Upload
richard-chaca-acho
View
20
Download
1
Embed Size (px)
DESCRIPTION
Information about plant growth, developmentand age forms the basis for understanding complex forest ecological processes. Although lianas play an important role in tropical forests, little is known about their growth and development from either climatic or ecological perspectives.Therefore, we studied the growth rings inLegume liana species collected in a mountainous AtlanticForest in southeastern Brazil.
Citation preview
ORIGINAL PAPER
Dendrochronology of lianas of the Leguminosae familyfrom the Atlantic Forest, Brazil
Arno Fritz Neves Brandes • Claudio Sergio Lisi •
Claudia Franca Barros
Received: 1 November 2010 / Revised: 30 November 2010 / Accepted: 3 December 2010 / Published online: 29 December 2010
� Springer-Verlag 2010
Abstract Information about plant growth, development
and age forms the basis for understanding complex forest
ecological processes. Although lianas play an important
role in tropical forests, little is known about their growth
and development from either climatic or ecological per-
spectives. Therefore, we studied the growth rings in
Legume liana species collected in a mountainous Atlantic
Forest in southeastern Brazil. Four of the eight studied
species did not show cambial variants, three had a lobed
stem, and one had a furrowed xylem. Distinct growth rings
were observed in all species. Semi-ring porosity, marginal
parenchyma, fibrous zone and radially flattened latewood
cells were the main characteristic features of these
growth rings. Species without cambial variants, including
Dalbergia frutescens, Piptadenia adiantoides, P. micra-
cantha and Senegalia tenuifolia, showed very distinct
growth rings visible in macroscopic and microscopic anal-
ysis. Ring-width time series and cambial wound assessment
were performed to analyze periodicity and dendrochronol-
ogy. The species with cambial variants, S. grandistipula,
S. lacerans, S. martiusiana and S. pedicellata, also showed
distinct growth rings, however, sometimes barely detectable
or not detected at all. Cambial wounding, cross-dating and
climate-growth relationships indicated the annual nature of
growth rings in species without cambial variant. Cross-
dating between radii within one individual and between
individuals was successful, and the synchronized series
enabled us to build species chronologies and a mean chro-
nology. Climate-growth analysis revealed significant cor-
relations between chronologies and precipitation, indicating
that available moisture is the main factor determining
growth rates of lianas in the Atlantic forest.
Keywords Lianas � Tropics � Wood anatomy � Cambial
variants � Dendroecology � Growth rings � Leguminosae
Introduction
Lianas are an essential component of tropical forest eco-
systems. As such, lianas represent about 25% of the
abundance and species richness (Gentry 1991; Perez-Sali-
crup et al. 2004; Schnitzer and Bongers 2002). During the
past two decades awareness and interest in this growth
form have increased. However, in many respects, lianas are
still poorly understood, particularly liana ecology at the
species level and the response of lianas to the environment
(Gerwing 2004; Isnard and Silk 2009). In addition, little
attention has been given to the anatomy of lianas (Bamber
and Ter Welle 1994) and to the analysis of growth rings,
although a few older reports do exist (e.g., Schenck 1893).
So far, dendrochronological studies on lianas were devel-
oped only in temperate climate regions, especially with
Hedera helix (Garfi and Ficarrotta 2003; Heuze et al. 2009;
Nola 1997; Schnitzler and Heuze 2006; Verheyden et al.
Communicated by A. Braeuning.
Contribution to the special issue‘‘Tropical Dendroecology’’.
A. F. N. Brandes (&) � C. F. Barros
Instituto de Pesquisas Jardim Botanico do Rio de Janeiro,
Diretoria de Pesquisas, Laboratorio de Botanica Estrutural,
Rua Pacheco Leao 915, Jardim Botanico, Rio de Janeiro,
RJ 22460-030, Brazil
e-mail: [email protected]
C. S. Lisi
Departamento de Biologia, CCBS, Universidade Federal de
Sergipe, Av. Marechal Rondon s/n, Rosa Elze, Sao Cristovao,
SE 49100-000, Brazil
e-mail: [email protected]
123
Trees (2011) 25:133–144
DOI 10.1007/s00468-010-0529-3
2006), which have improved our understanding of liana–
host interactions and climate–growth relationships of liana
species. Another notable growth ring analysis in lianas was
done at the beginning of the twentieth century, and it
reported the estimated age in Clematis vitalba L. (Kann-
giesser 1906 apud Schweingruber and Poschlod 2005).
Information about growth rings in trees is available, but
it is scarce for other growth forms. Schweingruber and
Poschlod (2005) studied growth rings in herbs and shrubs,
proving the great value of dendrochronology for the tem-
poral understanding of other growth forms and for eco-
logical studies. Nonetheless, studies reporting the growth
and age of lianas are sparse, and they are mostly restricted
to indirect methods (Ewers et al. 1991; Gerwing 2004;
Nabe-Nielsen 2002; Putz 1990). Therefore, dendrochro-
nology may be a valuable tool in future research with
lianas. Specifically, growth ring analysis can contribute
chronological information that can be used for growth
analysis, wood production, population age structure and
forest dynamics, liana–host interaction, forest manage-
ment, as well as conservation and restoration studies
(Braker 2002; Brienen and Zuidema 2006; Eckstein et al.
1995; Grau et al. 2003; Jacoby 1989; Nola 1997; Priya and
Bhat 1999; Worbes 2002; Worbes et al. 2003). Still, these
analyses can only be performed for lianas if anatomical and
dendrochronological studies are also performed.
In the past few decades, many dendrochronological
studies of tropical tree species have reported the occurrence
of seasonal growth rings that are correlated, in many cases,
with precipitation or some other seasonal climatic varia-
tions (Baas and Vetter 1989; Bormann and Berlym 1981;
Eckstein and Baas 1999; Eckstein et al. 1995). In Brazil,
some studies were developed in the Amazon Forest
(Botosso 1984; Schongart et al. 2005; Schongart 2008; Vetter
and Botosso 1989; Worbes 1985, 1989) and the Atlantic
Forest biomes (Callado et al. 2001a, b, 2004; Estrada et al.
2008; Lisi et al. 2008; Oliveira et al. 2009, 2010; Seitz and
Kanninen 1989). These studies and others showed the via-
bility of growth ring research in the tropics, and an excellent
thematic overview was presented by Worbes (2002).
