THE FERNS AND LYCOPHYTES OF A MONTANE TROPICAL FOREST IN SOUTHERN BAHIA, BRAZIL

2010·6.8 MB·English

by  Fernando B Matos

«
AND
THE FERNS LYCOPHYTES OF A MONTANE TROPICAL FOREST
SOUTHERN
IN BAHIA, BRAZIL
Amorim
Fernando Matos Andre M.
B.
Centro de Pesquisas do Cacau - CEPEC Universidade Estadual de Santa Cruz - UEl
Departamento de
Ctencias Bioldgicas
IMus, 45.662-900, Bahia, BRAZIL
[email protected]
Paulo Labiak
H.
do UFPR
Universidade Federal Parand -
Departamento de Botdnica
Caixa Postal 19031
81531-980, Parand, BRAZIL
Curitiba,
RESUMO
INTRODUCTION
Bahla and contains representative
one numbers plant species
of the terms of of
richest states in Brazil in
&
***
According
of almost all of the phytogeographic domains in the country (Brazao Araujo 1981). to
and
topography
Harle
and Mayo species richness are the
y two contribute greatly to this
(1980), factors that
lhe tension km* than France, with
560,000 (larger
of the which covers an area of approximately
state,
a
H0OO one
5 principally as
climatic diversity,
km*). considerable
This ample likewise contains
territory
*****
from Humid Forests are found in the eastern part of
the Atlantic
coast
to the continental interior.
the
state, “cerrado” [savanna], riparian forests,
while [dryland],
semi-arid regions (including the “caatinga”
*
50%
aS0nal occupy more than of the
fo and mountain vegetation])
rests, “campos rocky
rupestres” [open,
*
(Giulietti
2006).
l.
Although this floristic richness has attracted
t
19th century (for a more detailed account, see Urban, 1906), few collections have been made in the humid
of southern Bahia.
forests
Remnants of the Atlantic Coastal Forest in southern Bahia are known to be among the most
important
seem
sites for conservation of biodiversity in the world. Indeed, these forests to hold higher levels of specks
richness and plant endemism than any other part of the Brazilian Atlantic Rain Forest (Mori
et
al. 1981;
Thomas
et al. 1998, 2008; Martini et al. 2007). Southern Bahia is also considered one of the most remark-
able Pleistocene forest refuge areas, and a center of diversity for several major groups of organisms (Mori
et
&
Whitmore
Prance Gentry
1983; 1987; 1992).
al.
Most botanists studying this region have directed their efforts towards angiosperms, with only rare
studies of ferns and lycophytes, although the plant lists prepared by Mori et al. (1983) and Amorim et al.
become
(2005, 2008) are notable exceptions. Additional recent taxonomic information has also available
concerning specific groups of ferns in Fernandes (2003), Labiak and Prado (2003, 2005a, 2005b, 2005c,
2007), Matos et al. (2009, 2010), Prado (2000), and Sundue and Prado (2005). In addition to species lists of
the ferns and lycophytes of southern Bahia Paciencia and Prado (2004, 2005a, 2005b) have described
State,
some
of the ecological aspects of the area.
Considering these survey limitations and the fact that essentially all of the floristic studies undertaken
in southern Bahia have focused on the diversity of lowland vegetation, clear that the regional flora con-
is
it
tinues to be insufficiently studied. In an effort to further our floristic knowledge of the Brazilian Atlantic
humid
montane
Forest, the present study examined the fern and lycophyte species in a fragment of forest
The Serra Bonita Mountain Range occupies an area of approximately 7,500 ha in the municipalities of Ca-
macan km km D
and Pau-Brasil, 130 from the city of llheus and 526 from the state capital, Salvador (Fig.
39°33'W)
The x
Serra Bonita Private Reserve located in the central region of this range (15°23'S
is
2,000
and was founded to help protect regional biodiversity. The reserve occupies an area of approximately
m
hectares at elevations that vary from 300 to 1,080 (Amorim et al. 2009).
