainfall and fog) and temperature are major factors affecting leaf development and spore production (Mehltreter, 2006). Chiou et al. (2001) and Schmitt et al. (2009) also consider the influence of the photoperiod in phenological events in ferns. The wind also can affect the phenology of plants, although mainly of those that reach the canopy (Richards, 1952). Seasonal drought and changes in water availability have been identified as the principal external factors controlling the periodic rhythms of tropical seasonal forests (Reich and Borchert 1984).

Caudex growth in arborescent ferns varies greatly between species and habitats (Arens, 2001; Schmitt and Windisch, 2007; Mehltreter and GarcIa-Franco, 2008), and some species grow faster in secondary forests than in primary ones (Bittner and Breckle, 1995). Some studies have indicated the potential for perennial development in some species, through the continued growth of the fallen caudices subsequent to their toppling (Walker and Aplet, 1994; Windisch et al., 2008).

In the Neotropics, studies including phenological data for Cyatheaceae species were presented by Mehltreter and GarcIa-Franco (2008) in Mexico; Conant (1976); Tanner (1983); Bittner and Breckle (1995) in Central America; Arens (2001) in South America; Schmitt and Windisch (2001, 2003, 2006a, b, 2007); Lehn and Leuchtenberg (2008) specifically in south Brazil. Cyathea atrovirens (Langsd. & Fisch.) Domin occurs in a wide range of habitats, in south and southeastern Brazil extending into Paraguay, Uruguay and Argentina (Ponce, 1996). In Rio Grande do Sul, this species is commonly found in swampy forests in coastal plains, and in dense forests of mountain slopes in the northeastern region (Sehnem, 1978).

Cyathea atrovirens forms caudices as high as 6 m tall, with a sheath of adventitious roots at the base (up to 25 cm in diameter). Leaves are up to 3 m long with aculeus on the petioles and abaxially on the rachises and pinna-rachises. Petioles are up to 1.10 m long and the laminas are bipinnate-pinnatifid to pinatilobate (Sehem, 1978; Fernandes, 1997). Plants are harvested for their fibrous adventitious roots which are used as substrate for the cultivation of decorative plants (Fernandes, 2000). Cut leaves are used for decoration (Tryon and Tryon, 1982) and entire plants are used in gardening.

Most of the information on Cyathea atrovirens is found in the taxonomic literature (Tryon and Tryon, 1982; Fernandes, 2000), anatomy (Sant'Anna et al., 2001) floristic studies (Sehnem, 1978; Fontana et al., 2007), and in a study of native ornamental plants (Hoehne, 1930). Spore germination and early stages of gametophytic development of C. atrovirens were studied by Rechenmacher et al. (2010). Lehn and Leuchetenberg (2008) monitored a population of C. atrovirens in an open deforested moist ravine exposed to burning, in Rio Grande do Sul. The present study of C. atrovirens aims to determine 1) caudex growth rates; 2) leaf production, expansion and senescence rates; 3) spore production and release periods; 4) the intensity of the simultaneous occurrence of each phenologic event as well as the influence of temperature, photoperiod and precipitation over it, based on the monitoring of a population in a secondary forest in southern Brazil. Considering that in southern Brazil there is no dry season, photoperiod and temperature were expected to be important abiotic factors affecting the phenology of the tree fern analysed. Such basic life history information is critical to understanding its entire life cycle and will provide the basis for plant production used in gardening.

2. Material and Methods

Study area--Field work was conducted at the Henrique LuIs Roessler Municipal Park (29[degrees]40' 54" S and 51[degrees]06' 56" W, alt. ca. 20 m), in the municipality of Novo Hamburgo, in the state of Rio Grande do Sul, Brazil. The park, of 54 ha, is located in a region previously used for agricultural purposes that now includes dry fields, wet areas and secondary forests (Weisheimer et al., 1996). Some characteristic tree species that can be cited are Schinus terebinthifolius Raddi, Myrsine coriacea (Sw.). R. Br., M. umbellate Mart., Guarea macrophylla Vahl, Psidium cattleyanum Sabine, Ocotea pulchella (Nees) Mez, Casearia sylvestris Sw. and Cupania vernalis Cambess. The reddish-brown soil consists of slightly compressed, very fine sand mixed with clay and organic matter (Weisheimer et al., 1996). The climate, according to the Koeppen classification, corresponds to the Cfa type, with the warmest month's mean temperature above 22[degrees]C (Moreno, 1961) and rainfall distributed throughout the year. In 2004 the mean annual temperature was 19.4[degrees]C and the mean of the warmest month (January) was 25.1[degrees]C. The coldest month was July (12.9[degrees]C) and the annual accumulated rainfall was 1,341 mm. Mean day length ranged from 14.01 hours in December to 10.26 hours recorded in June. During the five years covered in this study (2004 to 2009), mean annual temperature ranged from 19.3 to 20[degrees]C and rainfall from 1,098 to 1,781 mm (Figure 1).