Lianas are woody climbers whose development begins
on the ground. However, since their ability to self-support
dissipates with growth, they need additional support in
order to ascend to the canopy and thrive in mature forests
(Gentry 1991; Gerwing et al. 2006). Most lianas show
cambial variants that are variations of cambial conforma-
tions, products and number. The most common condition
in woody species is a single and cylindrical cambium,
which produces secondary xylem (internally) and second-
ary phloem (externally) with similar amounts around stem
circumference (Carlquist 2001). Some species of lianas
do not show cambial variants (Carlquist 1991, 2001;
Caballe 1993), but frequently, such lianas do show wood
anatomical tendencies correlated to the habit, e.g., wide
vessels, higher conductive area, low proportion of sup-
portive tissues, and high amount of parenchyma (Brandes
and Barros 2008; Carlquist 1991). Only a few papers have
reported the growth ring anatomy of lianas (Baas and
Schweingruber 1987; Carlquist 1995; Gasson and Dobbins
1991; Lima et al. 2010; Schweingruber 2007).
Leguminosae are the third largest family of climbers in the
New World. Additionally, along with Bignoniaceae, they
represent the dominant climbing families in Neotropical
lowland forests (Gentry 1991). Lianas compete with trees for
nutrients, light and water (Gentry 1991). As a consequence of
their thin stems and low-density wood, lianas capture less
carbon than tree species. Moreover, infestations of lianas
inhibit the regeneration of forest trees which also reduces the
amount of carbon that would otherwise be assimilated in the
biomass (Schnitzer and Bongers 2002).
In this study, we analyzed eight liana species from a
well-preserved remnant of the Atlantic Forest located in a
mountainous region (Serra da Mantiqueira–Itatiaia Massif).
These species represent almost all legume lianas previously
recorded in this place and registered in the Programa Mata
Atlantica database. In the course of our study, we asked (1)
if Atlantic Forest lianas have growth rings, (2) what ana-
tomical features distinguish such growth rings, (3) what
periodicity applies to the formation of growth rings, and (4)
whether ring-width patterns reflect precipitation variations.
Materials and methods
Study site
The samples were collected from the Parque Nacional do
Itatiaia, municipality of Itatiaia, State of Rio de Janeiro,
southeastern Brazil. The park is located between the geo-
graphical coordinates of 22�150–22�300 S and 44�300–44�450 W, with an area of 28,155.97 ha (Morim 2006). Its
type of vegetation can be classified as Atlantic Forest
(Oliveira-Filho and Fontes 2000). Most of the Parque
Nacional do Itatiaia lies in a mountainous area with several
well-delimited climatic and vegetation belts related to
altitudinal gradients. The samples were taken between 700
and 1,100 m elevation. At 816 m elevation, the annual
mean precipitation is around 1,700 mm, and the annual
mean temperature is 18.2�C. The warm and rainy season is
between December and February, when 50% of the annual
precipitation occurs. January is the rainiest month, with a
mean of 290 mm. During these months, the mean tem-
perature is 20.8�C. The dry cold season is between June
and August, with only 5% of the annual precipitation. The
driest month is June, with a mean of 32 mm. During these
months, the mean temperature is 15.1�C, but an absolute
134 Trees (2011) 25:133–144
123
minimum of 0�C has been registered (Segadas-Vianna and
Dau 1965).
The precipitation data used in our dendrochronological
analysis were collected during 1986–2005 at the meteoro-
logical station of Resende (22� 270 S, 44� 260 W) and were
provided by the Instituto Nacional de Meteorologia
(INMET) (National Institute of Meteorology)—Sixth Meteo-
rological District (Fig. 1). The meteorological station of
Resende is 453 m elevation, around 18 km distance from
study site, and the precipitation data are very similar of study
site (Segadas-Vianna and Dau 1965).
Wood anatomy
We sampled 57 lianas from eight Leguminosae species
(subfamilies Mimosoideae and Papilionoideae). Of these,
four had cambial variants and four did not. The cambial
variants that occur in these species are the non-fragmented
lobed stem and the xylem-furrowed stem (Brandes and
Barros 2008) (Table 1). Both are products of a single
cambium with unequal activity on some regions (Carlquist
2001).
For this study, we selected lianas larger than 2.0 cm in
diameter at approximately 1.3 m above the ground, without
wounds or deformations at this height. The number of
samples per species differed because of the difficulty in
finding individuals with the characteristics cited above and
the different abundance of each species. For each indi-
vidual sampled, a voucher was collected, representing
reproductive and other vegetative parts as well. They were
stored at the herbarium Jardim Botanico do Rio de Janeiro
(RB).
Wood samples of the stems were collected at approxi-
mately 1.3 m above the ground. We collected partial or
complete cross-sections, including bark, wood and pith.
Blocks were polished for macroscopic observation through
an Olympus SZ11 stereomicroscope. The images were
taken by a photographic camera (Olympus C5050) attached
to the same stereomicroscope and analyzed with Image Pro
Plus version 3.0 for Windows. For light microscopy,
boiling water and glycerine were used to soften part of the
blocks; 12 to 30 lm-thick sections were made in trans-
versal, tangential and radial plains, using a Spencer 860
sliding microtome. After cleaning, they were stained with
safranin and astra blue (Bukatsch 1972), dehydrated,
and mounted on Permount resin in permanent slides.
Slides were observed using an Olympus BX50 microscope,
and images were captured with Image Pro Plus version 3.0
for Windows linked to the microscope through a Media
Cybernetics CoolSNAP-Pro video camera. The Zeiss
0
25
50
75
100
125
150
0
50
100
150
200
250
300
JAN
FE
B
MA
R
AP
R
MA
Y
JUN
JUL
AU
G
SE
P
OC
T
NO
V
DE
C
Tem
pera
ture
(C
)
Pre
cipi
tatio
n (m
m)
°
Fig. 1 Mean (1986–2005) monthly precipitation (bars) and temper-
ature (line) for Resende-RJ Meteorological Station
Table 1 Studied species, anatomical features of the growth rings, cambial variant types, analyzed samples RBw
Species Anatomical features
of growth rings
Cambial
variants
Samples RBw
Mimosoideae
Senegalia grandistipula 1a, 3a, 4a, 5a Lobed stem 8,627, 8,643, 8,644
Senegalia lacerans 1a, 2a, 3a, 4a, 5a Xylem furrowed 8,607, 8,608, 8,610, 8,611, 8,612, 8,624, 8,625,
8,629, 8,631, 8,641, 8,642
Senegalia martiusiana 1a, 3a, 5a Lobed stem 8,653, 8,655, 8,656, 8,657, 8,659, 8,660, 8,661
Senegalia pedicellata 1a, 3a, 5a Lobed stem 8,609, 8,615, 8,662, 8,663, 8,664
Senegalia tenuifolia 1, 2, 3a, 4a Absent 8,628, 8,658
Piptadenia adiantoides 1a, 2, 3a, 4 Absent 8,634, 8,635, 8,636, 8,646, 8,647, 8,648, 8,652
Piptadenia micracantha 1, 2, 3, 4a Absent 8,605, 8,632, 8,637, 8,645, 8,650, 8,651, 8,654
Papilionoideae
Dalbergia frutescens 1, 2, 3a, 4a Absent 8,606, 8,613, 8,614, 8,616, 8,617, 8,618, 8,619,
8,620, 8,621, 8,622, 8,623, 8,626, 8,630, 8,633, 8,649
1 semi-ring-porous, 2 marginal parenchyma, 3 fiber zone, 4 radially flattened latewood cells, 5 pith fleck and traumatic canalsa Features not present in all growth rings
Trees (2011) 25:133–144 135
123
polarized light microscope with red filter k was also used to
observe calcium oxalate crystals.