Roeder (1975) described the climate of the region as warm and humid, with an average annual rainfall
mm
between
vary
of 1 ,500-1 ,800 that is well distributed throughout the year. Average annual temperatures
humidity
23 and 24°C, the total annual evapotranspiration potential 1,200-1,300 mm, and the relative
is
wit
reaches 80%. There no and temperature
is specific information currently available for precipitation
lowland areas,
the study area itself, although there are obvious climatic variations between the highland and
where
Roeder’s earlier collections (1975) were made.
vary
reserve
Both the degree of preservatic physi tructure of the vegetatio lin the
-
regeneration
of
stages
„ act forests while others have forests in different
_
mountaintop
(areas that were harvested timber road leading to a
for or cleared for agriculture). Additionally, a
vegetation
transmission tower cuts through part of the Reserve, resulting in the eradication of the original
(Amorim
in that area
et 2009).
al.
shelter
Recent research has shown that the few remaining moist fragments in the region
forest
capuc
numbers
of rare species, including two endangered primates: Cebus xanthosternos (yellow-breasted
°_
and PrellI
comm.).
Leontopithecus chrysomelas (golden-headed lion tamarin) (Vitor O. Becker, pers.
spec**
floristic studies have identified ca. 700 species of angiosperms (Amorim et al. 2009), with several
&
new
to science, including a very notable bromeliad (Amorim Leme
2009).
coni
However, timber
despite its remarkable regional biodiversity, the harvesting of native trees for
to be a major contributor
to forest destruction in
this area.
Ferns and lycophytes in southern Bahia, Brazil
Matos et al.
(
Journal of the Botanical Research
Institute of Texas4(1)
able for this area are some ferns and lycophytes that were collected by Talmon Soares dos Santos (in
1969,
Wm.
1971, and 1979), Scott Alan Mori (in 1979), Andre Mauricio Vieira de Carvalho (in 1983), and Wayt
CEPEC
Thomas (in 1994 and 2002). Complete sets of all of these collections are deposited in the herbarium,
NY
and have been and UPCB.
duplicates sent to
While duplicates of some collections were sent to specialists of other institutions for identification,
the
great majority of the plants were identified by the first author using well-documented collections at CEPEC,
NY UPCB
and (among and
others) specific bibliographies.
The ferns and lycophytes are arranged alphabetically in the checklist by family, genus, and then species.
The fern families were circumscribed according to the system proposed by Smith et al. (2006). Authors of
names specimen could be
species are abbreviated according to Pichi Sermolli (1996). Occasionally, a reliably
identified only to genus but was clearly distinct from any of the identified material; these specimens were
was
included in the as In the present work, the concept of Atlantic Forest treated in a broader sense
list “sp.”
&
(Oliveira-Filho Fontes 2000), with the result that the areas of distribution of some species extended into
and
the continental sometimes reaching neighboring countries (Argentina Paraguay).
interior,
A
total of 182 species in 67 genera and 23 families of ferns and lycophytes from the Serra Bonita Reserve
are presented here (Appendix The ferns comprised 173 species in 64 genera and 21 families, while the
1).
Only remained unidenti-
lycophytes included nine species in three genera and two families. three species
from of the other
fied Ctenitis sp., Elaphoglossum sp., and Thelypteris sp.), but they are distinctly different all
(
species in their respective genera.
and
The most diverse fern families were Polypodiaceae Dryopteridaceae (28), Pteridaceae (19),
(35),
found in
species
Hymenophyllaceae Together, these four families comprise about 57 percent of the
(16).
Thelypterts
Serra Bonita. The most species-rich genera were Asplenium followed by Elaphoglossum (11),
(12),
'
and '
Diplazium
(10), (9).
being
new currently
Several specimens collected during this study have been identified as species or are
M
beckeria*
and
described by specialists, including: Asplenium truncorum, egalastrum indusiatum, Thelypteris
2C-E).