Individual tagging--In January 2004, 50 individuals of Cyathea atrovirens were tagged using wood stakes with numbered aluminum tags placed in the soil near each plant. Plants were selected inside 32 (2 x 5 m) plots, along two transections, with 18 and 14 plots each. These plots were previously marked in a secondary forest that reached an intermediate stage of regeneration, characterised by a low canopy (less than 8 m high), near a stream crossing the park. The voucher specimen (HASU 93510) was deposited in the Herbarium Anchieta (PACA), in Sao Leopoldo, Rio Grande do Sul.

Monthly monitoring--During the first year (2004), croziers, mature (fully expanded green pinnae), fertile and senescent leaves (with all pinnae dried pinnae or only the remaining petiole bases) were counted monthly in all individuals in order to determine production and senescence rates. Young croziers were marked with plastic rings and their development was followed monthly until its total expansion in order to determine leaf growth rates. We recorded the period in which individuals had leaves with immature (green) sporangia, developed (but still closed) sporangia, until the opening stage with spore release.

Annual monitoring--To calculate the annual growth rates, plant height was measured from caudex apex to ground level in January 2004, and at intervals of 12, 24, 36, 48 and 60 months. The number of mature and fertile leaves was thereafter recorded annually.

Statistical analysis--Using the statistical program SPSS version 15.0, the Spearman post correlation test was applied to determine the relationship between number of fertile leaves with the caudex height and phenological events with temperature, photoperiod and precipitation. The synchrony of the population phenophases was measured by the synchrony index (Z) adapted from Augspurger (1983) by Pedroni et al. (2002). The synchrony is perfect when Z = 1, i.e. all individuals of the population are simultaneously in the same phenophase, while no synchrony in the population corresponds to Z = 0. Data on mean annual caudex growth rates mean number of mature and fertile leaves in January throughout the years for the five-year (2004-09) period were tested for normality and homogeneity using the Kolmogorov-Smirnov test and Levene's test. Repeated ANOVA measures were applied to compare the annual data (2004-09) meeting the normality and homogeneity assumption. Differences between annual means were verified using the multiple comparisons Bonferroni test, with a 5% significance level (Zar, 1999). Annual caudex growth rates were transformed into Ln (rate + 1) to normalise data distribution.

3. Results

Monthly monitoring--During 2004, most individuals had concomitant emergence and leaf senescence, reflected in the similar annual synchrony rates of Z = 0.65 and Z = 0.56, respectively, without total absence of leaves. Plants produced in average 8.6 [+ or -] 3.46 leaves.[year.sup.-1], ranging from 3 to 19 leaves.[year.sup.-1]. During May no leaf production was recorded. However, during spring the highest monthly means for leaf emergence were observed, with the maximum mean of 2.26 [+ or -] 1.21 leaves per plant recorded in September (Figure 2). In September and October [greater than or equal to] 84% of marked individuals produced leaves (Figure 3), with an index of synchrony higher than the annual index (Z = 0.86). Croziers (n = 29) of Cyathea atrovirens expanded faster in the first (2.53 [+ or -] 0.93 cm.[day.sup.-1]) and second (1.50 [+ or -] 0,91 cm.[day.sup.-1]) month after emergence. After the 60 days, only 15 leaves continued to increase in length, although at a slower rate (0.29 [+ or -] 0.56 cm.[day.sup.-1]). Maximum crozier expansion rate was 5.18 cm.[day.sup.-1] in the first month. One crozier during winter (August 2004), and three in summer (January 2005), died. Minimum, maximum and medium leaf length was 71, 272 and 157.36 [+ or -] 39.31 cm (n = 50), respectively. During the 12 months, the minimum and maximum numbers of leaves per sporophyte fully expanded with green pinnae (mature) were one and 16, respectively. However, plants with senescent leaves were observed during all year. Leaves senesced at a rate of 8.76 [+ or -] 4.25 leaves per plant.[year.sup.-1], ranging from 3 to 27 leaves per plant.[year.sup.-1]. In the spring, the highest monthly mean rates of senescent leaf production were observed, with a maximum mean of 2.02 [+ or -] 1.44 leaves per plant recorded in September (Figure 2). After the late winter, in September and October [greater than or equal to] 78% of the population had senescent leaves (Figure 3), with a synchrony index higher than the annual value (Z = 0.82). In September of 2004 the highest rainfall was recorded together with a higher frequency of individuals with leaf emergence (92%) and senescence (86%), although these phenological events did not correlate with precipitation in the same manner as with temperature and photoperiod (Figure 3 and Table 1).