Wood samples and permanent slides were incorporated
into the wood collection from the Jardim Botanico do Rio
de Janeiro (RBw). The terminology complies with the
IAWA Committee (1989).
Cambial wounding
The technique of repeated wounding of the vascular cam-
bium, the so-called ‘‘Mariaux Window’’ (Mariaux 1967),
was used to analyze the characteristics of the secondary
xylem produced during the year, as well as confirm the
presence of annual growth rings. In the procedure, the bark
and the cambium at 0.5 cm in width and approximately
5 cm in height were removed, and a Bordeaux mixture was
applied to avoid the action of pathogenic microorganisms.
Four markings were performed throughout the year (one in
each season), and 1 year after the first wound, a section of
the area appointed for analysis was collected. Fifteen
individuals of Dalbergia frutescens, seven Piptadenia
adiantoides, seven Piptadenia micracantha, and two
Senegalia tenuifolia were analyzed.
Dendrochronology
For dendrochronological studies, samples of 29 lianas from
Piptadenia adiantoides, Piptadenia micracantha, and
Dalbergia frutescens species were analyzed (Table 2).
Senegalia tenuifolia, one species that shows a distinctive
growth ring, was not used because we could not find
enough specimens to study.
Four rays (temporal series) were measured per liana.
Growth ring measurements and image processing were
performed with Image Pro Plus version 3.0 for Windows,
with a precision of 0.01 mm. The cross-dating of the
temporal series was performed, following the recom-
mendations of Stokes and Smiley (1996) and Fritts (1976)
and was supported by graphs and statistical analysis. The
COFECHA (Holmes 1983) program was used to verify
the precision of the measurements and the cross-dating.
The growth ring series was standardized (de-trended)
using a spline curve (cubic smoothing spline 50%
wavelength cutoff; 5 years rigidity of spline for filtering).
A flexible spline was used to minimize undesirable signal
(e.g., competition and local disturbance). The flexible
spline is an appropriate de-trending method for trees from
closed-canopy stands, as previously reported (Brienen and
Zuidema 2005; Cook and Peters 1981), and it may also
be applicable to lianas, taking into account ecological
conditions. For each of these species, a reference, or
master, chronology was produced, calculating the mean
value of all standardized series (de-trended series). Each
temporal series was tested in relation to the reference
chronology. A final growth ring chronology was produced
for each species by averaging the best correlated series.
Successful cross-dating indicates the influence of an
external growth factor on tree growth in a region. By
identifying the common signal that represents the climatic
factor in a growth rings time series, it is possible to retain
the highly correlated series in the final chronologies.
Finally, a mean reference chronology (master chronology)
of lianas from the Parque Nacional de Itatiaia was pro-
duced from the species chronologies. For the time series
analysis and building the chronologies, software from the
Dendrochronology Program Library (Holmes 1994) was
used.
Pearson correlation analyses were performed between
the chronologies produced and annual precipitation (Janu-
ary–December), monthly precipitation and the precipitation
total of December–January–February (summer), March–
April–May (autumn), June–July–August (winter), and
September–October–November (spring). The correlation
analyses were executed using Statistica 8.0 software.
Correlation analysis is also the most common method to
measure the association between growth rings and climate
(Fritts 1976). The methods described above for the treat-
ment and analysis of data are an attempt to follow the
Table 2 Ring-width data
Chronology Number
of lianas
Number
of series
Intercorrelation Sensitivity Chronology
extension
Samples RBw
Mimosoideae
Piptadenia adiantoides 7 (7) 28 (21) 0.69 0.57 1993–2005 8,634, 8,635, 8,636, 8,646, 8,647, 8,648, 8,652
Piptadeniamicracantha
7 (6) 28 (14) 0.48 0.37 1987–2005 8,605, 8,632, 8,637, 8,645, 8,650, 8,651, 8,654
Papilionoideae
Dalbergia frutescens 15 (15) 60 (37) 0.50 0.51 1970–2005 8,606, 8,613, 8,614, 8,616, 8,617, 8,618, 8,619, 8,620,
8,621, 8,622, 8,623, 8,626, 8,630, 8,633, 8,649
Species, number of lianas before and after cross-dating (), number of series before and after cross-dating (), intercorrelation, sensitivity,
chronology extension, and analyzed samples RBw
136 Trees (2011) 25:133–144
123
methodological steps recommended by Braker (2002)
which visualize, explore, test, and relate data.
Results
Wood anatomy
Distinct growth rings were observed in all studied species.
The four species without cambial variants revealed easily
detectable and well-delimited growth rings (Figs. 2a–d,
3a–d). Anatomical ring boundaries of species with cambial
variants were sometimes detectable, sometimes barely
detectable rings or even undetectable (Figs. 4a–d, 5a–d).
The most evident anatomical features of growth rings were
semi-ring porosity, fibrous zones, marginal parenchyma
bands, and radially flattened latewood cells. Species with
cambial variants also exhibited traumatic canals and pith
flecks within the growth boundaries. The features listed
above were not present concomitantly in all growth rings
(Table 1). In combination, the macroscopic and micro-
scopic observations enabled a proper distinction of growth
rings. Usually, the macroscopic view facilitated the
detection of growth ring boundaries because of a broader
field view.
Among the species without cambial variants, Dalbergia
frutescens (Vell.) Britton var. frutescens (subfamiliy Pap-
illionideae) (Figs. 2a, 3d), P. adiantoides (Spreng.) J. F.
Macbr. (Figs. 2b, 3b), P. micracantha Benth. (Figs. 2c, 3c)
and Senegalia tenuifolia (L.) Britton and Rose (subfamily
Mimosoideae) (Figs. 2d, 3a) exhibited semi-ring porosity,
marginal parenchyma, fibrous zones in latewood, and
radially flattened latewood cells. However, a fibrous zone
and radially flattened latewood cells were not present in all
growth rings of D. frutescens (Figs. 2a, 3d) and S. tenui-
folia (Figs. 2d, 3a). Within P. adiantoides (Figs. 2b, 3b)
some growth rings did not present semi-ring porosity and
fiber zone. In P. micracantha (Figs. 2c, 3c) few growth
rings showed radially flattened latewood cells. Abundance
of prismatic calcium oxalate crystals was observed near
growth ring boundaries of all Mimosoideae without cam-
bial variants.