(Fig.
£
was
Terpsichore asplenifolia (Fig. 2F) recorded for the time in Brazi
first
ortheastern
junct between Venezuelan-Guyana and do
distribution the Shield the Serra
1
& Bahia or
time for
Brazil (Labiak Prado 2007). Forty-three additional species were recorded for the first
Pi*
Pernambuco,
northeastern Brazil (comprising the states of Alagoas, Bahia, Ceara, Maranhao, Paraiba,
rescn*
the
Rio Grande do Norte, and Sergipe), representing 24.2% of the total number of species found in
new reco
new these
These records are indicated with asterisks in the checklist (Appendix In general,
1).
and are
represent species characteristic of montane areas of the Atlantic Forest of southeastern Brazil,
expected to occur in the other states of northeastern Brazil. Polypodium dulce, Pteris schwackeana,
no
in
and from other states
decomposita, S.Jlexuosa, Serpocaulon levigatum have been previously reported
new
eastern Brazil, but are records for the Atlantic Rain Forest of southern Bahia.
atedwith
associate
many
In terms of habitat preferences, representatives of the local flora are typically
plantations
disturbed environments roadsides, forest edges, forest regrowth, cabrucas [cocoa
(e.g.,
B
auritum,
native and other anthropogenic and Adiantum Asplenium
forests] include:
sites), latifolium,
,
GleichenellapectinataM
brasiliense (Fig. B. occidental Dennstaedtia Dicranopterisflexuosa,
3), globulifera,
cinna
Osmundastrum
Hemicmitis tomentosa, Hypolepis cemua, Lygodium
aff. repens, Lycopodiella volubile,
lanugos
Pityrogramma 5.
calomelanos, Pleopeltis pleopeltifolia, Pteridium arachnoideum, Sticherus bifidus,
and
Thelypteris opposita,
serrata.
T.
h****
an 70%).
The
great majority of the ferns and lycophytes identified in the present study (more
chai
c
spP*
(89
49% terrestrial
of the species inventoried were exclusively
ats,

including herbacec
w
2%
and
(9 spp.),
type of habitat.
New
Ferns are the third most species-rich group of epiphytes in the World, after orchids and bromeliads
&
(Gentry Dodson 1987). The last two groups are represented in the Serra Bonita Reserve by 62 and 25
(Amorim making second most group
species respectively et 2009), thus the ferns the diverse of epiphytic
al.
plants in the area (59
spp.).
Moran some
Several authors 2003; Mehltreter 2008) have observed that epiphytic fern spe-
(e.g., et al.
on which
cies demonstrate notable specificity in relation to the type of substrate phorophytes) they can
(i.e.,
among
The phorophyte supports
grow. arboreal ferns of the family Cyatheaceae stand out the available in
humid
tropical forests, as they generally have a dense mass of adventitious roots surrounding their trunks,
which can store considerable quantities of water and nutrients due to their high porosity (Mehltreter 2008).
In Serra Bonita, five epiphyte species were observed growing exclusively on this type of substrate (notably
on Alsophila setosa including Asplenium truncorum, Pecluma truncorum, Polyphlebium angustatum, Terpsichore
),
asplenifolia, and Trichomanes polypodioides. However, most epiphytic species inventoried did not appear to
depend exclusively on these ferns and were collected on a wide variety of angiosperms.
Among
many narrowly distributed spe-
the terrestrial species, is clearly noticeable the preference of
it
cies to the forest understory, occurring exclusively in well-preserved forest remnants. The high diversity of
and number show the importance
epiphytic ferns, the large of terrestrial species in the forest understory,
the
of well-preserved environments not only for the richness of species in numerical terms, but also for
maintenance of the narrowly distributed species populations.
Geographical and endemism
distribution
endemism
and
According to Tryon (1972), Brazil is one of the principal centers of fern and lycophyte diversity
40%
in the Neotropical region, with about endemism.