Production of new spores occurred during all months of 2004 except July, resulting in Z = 0.66. In spring the highest frequencies of individuals producing spores (immature sporangia) was observed, reflecting an increase in the index of synchrony to 0.84 in the period from October to December 2004. In winter, on the other hand, spore production was low and, consequently, the frequency of plants with closed sporangia was also very low from August to October. Most individuals had leaves with closed sporangia during the summer (January and February), reflected by synchrony index (Z = 0.83) higher than the yearly one (Z = 0.67) and in late spring, in December 2004 (Figure 3). The frequency of individuals with immature and closed sporangia correlated positively and strongly with temperature and photoperiod (Table 1). Spore release occurred from January to December 2004, except in November. During summer (February and March), the highest frequencies of individuals releasing spores were recorded (Figure 3), resulting in a high synchrony (Z = 0.84) for the period, higher than throughout the year (Z = 0.62). Nonetheless spore release did not correlate with the climatic variables. Temperature was the single climatic variable that affected the mature and fertile leaves means per plant (Table 1). A relationship between plant height and monthly mean of fertile leaves was not observed ([r.sub.s] = 0,11; p = 0,46; n = 50). All monitored individuals were fertile with caudices at least 10 cm tall.

Annual monitoring--Monitored plants had a decreasing and statistically different sequence among them in mature leaf means from January 2004 to 2008, except from those recorded in 2007-08. Only in January 2007 and 2008 plants showed lower fertile leaf means that were significantly different from those recorded during the first year of observation. Yet, the coinciding means of mature and fertile leaves in January 2004 and January 2009 point toward the maintenance of a constant number of leaves during the monitoring period (Table 2). In average the caudices of Cyathea atrovirens grew significantly more during the first year compared to the second, third and fifth year of observation. Following this period, from the second year on, plants showed a more uniform growth, with no significant differences. The maximum growth was 10 cm.[year.sup.-1] (Table 3), recorded only in the first period (January 2004-05). During the five years of study, all individuals showed an increase in height. Individual mortality was low (4%): two dead plants in 2007 and 2008, respectively.

4. Discussion

Cyathea atrovirens had a slow and relatively constant growth under a forest canopy, following similar climatic conditions during the years of monitoring. In this study, the mean height increase rate of this species during five years was considerably lower than that recorded for other tree ferns in Rio Grande do Sul: Alsophila setosa Kaulf. (6.32 cm.[year.sup.-1]) and C. delgadii Sternb. (4.65 cm.[year.sup.-1]) by Schmitt and Windisch (2006a, 2007), growing in secondary semideciduous seasonal forest formations; and Dicksonia sellowiana Hook. (4.11 cm.[year.sup.-1]) in the contact area between seasonal semideciduous forest and mixed humid forest by Schmitt et al. (2009). Lehn and Leuchtenberger (2008) studied a population of C. atrovirens growing in a location fully exposed to sunlight after exposure to fire through the burning of the underbrush and observed a mean caudex growth of 8.4 cm.[year.sup.-1]. The ashes may have released nutrients into the soil, allowing the plants to grow faster during the year following the burn, although probably decreasing in the subsequent years. This result contrasted with our observations of slow growth, which is an example of the influence of external conditions and an intra-specific variation on growth patterns. The mean height increase rate of C. atrovirens is also significantly smaller than the values recorded for other neotropical tree ferns of this genus growing in secondary forests: C. arborea (L.) Sm. (28.6 cm.[year.sup.-1]) by Conant (1976); C. delgadii (81.9 cm.[year.sup.-1]) and C. trichiata (Maxon) Domin (89.7 cm.[year.sup.-1]) by Bittner and Breckle (1995); C. caracasana (Klotzsch) Domin (16.8 cm.[year.sup.-1]) by Arens (2001). This demonstrates the large interspecific variation in tree fern growth as already cited by Arens (2001); Schmitt and Windisch (2007). The slow growth might have been due to the proximity of the studied ferns to the stream, which usually limits the capacity of the litter to decompose and release nutrients into the soil.