The other studied species of genus Senegalia revealed
cambial variants. Although all species exhibit distinct
growth ring boundaries, they are sometimes difficult to
detect or, in some stem portions, even undetectable. The
main distinctive features of growth rings for this genus
included semi-ring porosity and fibrous zone. S. grandi-
stipula (Benth.) Seigler and Ebinger revealed a square-like
lobed stem cambial variant. In addition to the features
mentioned above, some growth rings had radially flattened
latewood cells, pith flecks and traumatic canals (Figs. 4a, 5a).
S. lacerans (Benth.) Seigler and Ebinger showed a
xylem-furrowed cambial variant. Beyond the features for
genus, some growth rings had marginal parenchyma,
radially flattened latewood cells, pith flecks and traumatic
canals (Figs. 4c, 5b). S. martiusiana (Steud.) Seigler and
Ebinger, a lobed stem cambial variant with cylindrical
lobes, presented the features cited above for the genus,
including pith flecks and traumatic canals (Figs. 4d, 5c).
Finally, S. pedicellata (Benth.) Seigler and Ebinger, a
lobed stem cambial variant with flattened lobes, showed
pith flecks and traumatic canals (Figs. 4b, 5d). Occasion-
ally, semi-ring porosity and fibrous zone were also
presented.
Cambial wounding
The four studied species showed a clear periodicity in
radial growth, with the formation of one growth ring per
year. At the beginning of the rainy season in September,
the cambium produced large vessels. As the dry season
approached, vessels with gradually smaller diameters were
Fig. 2 Transverse sections (light microscopy) of a D. frutescens,
b P. adiantoides, c P. micracantha, d S. tenuifolia. Arrows indicate
growth ring boundaries, scale bars 100 lm
Trees (2011) 25:133–144 137
123
produced (Fig. 6a–d). Through the experimental delinea-
tion employed, it was not possible to determine whether the
vascular cambium became inactive for a determined
period; however, we noticed that the products of the vas-
cular cambium (cells composing the secondary xylem) and
the size of these cells varied throughout the year.
Dendroecology
All studied species included discontinuous rings (wedging
rings), which may cause serious difficulties for proper syn-
chronization between tree-ring series. Since we mainly used
complete or partial sections of liana stems and not samples
collected with an increment borer, it was possible to validate
the cross-dating of radii and to identify discontinuous rings
with a certain ease and precision. Both, graphical analysis
and statistics provided by COFECHA software were very
important to synchronize the measured growth ring series.
Thus, the cross-dating procedure was successful between
most radii and individuals, as indicated by a high intercorre-
lation between the tree-ring series of 0.69 for P. adiantoides,
0.50 for D. frutescens and 0.48 for P. micracantha (Table 2),
for which three growth ring chronologies were produced
(Fig. 7). The mean sensitivity was 0.57 in P. adiantoides, 0.51
in D. frutescens and 0.37 in P. micracantha (Table 2),
revealing a high inter-annual growth variability that might be
related to climate sensitivity (Fritts 1976). Finally, a mean
chronology of lianas from Itatiaia was built by averaging the
three individual species chronologies (Fig. 7d).
Correlation analysis between the individual species
chronologies and total annual precipitation revealed sig-
nificant correlation coefficients for D. frutescens (r = 0.63;
p = 0.003), P. adiantoides (r = 0.53; p = 0.062) and
P. micracantha (r = 0.39; p = 0.096), respectively. The
correlation between the mean chronology of lianas from
Itatiaia and total annual precipitation was even higher than
Fig. 3 Transverse sections
(stereomicroscopy) of
a S. tenuifolia, b P. adiantoides,
c P. micracantha,
d D. frutescens. Arrows indicate
growth ring boundaries, scalebars 1 mm
Fig. 4 Transverse sections (light microscopy) of a S. grandistipula,
b S. pedicellata, c S. lacerans, d S. martiusiana. Arrows indicate
growth ring boundaries, scale bars 100 lm
138 Trees (2011) 25:133–144
123
that found for the individual species (r = 0.66; p = 0.001)
(Table 3, Fig. 7).
Highest correlation coefficients of the chronologies with
monthly and seasonal precipitation were generally
observed for the summer months of the previous growing
season and the spring months of the current growing sea-
son. Lowest correlations were observed for autumn and
winter, except for P. micracantha. The P. adiantoides
chronology was significantly correlated with precipitation
of February of the previous growing season, October of the
current season, and summer of the previous growing season
(Table 3). For D. frutescens, positive correlations occurred
with January of the previous growing season, September of
the current season, and summer of the previous growing
season. In contrast to these species, growth of P. micra-
cantha was positively correlated with June and July of the
previous growing season, winter of the previous growing
season and May of the current growing season (Table 3,
Fig. 7).
Discussion and conclusions
The anatomical results demonstrate that P. micracantha,
P. adiantoides, S. tenuifolia and D. frutescens form clear
annual rings, which is fundamental for precise ring counting
and ring-width measurements. In contrast, Senegalia gran-
distipula, S. lacerans, S. martiusiana and S. pedicellata are
species with cambial variants that may form distinct growth
rings, which are sometimes indistinct and difficult to detect
or absent in some stem portions. Beyond that, species which
show lobate growth should not be used in an analysis of
growth rings (Worbes 1989). Growth rings were detected in
other liana species, but they were rarely analyzed in detail.
Baas and Schweingruber (1987) observed that climbers from
temperate climates show ring porous and semi-ring porous
wood anatomy. Other examples of lianas with distinct
growth rings from temperate and tropical regions were pre-
sented by Schweingruber (2007). Gasson and Dobbins
(1991) report distinct growth rings in lianas from the genera
Capsis, Schlegelia nine other genera of the Bignociaceae
family. A detailed description of growth rings in tropical
lianas from the Bignonieae tribe was provided by Lima et al.
(2010). In lianas from Venezuela, growth rings marked by
marginal parenchyma were observed in Anomospermun
schomburgkii Miers (Menispermaceae) and Strycnos
brachistantha Standley (Loganiaceae) (Araque et al. 2000).
The main anatomical markers for growth rings observed by
these authors were semi-ring porosity, parenchyma bands,
radially flattened latewood fibers and radially shorter ray
cells. Semi-ring porosity and marginal parenchyma were
also important features observed in the present study. They
were present in all studied species without cambial variants
and having a distinct growth ring. These studies show that
growth rings in lianas are not exceptional and have common
anatomical features.