Bonita
The number Serra
of species endemic to the Atlantic Rain Forest that were encountered in the
un
studies
Reserve is quite high (59 species, or 32.5% of the especially when compared with other
total),
&
Schwartsburd
dertaken in the Atlantic Rain Forest domain Labiak Prado 1998; Salino et 2005;
al.
(e.g.,
&
Amorim
Labiak
2007; et 2008).
al.
Bahia
southern
of
lins
Atlantic
appear to constitute the northern limit of occurrence for many ende d lycophytes n the
Some southeastern
Forest. of these species can be considered characteristic of the montane regions of
H.
southern Brazil Adiantum mynssenae, Asplenium scandidnum, Cyathea Huperziaflexibilis,
(e.g., rufa,
r
Thelypteris
Micropolypodium
achilleifolium, Pleopeltis pleopeltidis, Pteris angustata, Terpsichore reclinata,
and among
Vittaria scabrida,
others).
some
specif
of
Paradoxically, the southern region of Bahia represents the southern limit of distribution
oreSt
dryland f
endemic
to the Atlantic Forest, as they also occur in the “Brejos de altitude” (high elevation
^
Bon
1
Serra
of northeastern Brazil. Two examples of this unusual situation among the taxa recorded for the
Reserve are Cyathea praecincta and Megalastrum
eugenii.
chains
mountain
Although and
ferns lycophytes are usually capable of dispersing over large areas,
In
been found Moran 2008).
to represent frequent barriers to their migration (Tryon 1986; 1995,
P^
Te
give
11
favoring high levels of endemism, mountains can also influence the taxonomic richness of a
andha
regions
Entire families can sometimes be considered typical (but not exclusive high elevation
to)
^
Acco %
fundamental 2008).
role in the floristic characterization of those areas (Moran 1995; Paciencia
**
Hymenophy
main
these authors, the examples
of these families are Cyatheaceae, Dryopteridaceae,
qr
E
and
Lycopodiaceae, and Polypodiaceae. In the same sense, many tropical genera such as Diplazium

Dincidence that they show
the
greatest species richness in the Serra Bonita Reserve.
It is also important to note the existence of species with disjunct distributions between the Atlantic
Amazon
and (and/or Andean) forests. According to Tryon (1986), a given fern species can be considered
km
when
disjunct the distance between populations reach about 1,000 or more, even though
its there
are
adequate environments for their occurrence in the intervening regions. Doryopteris
sagittifolia (Pteridaceae),
for example, occurs in the mountains of eastern Brazil but has also been reported in isolated populations
in
various countries in northern South America (Guyana, French Guyana, Suriname and Venezuela). Terpskhort
asplenifolia (a species widely distributed from southern Mexico to Bolivia and the Antilles) occurs disjunctly
known &
and
in Brazil, the Serra Bonita Reserve the of the only population in the country (Labiak
is site
Prado 2007). Also noteworthy are Elaphoglossum gardnerianum, Hymenophyllum caudiculatum and
Pleopeltis
Amazon
monoides, Brazilian endemics showing disjunct distributions between the Atlantic and forests; 58
Amazon
additional species encountered in our study occur in both southern Bahia and in forests.
Some many
Brazilian species have wide geographical distributions throughout parts of the world
(e.g.,
Adiantum Asplenium Hymenophyllum and Pityrogramma
latifolium, auritum, polyanthos, Lycopodiella cernua,
number of species shared by both the Atlantic and Amazon forests (a total of 61 species) is still quite notable,
however, especially in view of the fact that these two extensive forest formations are separated by a “diagonal
—
of drought” a corridor of highly seasonal and dry formations the “Caatinga” of northeastern Brazil,
(e.g.,
&
the “Cerrado” savanna of Central Brazil, and the “Chaco” of Paraguay, Argentina and Bolivia) (Prado
Gibbs 1993) that “isolates” the Atlantic Rain Forest from other rain forests in South America (Andean and
Amazon
forests).
many Moriet
Although reported by authors Andrade-Lima 1953, 1966, 1969; Bigarella et al. 1975;
(e.g.,
al. 1981; Rizzini 1997), the disjunction observed between species of the floras of northern and eastern Brazil
must be evaluated with some caution, as the differentiation between long distance dispersal and vicariance
(Wolf
examination
in the historical biogeographical patterns of fern distribution requires more intensive
still
et 2001).
al.