Slow growth rates do not exclude the possibility of cultivation. Hoehne (1930) observed that Cyathea atrovirens is a rustic plant, with decorative leaves, easily grown even when planted in exposed sites, being able to stand direct sunlight. The species may present heliomorphic characters such as leathery shiny laminar tissue (Fernandes, 1997), adapting well to different environmental conditions. This is reflected by its wide distribution and occurrence in diverse hatitats. Furthermore, the low percentage of adults killed by natural causes, observed in the present study, indicates that individuals of this species, once established, may last for many years. Nevertheless, no information was obtained on the cultivation of C. atrovirens for commercial and landscaping projects in southern Brazil, although it is used in areas where it can be harvested in nature.

Values of annual leaf production and expansion rates for Cyathea atrovirens correspond to those recorded for other neotropical tree ferns. The highest expansion rate recorded by Shreve (1914) for C. pubescens growing in the humid mountain forests of Jamaica, comes close to the values recorded in the present study (Table 4). Different expansion rates in different stages of leaf development observed here in C. atrovirens seems to be a pattern among tree ferns in southern Brazil, which was also observed in Alsophila setosa, C. delgadii (Schmitt and Windisch 2006b, 2007) and Dicksonia sellowiana (Schmitt et al., 2009). Leaf senescence and emergence in the studied population of C. atrovirens was continuous throughout the year due to heterogeneity in individual patterns. The period of highest synchrony of these pheno logical events was during spring, thus preventing total leaf abscission. This continuous leaf phenology pattern was also observed for C. delgadii (Schmitt and Windisch, 2007) and Dicksonia sellowiana (Schmitt et al., 2009) in Rio Grande do Sul, Brazil, and for C. pubescens (Tanner, 1983), in Jamaica. Croziers, protected by a layer of light brown to ferruginous scales, were resistant to winter low temperatures and to summer heat, with one and three croziers necrosed in the cold and in the warm season of 2004, respectively. In addition to physical protection of the apical meristem, scales can moisturise the tissue by absorbing water from rain, fog or condensation while keeping humid air around the tissues (see Barrington, 1978; Tryon and Tryon, 1982).

During spring, with increased rainfall, higher temperatures and extended photoperiod, there was a higher frequency of individuals producing new and senescent leaves. Nonetheless this observation was not reflected in a correlation of leaf emergence and senescence with climatic variables. In another tree ferns species of Rio Grande do Sul, such as Cyathea delgadii (Schmitt and Windisch, 2007) and Dicksonia sellowiana (Schmitt et al., 2009) leaf production and senescence showed no relationship with precipitation, temperature or photoperiod. Precipitation affects the activity of plants in strongly seasonal forests (van Schaik et al., 1993) and although rainfall varied over the first year of this study, there was not a defined dry season. The pressure of herbivores and competition processes are some of the determinants of plant phenology in environments with less seasonal climates (Aide, 1988) that may have influenced the senescence and emergence of leaves in the studied population of C. atrovirens. Endogenous periodic processes work, primarily on the reproduction and growth of tropical plants, while the environmental changes are secondary factors of influence (Borchert, 1980).

The cold had a restrictive effect on the number of mature and fertile leaves of Cyathea atrovirens, seeing that temperature was the only variable correlated with leaf monthly means. Mean numbers of mature and fertile leaves increased slowly and gradually after a highly synchronous leaf emergence during spring, following the increase in mean monthly temperatures. Monthly mature and fertile leaf means of C. atrovirens varied slightly during the first year of observation because leaf emergence overlapped with senescence. Although periods of reduction in the annual mean of mature and fertile leaves were observed during the five years of monitoring, means for January 2004 and January 2009 were statistically equivalent. Thus it is possible that tree fern individuals can maintain a relatively stable number of leaves over a long period of time. A similar pattern was observed for a Dicksonia sellowiana population (Schmitt et al., 2009), where monthly means of mature leaves were correlated with temperature and, during a three-year period, plants maintained their number of leaves practically stable.