Based on the evidence from wood anatomy, vascular
cambium wounds (Worbes 1995), cross-dating, intercor-
relation between ring-width time series, correlations
between chronologies and precipitation data (Stahle 1999),
as well as the seasonal rainfall regime of the study area, we
conclude that growth rings of the studied species are
formed annually. According to Worbes (1995), areas with a
dry season of 3 months or more with a monthly precipi-
tation below 60 mm are favorable for the occurrence of
species that form annual growth rings. This holds true for
Fig. 5 Transverse sections
(stereomicroscopy) of
a S. grandistipula,
b S. lacerans, c S. martiusiana,
d S. pedicellata. Arrowsindicate growth ring boundaries,
scale bars 1 mm
Trees (2011) 25:133–144 139
123
the Parque Nacional do Itatiaia, where the dry season lasts
3 months. Supporting this evidence, Schweingruber (2007)
reported growth rings in tropical lianas from seasonal cli-
mates. The occurrence of annual growth rings and annual
growth seasonality was also reported in arboreal species
from the Atlantic Forest (Callado et al. 2001b; Estrada
et al. 2008; Lisi et al. 2008; Oliveira et al. 2009, 2010), in
lianas from the Atlantic Forest of the Bignoniaceae family
(Lima et al. 2010) and in lianas of the Leguminosae from a
Mexican tropical rainforest (Leon-Gomez and Monroy-Ata
2005).
The successful cross-dating and the high intercorrelation
values between ring-width series showed that liana species
of this study share a common growth pattern and respond
to a common environmental signal. Importantly, the den-
drochronological results suggest that the growth of tropical
lianas is sensitive to variations in local climate. Specifi-
cally, positive correlations between the chronologies and
annual, monthly and seasonal precipitation were observed.
Strongest relationships were observed between chronolo-
gies and annual precipitation. Precipitation was also
reported as the most important factor for the secondary
growth of tropical tree species (Worbes 1989). Schongart
et al. (2006) studied six arboreal species in Africa, among
them four species of the Leguminosae family and observed
significant correlations (p \ 0.01) between growth rates
and annual precipitation. In a tropical dry forest in Costa
Rica, Enquist and Leffler (2001) observed a significant
relationship between growth of the evergreen Capparis
indica and annual precipitation. Fichtler et al. (2004)
studied two leguminous species from a semiarid forest in
Namibia and found a positive relationship between a
Burkea africana chronology and the rainfall total of all
months to the growth year (August–July). Worbes (1999)
studied several species in Venezuela and detected a high
correlation coefficient (r = 0.75; p \ 0.05) of annual pre-
cipitation with the mean chronology of all studied species.
Besides, significant correlations of 0.62 (p \ 0.05) and
0.68 (p \ 0.05) between chronologies of Cedrela odorata
and Terminalia guianensis and annual rainfall were found.
Similar to these reports, the present study demonstrates that
a mean chronology of several species shows a higher
relationship to annual precipitation than chronologies of
individual species.
Climate during certain periods of the year may have a
greater influence on growth than during other periods
(Fritts 1976). For example, D. frutescens and P. adianto-
ides show significant correlations with precipitation during
summer of the previous growing season and with some
spring months of the current growing season. On the other
hand, P. micracantha shows significant correlations with
precipitation in winter of the previous growing season.
Thus, in some of the studies noted above, a controversial
picture arises with correlation between growth and pre-
cipitation between dry and rainy seasons, as well as with
transitional months.
Brienen and Zuidema (2005) related tree growth in a
Bolivian rain forest with rainfall. While they did not find
any correlation between chronologies and annual precipi-
tation, they documented a positive relationship between
tree growth and precipitation during certain periods of the
year. Three species showed a relationship to precipitation
at the beginning of the rainy season, one species with
precipitation in the transition from the rainy to the dry
Fig. 6 Macroscopic cross-sections of cambial wounds set in Decem-
ber 2005. Collection of the samples was conducted after 1 year
(December 2006). a S. tenuifolia, b P. adiantoides, c P. micracantha,
d D. frutescens. Scale bars 1 mm
140 Trees (2011) 25:133–144
123
season, and two species were correlated with precipitation
in the transition period from dry to rainy. Dunisch et al.
(2003) observed the highest correlation coefficients of
Swietenia macrophylla with rainfall in November,
December, January and May, and in Cedrela odorata in
March, April and May, and rainy months of the previous
growth period. Fichtler et al. (2004) studied the leguminous
trees Burkea africana and Pterocarpus angolensis in
Namibia. P. angolensis from Katima Mulilo was highly
correlated to rainfall in April and total precipitation of
April and May, the beginning of the dry season. The
chronology B. africana from Ondangwa responded to
rainfall in January and February, the rainy season, and the
chronology from Katima Mulilo responded to rainfall of
August, September and November, the end of dry season,
as well as the total rainfall for October and November, the
beginning of the rainy season. Eshete and Stahl (1999)
observed high correlations in Acacia species with precipi-
tation total from June to September, the rainy season. In
Venezuela, Worbes (1999) noticed significant correlations
between dry season precipitation and five species and
between rainy season precipitation and four species stud-
ied. Two of these species showed correlations with both the
dry season and rainy season rainfall. Enquist and Leffler
(2001) noticed correlations of growth of Genipa americana
with the precipitation of the dry season and of Capparis
indica with the rainy season of the previous year. The
different reaction pattern of the two species is explained by
individualistic response and differences in the root system.
Regarding lianas, Lima et al. (2010) detect cambial activity
in Tynanthus cognatus (Bignoniaceae) only at the end of
the rainy season. To summarize, precipitation is an
important climatic factor related to the growth of woody
species in the tropics, being it trees or lianas. Moreover, it
50
150
250
350
450
- 4
- 3
- 2
- 1
0
1
2
3
Pre
cipi
tatio
n (m
m)
Inde
xed
ring
wid
th
P. adiantoides February precipitation
0
10
20
30
1970
1972
1974
1976
1978
1980
1982
1984
1986
1988
1990
1992
1994
1996
1998
2000
2002
2004S
ampl
ing
dept
h
Year
500
1000
1500
2000
2500
-4
-3
-2
-1
0
1
2
Pre
cipi
tatio
n (m
m)
Inde
xed
ring
wid
th
Lianas Itatiaia Total annual precipitation
020406080
1970
1972
1974
1976
1978
1980
1982
1984
1986
1988
1990
1992
1994
1996
1998
2000
2002
2004S
ampl
ing
dept
h
Year
0
50
100
150
200
250
- 4
- 3
- 2
- 1
0
1
2
3
Pre
cipi
tatio
n (m
m)
Inde
xed
ring
wid
th
P. micracantha Winter precipitation
0
10
20
1970
1972
1974
1976
1978
1980
1982
1984
1986
1988
1990
1992
1994
1996
1998
2000
2002
2004S
ampl
ing
dept
h
Year
500
1000
1500
2000
2500
- 4
- 3
- 2
- 1
0
1
2
Pre
cipi
tatio
n (m
m)
Inde
xed
ring
wid
th
D. frutescens Total annual precipitation
010203040
1970
1972
1974
1976
1978
1980
1982
1984
1986
1988
1990
1992
1994
1996
1998
2000
2002
2004S
ampl
ing
dept
h
Year
a b
c d
Fig. 7 Ring-width chronologies and their sampling depth and
comparison with precipitation. a D. frutescens and total annual
precipitation, b P. adiantoides and February precipitation,
c P. micracantha and winter precipitation, d Mean chronology of
lianas from Itatiaia and total annual precipitation
Trees (2011) 25:133–144 141
123
appears that growth can be related to precipitation of either
a short period (seasons or months) or a long period (year).