During the five years of monitoring, one 2 m tall plant with the maximum number of leaves (16) gradually tilted until it touched the ground and then redirected its crown of leaves vertically. This growth pattern with regeneration after toppling offers a potential for continuous growth (Windisch et al., 2008), reducing the risk of mortality of individual plants. The mantle of adventicious roots at the caudex base may partially function to provide support in the same way as the secondary structure of woody trunk in angiosperms (Ogura, 1972), although with less efficiency (Mehltreter and GarcIa-Franco, 2008).

All marked plants produced at least some fertile leaves during the study indicating that the Cyathea atrovirens population has favourable conditions for its development in the studied forest formation. However this population structure, with all (100%) individuals producing spores, is not common among tree ferns when compared with data from other studies such as Nagano and Suzuki (2007) in C. spinulosa Wall. ex Hook. (33%) from Japan; Mehltreter and GarcIa-Franco (2008) in Alsophila firma (25%) from Mexico; Schmitt and Windisch (2006b) in A. setosa (8.88%); Schmitt and Windisch (2007) in C. delgadii (9.75%) and Schmitt et al. (2009) in Dicksonia sellowiana (38%), from southern Brazil. This suggests C. atrovirens is potentially a great competitor, being able to increase population size in the study forest, where habitat conditions are not adverse. Among the four tree fern species recorded by Schmitt and Goetz (2010), C. atrovirens was the only one with generalised occurrence at Henrique LuIs Roessler Municipal Park. Page (1979) emphasized that the production of spores may be high when the plant is competing with others, and perhaps, when the group reaches maturity.

Spore production was not related to age/size of plants as we did not find a tendency in taller plants to have more fertile leaves. The lack of influence of height on the fertility of Cyathea atrovirens may be related to the fact that the population is in a secondary forest, where the scarce canopy cover provides an increase in duration and intensity of the light that reaches the understory, thus decreasing the competition for this resource.

Longer day-lengths and higher temperatures seem to promote fertility as the number of plants with immature closed sporangia increased during spring. This observation indicates a positive correlation among these climatic variables and suggests that Cyathea atrovirens might be favoured by global warming. Sato (1982) observed that lower temperatures may restrict spore production. In the present study no plants with new spores were observed during the coldest month of 2004 (July). Populations of Cibotium taiwanensis Kuo CM (Chiou et al., 2001) and Dicksonia sellowiana (Schmitt et al., 2009), growing in places where there is not a defined dry season as well, had a spore production phenology more influenced by temperature and day length than by rainfall. These two climatic variables seem more important to the phenology of plants in localities where the environment is humid throughout the year (Morellato et al., 2000). Spore release in C. atrovirens was not related to rainfall, photoperiod or temperature. Considering that spore dispersal was not limited by the climatic variables, wind might have a relation to this phenological event, although it was not investigated in this study.

Spore production and release, occurring throughout the year, even if with an inconstant frequency, increases the possibility of recruitment of new individuals in the population. This avoids the loss of the whole or most of the spore production in case of unfavorable events, also allowing a higher colonisation potential of newly exposed microhabitats (Ranal, 1995).

Acknowledgements--The authors acknowledge the support of the Federal University of Rio Grande do Sul--UFRGS, University of Novo Hamburgo--FEEVALE, University of Vale do Rio dos Sinos--UNISINOS and Brazilian Research Council--CNPq (grant to the second author). Cristina L. J. Schmitt, friends and students provided welcome help on the project activities. Dr. Joanne Sharpe kindly revised the preliminary manuscript presenting relevant comments and suggestions.


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Schmitt, JL. (a), (b) * and Windisch, PG. (b)

(a) Programa de Pos-Graduacao em Qualidade Ambiental, Laboratorio de Botanica, Universidade Feevale, Rod. RS 239, 2755, CEP 93352-000, Novo Hamburgo, RS, Brazil

(b) Programa de Pos-Graduacao em Botanica, Universidade Federal do Rio Grande do Sul--UFRGS, Av. Bento Goncalves, 9500, CEP 91501-970, Porto Alegre, RS, Brazil

* e-mail:

Received May 11, 2011--Accepted July 18, 2011--Distributed May 31, 2012 (With 3 figures)
Table 1. Spearman rank correlations (r) between phenological events
of Cyathea atrovirens and environmental variables, from January to
December 2004, in a secondary forest formation in southern Brazil.
* p < 0.05; ** p < 0.01; ns = non-significant.

Phenological events       Temperature    Precipitation   Photoperiod
                          ([degrees]C)       (mm)            (h)

Mean monthly new leaves     -0.19ns         0.29ns         0.24ns
  per plant
Mean monthly senescent      -0.15ns         0.32ns         0.32ns
  leaves per plant
Mean monthly mature          0.69 *         -0.29ns        0.28ns
  leaves per plant
Mean monthly fertile         0.64 *         -0.39ns        0.18ns
  leaves per plant
Relative frequency of        0.67 *         0.09ns         0.91 **
  individuals with
  immature sporangia
Relative frequency of       0.82 **         -0.41ns        0.63 *
  individuals with
  closed sporangia
Relative frequency of        0.35ns         -0.46ns        -0.56ns
  individuals spore

Table 2. Minimum, maximum and mean mature and fertile leaf number,
from January (2004-09) of Cyathea atrovirens in secondary forest,
southern Brazil. Means with different letters are significantly
different (Bonferroni test, [alpha] = 0.05). SD: standard deviation;
d.f.: degrees of freedom; F: value of the Snedecor distribution;
P: Probability.

                Minimum  Maximum  Mean [+ or -]   d.f.   F     P

Mature leaves
 January 2004      3       15     7.52 [+ or -]   5    13.95  <0.001
 January 2005      4       16     7.42 [+ or -]
 January 2006      3       16     6.52 [+ or -]
 January 2007      2       16     6.06 [+ or -]
 January 2008      2       11     5.73 [+ or -]
 January 2009      2       12     6.71 [+ or -]

Fertile leaves
 January 2004      0       13     6.13 [+ or -]   5     7.77  <0.001
 January 2005      0       16     6.29 [+ or -]
 January 2006      1       16     5.56 [+ or -]
 January 2007      0       16     4.77 [+ or -]
 January 2008      0       11     4.90 [+ or -]
 January 2009      0       12     6.13 [+ or -]

Table 3. Minimum, maximum and annual growth mean rate of Cyathea
atrovirens in secondary forest, southern Brazil. Means with different
letters are significantly different (Bonferroni test, [alpha] =
0.05). SD: standard deviation; d.f.: degrees of freedom; F: value of
the Snedecor distribution; P: Probability.

    Period        Minimum growth   Maximum growth
                    rate (cm.        rate (cm.
                  [year.sup.-1])   [year.sup.-1])

1[degrees] Jan.         0                10
2[degrees] Jan.         0                6
3[degrees] Jan.         0                6
4[degrees] Jan.         0                8
5[degrees] Jan.         0                8

    Period         Annual growth rate    d.f.    F       P
                    mean [+ or -] SD

1[degrees] Jan.   2.50 [+ or -] 1.94a     4     6.61   <0.001
2[degrees] Jan.   1.19 [+ or -] 1.27b
3[degrees] Jan.   1.21 [+ or -] 1.13b
4[degrees] Jan.   2.27 [+ or -] 2.29ab
5[degrees] Jan.   1.46 [+ or -] 2.08b

Table 4. Annual production and leaf expansion rates of tree ferns
from southern Brazil and other neotropical Cyathea spp.

Species                Annual leaf       Leaf expansion     Site
                     production rate       rate (cm.
                    (leaves per plant.   [day.sup.-1])

Cyathea                    5.09                --          Colombia
  caracasana (a)
Cyathea                    8.0                4.94        Jamaica
  pubescens (b,c)
Dicksonia                 10.86               3.45         Brazil
  sellowiana (d)
Cyathea                    8.6                5.18         Brazil
  atrovirens (e)
Cyathea                    5.75               6.71         Brazil
  delgadii (f)
Alsophila                  5.51               7.48         Brazil
  setosa (g)

(a) Arens, 2001; (b) Tanner, 1983; (c) Shreve, 1914; (d) Schmitt et
al., 2009; (e) present study; (f) Schmitt and Windisch, 2007; (g)
Schmitt and Windisch, 2006b
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Date:May 1, 2012
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