In an interesting study about the abundance patterns of
lianas, Schnitzer (2005) found that lianas are more abun-
dant in dry seasonal forests. He suggested that lianas can
maintain their growth activity during the dry season, by
gathering enough water resources with their deep roots to
continue their photosynthesis and growth. Thus, lianas
confer an adaptive advantage over trees. This community-
level explanation can be supported by our results for
P. micracantha. At the same time, however, the present study
shows that the growth of D. frutescens and P. adiantoides is
confined mostly to the rainy season. These results corroborate
Enquist and Leffler’s (2001) hypothesis of individualistic
response to climate, as well as the idea that some tropical
assemblages may in fact be structured by species-specific
differences in soil–water use.
It is possible that lianas respond well to precipitation
variations, as a result of their peculiarities regarding the
conduction of sap in the xylem. In lianas, vessels of large
diameter are a common feature (Carlquist 1985; Ewers
et al. 1990; Ewers et al. 1991), which is also a character-
istic in the species of this study (Brandes and Barros 2008).
The large liana vessels are more susceptible to embolism
during the dry season than vessels of smaller diameter
(Zimmermann 1983). During the dry season, drought-
sensitive species show a reduction in their growth in
comparison with drought-tolerant species, and in the rainy
season, they show an increase in growth. Thus, it is
expected that drought-sensitive species show a better
correlation with climatic parameters, especially during the
rainy season (Gebrekirstos et al. 2008). While precipitation
is an important factor for the secondary growth of liana
species, other environmental factors, such as temperature,
solar radiation, day length and phenological phases, may
also influence the formation of growth rings (Callado et al.
2001b; Clark and Clark 1994; Devall et al. 1995; Oliveira
et al. 2009, 2010; Schweingruber 2007). Their relevance
for controlling growth rings in lianas has to be tested in
further studies.
In this study, wedging rings were detected in all species
during the cross-dating procedure of time series of radial
growth series within individuals. The analysis of stem discs
facilitated the detection of problematic growth rings
(Worbes 1999). Absent and wedging rings may lead to age
underestimation and hence growth overestimation (Lorimer
et al. 1999). The presence of wedging rings was reported
from several neotropical arboreal species, and it was
observed that they are more common in small understory
trees growing under competition with diminished light
conditions (Lorimer et al. 1999; Worbes 2002). Ecological
studies on lianas report a strong competition pressure with
trees for nutrients, light, and water during the dry season
(Schnitzer and Bongers 2002). The presence of wedging
rings documented in our study reinforces the idea that
lianas are subject to competition processes which may
initiate alterations of cambial activity in determined stem
regions.
Thus, we conclude that the lianas studied do have growth
rings, detectable by wood anatomical features like semi-ring
Table 3 Correlation coefficients between chronologies and monthly precipitation (Jan–Aug previous growing season; Sep–Jun current growing
season), total precipitation in summer (SUM), autumn (AUT), winter (WIN), spring (SPR) and total annual precipitation (TAP)
Previous growing season
Jan Feb Mar Apr May Jun Jul Aug
Piptadeniaadiantoides
0.33 0.57 -0.18 -0.21 0.11 -0.24 0.34 -0.12
Piptadeniamicracantha
0.36 0.12 0.14 0.27 -0.24 0.56 0.52 -0.16
Dalbergiafrutescens
0.51 0.37 -0.06 0.11 0.30 0.05 -0.01 -0.41
Lianas Itatiaia 0.56 0.31 -0.03 0.21 0.06 0.32 0.31 -0.36
Current growing season
Sep Oct Nov Dec Jan Feb Mar Apr May Jun SUM AUT WIN SPR TAP
Piptadenia adiantoides 0.32 0.53 -0.21 0.42 -0.24 -0.28 0.43 0.50 -0.32 0.11 0.52 -0.21 0.04 0.28 0.53
Piptadenia micracantha 0.17 -0.44 -0.06 0.34 -0.32 -0.30 -0.03 0.07 0.45 -0.41 0.13 0.25 0.54 -0.17 0.39
Dalbergia frutescens 0.55 0.11 0.22 0.00 -0.18 -0.28 0.32 -0.11 -0.57 -0.01 0.58 0.12 -0.25 0.38 0.63
Lianas Itatiaia 0.49 0.01 0.05 0.17 -0.37 -0.34 0.24 -0.02 -0.16 0.25 0.50 0.15 0.12 0.21 0.66
Significant correlations: Italic value p \ 0.08; Bold value p \ 0.05; Bold italic value p \ 0.005
142 Trees (2011) 25:133–144
123
porosity, fibrous zone, marginal parenchyma and radially
flattened latewood cells. The four species without cambial
variants had well-delimited growth rings, which were easily
detectable. The periodicity of growth ring formation and
correlation of ring-width time series proved the annual nat-
ure of their growth rings. Climate-growth analyses revealed
that growth is conditioned by precipitation. Future ecologi-
cal studies, particularly dendroecological studies, will be an
important source of information about the role played by
lianas in the Atlantic Forest of Brazil and in other tropical
forest ecosystems.
Acknowledgments Our thanks go to the Instituto de Pesquisas
Jardim Botanico do Rio de Janeiro, Petrobras and CAPES (Coorde-
nacao de Aperfeicoamento de Pessoal de Nıvel Superior) for financial
support; Parque Nacional do Itatiaia for logistical support and Dr.
Achim Braeuning for the revision of the paper and valuable sugges-
tions and comments.
References
Araque OZ, De Pernıa NE, Leon WJ (2000) Estudio anatomico del
leno de seis especies de lianas. Rev For Venez 44:39–48
Baas P, Schweingruber FH (1987) Ecological trends in the wood
anatomy of trees, shrubs and climbers from Europe. IAWA Bull
8:245–274
Baas P, Vetter RE (1989) Growth rings in tropical trees. IAWA Bull
N. ser. 10:95–174
Bamber RK, Ter Welle BJH (1994) Adaptative trends in the wood
anatomy of lianas. In: Iqbal M (ed) Growth patterns in vascular
plants. Dioscorides Press, Portland, pp 272–287
Bormann FH, Berlym G (1981) Age and growth of tropical trees: new
directions for research. Yale Univ Sch For Eviron Stud Bull
94:1–137
Botosso PC (1984) Some anatomical wood characteristics as
source of cyclic structural change (regular or irregular) of
growth periodicity for 20 amazonian species. IAWA Bull
5:545–546
Braker OU (2002) Measuring and data processing in tree-ring
research: a methodological introduction. Dendrochronologia
20:203–216
Brandes AFN, Barros CF (2008) Anatomia do lenho de oito especies
de lianas da famılia Leguminosae ocorrentes na Floresta
Atlantica. Acta Bot Bras 22:465–480
Brienen RJW, Zuidema PA (2005) Relating tree growth to rainfall in
Bolivian rain forests: a test for six species using tree ring
analysis. Oecologia 146:1–12
Brienen RJW, Zuidema PA (2006) The use of tree rings in tropical
forest management: projecting timber yields of four Bolivian
tree species. For Ecol Manag 226:256–267
Bukatsch F (1972) Bemerkungen zur doppelfarbung astrablau-safra-
nin. Mikrokosmos 61:33–36
Caballe G (1993) Liana structure, function and selection: a compar-
ative study of xylem cylinders of tropical rainforest species in
Africa and America. Bot J Linn Soc 113:41–60
Callado CH, Neto SJS, Scarano FR, Barros CF, Costa CG (2001a)
Anatomical features of growth rings in flood-prone trees of the
Atlantic rain forest in Rio de Janeiro, Brazil. IAWA J 22:29–42
Callado CH, Neto SJS, Scarano FR, Costa CG (2001b) Periodicity of
growth rings in some flood-prone trees of the Atlantic rain forest
in Rio de Janeiro, Brazil. Trees 15:492–497
Callado CH, Neto SJS, Scarano FR, Costa CG (2004) Radial growth
dynamics of Tabebuia umbellata (Bignoniaceae), a flood-toler-
ant trees from the Atlantic forest swamps in Brazil. IAWA J
25:175–183
Carlquist S (1985) Observations on functional wood histology of
vines and lianas: vessel dimorphism, tracheids, vasicentric
tracheids, narrow vessels, and parenchyma. Aliso 11:139–157
Carlquist S (1991) Anatomy of vine and liana stems: a review and
synthesis. In: Putz FE, Mooney HA (eds) The biology of vines.
Cambridge University Press, Cambridge, pp 53–72
Carlquist S (1995) Wood and bark anatomy of Ranunculaceae
(including Hydrastis) and Glaucidiaceae. Aliso 14:65–84
Carlquist S (2001) Comparative wood anatomy: systematic, ecolog-
ical and evolutionary aspects of dicotyledon wood, 2nd edn.
Springer-Verlag, Berlin
Clark DA, Clark DB (1994) Climate-induced annual variation in
canopy tree growth in a Costa Rican tropical rain forest. J Ecol
82:865–872
Committee IAWA (1989) List of microscopic features of hardwood
identification. IAWA Bull N. ser. 10:219–332
Cook ER, Peters K (1981) The smoothing spline: a new approach to
standardizing forest interior tree-ring width series for dendrocli-
matic studies. Tree-ring Bull 41:45–53
Devall MS, Parresol BR, Wright SJ (1995) Dendroecological analysis
of Cordia alliodora, Pseudobombax septenatum and Annonaspraguei in central Panama. IAWA J 16:411–424
Dunisch O, Montoia VR, Bauch J (2003) Dendroecological investi-
gations on Swietenia macrophylla King and Cedrela odorata L.
(Meliaceae) in the central Amazon. Trees 17:244–250
Eckstein D, Baas P (1999) Dendrochronology in Monsoon Asia.
IAWA J 20:223–350
Eckstein D, Sass U, Baas P (1995) Growth periodicity in tropical
trees. IAWA J 16:323–442
Enquist BJ, Leffler AJ (2001) Long-term tree ring chronologies fromsympatric tropical dry-forest trees: individualistic responses to
climatic variation. J Trop Ecol 17:41–60
Eshete G, Stahl G (1999) Tree rings as indicators of growth
periodicity of acacias in the Rift Valley of Ethiopia. For Ecol
Manag 116:107–117
Estrada GCD, Callado CH, Soares MLG, Lisi CS (2008) Annual
growth rings in the mangrove Laguncularia racemosa (Com-
bretaceae). Trees 22:663–670
Ewers FW, Fisher JB, Chiu ST (1990) A survey if vessel dimensions
in stem of tropical lianas and others growth forms. Oecologia
84:544–552
Ewers FW, Fisher JB, Fichtner K (1991) Water flux and xylem
structure in vines. In: Putz FE, Mooney HA (eds) The biology of
vines. Cambridge University Press, Cambridge, pp 127–160
Fichtler E, Trouet V, Beeckman H, Coppin P, Worbes M (2004)
Climatic signal in tree rings of Burkea africana and Ptero-carpus angolensis from semiarid forest in Namibia. Trees
18:442–451
Fritts HC (1976) Tree rings and climate. The Blackburn press, New
Jersey
Garfi G, Ficarrotta S (2003) Influence of ivy (Hedera helix L.) on the
growth of downy oak (Quercus pubescens s.l.) in the Monte
Carcaci Nature Reserve (central-western Sicily). Ecol Mediter
29:5–14
Gasson P, Dobbins DR (1991) Wood anatomy of the Bignoniaceae,
with a comparison of trees and lianas. IAWA Bull 12:389–417
Gebrekirstos A, Mitlohner R, Teketay D, Worbes M (2008) Climate–
growth relationships of the dominant tree species from semi-arid
savanna woodland in Ethiopia. Trees 22:631–641
Gentry AH (1991) The distribution and evolution of climbing plants.
In: Putz FE, Mooney HA (eds) The biology of vines. Cambridge
University Press, Cambridge, pp 3–50
Trees (2011) 25:133–144 143
123
Gerwing JJ (2004) Life history diversity among six species of canopy
lians in an old-growth forest of the eastern Brazilian Amazon.
For Ecol Manag 190:57–72
Gerwing JJ, Schnitzer SA, Burnham RJ, Bongers F, Chave J, Dewalt
SJ, Ewango CEN, Foster R, Kenfack D, Martınez-Ramos M,
Parren M, Parthasarathy N, Perez-Salicrup DR, Putz FE, Thomas
DW (2006) A standard protocol for Liana censuses. Biotropica
38:256–261
Grau HR, Easdale AT, Paolini L (2003) Subtropical dendroecology–
dating disturbances and forest dynamics in northwestern Argen-
tina montane ecosystems. For Ecol Manag 177:131–143
Heuze P, Dupouey J, Schnitzler A (2009) Radial growth response of
hedera helix to hydrological changes and climatic variability in
the rhine floodplain. River Res Applic 25:393–404
Holmes RL (1983) Computer-assisted quality control in tree-ring
dating and measurement. Tree-Ring Bull 43:69–78
Holmes RL (1994) Dendrochronology Program Library: users manual
(Updated November 1994). Laboratory of Tree-Ring
Research,University of Arizona, Tucson
Isnard S, Silk WK (2009) Moving with climbing plants from Charles
Darwin’s time into the 21st century. Am J Bot 96:1205–1221
Jacoby GC (1989) Overview of tree-ring analysis in tropical regions.
IAWA Bull 10:99–108
Leon-Gomez C, Monroy-Ata A (2005) Seasonality in cambial activity
of four lianas from a Mexican lowland tropical rainforest. IAWA
J 26:111–120
Lima AC, Pace MR, Angyalossy V (2010) Seasonality and growth
rings in lianas of Bignoniaceae. Trees 24:1045–1060. doi:
10.1007/s00468-010-0476-z
Lisi CS, Tomazello Fo M, Botosso PC, Roig FA, Maria VRB,
Ferreira-Fedele L, Voigt ARA (2008) Tree-ring formation, radial
increment periodicity, and phenology of tree species from a
seasonal semi-deciduous forest in Southeast Brazil. IAWA J
29:189–207
Lorimer CG, Dahir SE, Singer MT (1999) Frequency of partial and
missing rings in Acer saccharum in relation to canopy position
and growth rate. Plant Ecol 143:189–202
Mariaux A (1967) Les cernes dans les bois tropicaux africains, nature
et periodicite. Rev Bois For Trop 113(3–14/114):23–37
Morim MP (2006) Leguminosae arbustivas e arboreas da Floresta
Atlantica do Parque Nacional do Itatiaia, Sudeste do Brasil:
Padroes de distribuicao. Rodriguesia 57:27–45
Nabe-Nielsen L (2002) Growth and mortality rates of the liana
Machaerium cuspidatum in relation to light and topographic
position. Biotropica 34:319–322
Nola P (1997) Interactions between Fagus sylvatica L. and Hederahelix L.: a dendroecological approach. Dendrochronologia
15:23–37
Oliveira JM, Santarosa E, Pillar VD, Roig FA (2009) Seasonal
cambium activity in the subtropical rain forest tree Araucariaangustifolia. Trees 23:107–115
Oliveira JM, Roig FA, Pillar VD (2010) Climatic signals in tree-rings
of Araucaria angustifolia in the southern Brazilian highlands.
Austral Ecol 35:134–147
Oliveira-Filho AT, Fontes MAL (2000) Patterns of floristic differen-
tiation among Atlantic forests in Southeastern Brazil and the
influence of climate. Biotropica 32:793–810
Perez-Salicrup DR, Schnitzer S, Putz FE (2004) Community ecology
and management of lianas. For Ecol Manag 190:1–2
Priya PB, Bhat KM (1999) Influence of rainfall, irrigation and age on
the growth periodicity and wood structure in Teak (Tectonagrandis). IAWA J 20:181–192
Putz FE (1990) Liana stem diameter growth and mortality rates on
Barro Colorado Island, Panama. Biotropica 22:103–105
Schenck H (1893) Beitrage zur biologie und anatomie der lianen, in
besonderen der in Brasilien einheimishe arten. 2. Beitrage zur
anatomie der lianen. In: Schimpers AFW (ed) Botanische
Mittheilungen aus der Tropen 5. G. Fischer, Jena, pp 1–271
Schnitzer SA (2005) A mechanistic explanation for global patterns of
liana abundance and distribution. Am Nat 166:262–276
Schnitzer SA, Bongers F (2002) The ecology of lianas and their role
in forests. Trends Ecol Evol 17:223–230
Schnitzler A, Heuze P (2006) Ivy (Hedera helix L.) dynamics in
riverine forests: effects of river regulation and forest disturbance.
For Ecol Manag 236:12–17
Schongart J (2008) Growth-oriented logging (GOL): a new concept
towards sustainable forest management in Central Amazonian
varzea floodplains. For Ecol Manag 256:46–58
Schongart J, Piedade MTF, Wittmann F, Junk WJ, Worbes M (2005)
Wood growth patterns of Macrolobium acaciifolium (Benth.)
Benth. (Fabaceae) in Amazonian black-water and white-water
floodplain forests. Oecologia 145:454–461. doi:10.1007/s00442-
005-0147-8
Schongart J, Orthmann B, Hennenberg KJ, Porembski S, Worbes M
(2006) Climate-growth relationships of tropical tree species in
West Africa and their potential for climate reconstruction. Glob
Chang Biol 12:1139–1150
Schweingruber FH (2007) Wood structure and environment.
Springer-Verlag, Berlin
Schweingruber FH, Poschlod P (2005) Growth rings in herbs and
shrubs: life span, age determination and stem anatomy. For Snow
Landsc Res 79:195–415
Segadas-Vianna F, Dau L (1965) Ecology of the Itatiaia Range,
Southeastern Brazil. II. Climates and climatic altitudinal zona-
tion. Arq Mus Nac 53:31–53
Seitz RS, Kanninen M (1989) Tree ring analysis of Araucariaangustifolia in southern Brazil: preliminary results. IAWA Bull
N. ser. 10:170–174
Stahle DW (1999) Useful strategies for the development of tropical
tree-ring chronologies. IAWA J 20:249–253
Stokes MA, Smiley TL (1996) An introduction to tree-ring dating,
2nd edn. The University of Arizona Press, Arizona
Verheyden A, Helle G, Schleser GH, Beeckman H (2006) High-
resolution carbon and oxygen isotope profiles of tropical and
temperate liana species. Schr Forsch Julich Reihe Umw
61:31–35
Vetter RE, Botosso PC (1989) Remarks on age and growth
rate determination of Amazonian trees. IAWA Bull N. ser.
10:133–145
Worbes M (1985) Structural and other adaptation to long-term
flooding by trees in Central Amazonia. Amazoniana 9:459–484
Worbes M (1989) Growth rings, increment and age of trees in
inundation forests, savannas and a mountain forest in the
neotropics. IAWA Bull N. ser. 10:109–122
Worbes M (1995) How to measure growth dynamics in tropical trees:
a review. IAWA J 16:337–351
Worbes M (1999) Annual growth rings, rainfall-dependent growth
and long-term growth patterns of tropical trees from the Caparo
Forest Reserve in Venezuela. J Ecol 87:391–403
Worbes M (2002) One hundred year of tree-ring research in the
tropics: a brief history and an outlook to future challenges.
Dendrochronologia 20:217–231
Worbes M, Staschel R, Roloff A, Junk WJ (2003) Tree ring analysis
reveals age structure, dynamics and wood production of a natural
forest stand in Cameroon. For Ecol Manag 173:105–123
Zimmermann MH (1983) Xylem structure and the ascent of sap.
Springer-Verlag, Berlin
144 Trees (2011) 25:133–144
123