Invasive species
brown
In spite of the relatively recent introduction of Macrothelypteris torresiana, Nephrolepis ii
Sou
and Thelypteris dentata into the tropical Americas, these species are already found in many areas °f *
&
&
associated
America (Mickel Smith 2004; Hovenkamp Miyamoto 2005). These species are primarily
and areas
with ruderal environments disturbed areas,
in the Serra Bonita Reserve along forest edges,
(e.g.,
under and habitats.
cultivation) apparently are not yet seriously competing with the local flora for
to
part,
The low number in large
due,
of unidentified species encountered in the present study (three) is
was
many Identification
the collaboration of specialists in identifying this material (see Acknowledgments).
and Thelypt*™'
especially difficult in very diverse or little-studied genera such as Ctenitis, Elaphoglossum,
each of which had one species of unknown
identity.
Floristic relationships
Preliminary analyses of similarities between the flora of southern Bahia and other diverse
by
characterized
America
(Matos 2009) indicate that the montane forests of southern Bahia are especial
_
^
this
supports
“southern” elements of the Atlantic Forest. The large number of new records reported here
same c
The
as the majority of these species are characteristic of the montane regions of southern Brazil.
B
southeastern
floristic relationships between the montane forests of southern Bahia and the mountains of
elevatio^
low
has likewise been observed for the angiosperms (Amorim et 2009). On the other hand, the
al.
are
northern
forests of southern Bahia appear be more Amazon or to
to closely related the forests
to
j^
Ferns and lycophytes in southern Bahia, Brazil
Matos et al..
Conservation
modern mankind
One of the greatest challenges to is reconciling economic growth (which usually implies
utilization of natural resources) with global biodiversity conservation, and preservation efforts must
increased
optimized by establishing criteria that guarantee the most favorable possible balance between costs, social
be
needs and the efficient functioning of established conservation areas (Crozier 1997; Crandall et 2000).
al.
Among the notable examples of diversity observed in the region, some species are noteworthy by their
Appendix represent approximately 25% of the total number of ferns and lycophytes encountered in the
1)
Serra Bonita Reserve.
The montane forests of the Serra Bonita Reserve offer ideal environmental conditions for the establish-
ment and growth of ferns and lycophytes, harboring almost all of the taxonomic orders proposed by Smith
ttal. (2006) (the only exceptions being the Psilotales, Equisetales and the heterosporous ferns [Salviniales],
although the last can be found lower elevations in the region). The conservation importance of the Serra
at
Bonita Reserve therefore lies not just in the number of species, but also in the phylogenetic diversity it pre-
APPENDIX
1
names
The before species
Checklist of the ferns and lycophytes from the Serra Bonita Reserve, southern Bahia, Brazil. asterisk
on
gjtothefirstrecoi.j -io -a " to species newly described, based material
rF-.hn fer
»ri r.-n
f . ,, i I- '
m M
M
:-V ,-vn-.H.h AA - Andre Arn,,-im FF = Fabric Ferreira.
hi -urn- v.- r;ll
o;.|l-.-.;r, r. i.
.
; I i
M
= WT
Fernando ML = = and - Wm. Wayt Thomas. Abbreviation for the
B. Matos, Mardel M. Lopes, PL Paulo H. Labiak,
J
=
habitat of the species: EP = Epiphytic HE = Hnir.i-ec- pnvtir RU - Ru * m,,i and TE Terrestrial.
(
AND
FERNS
LYCOPHYTES
FM
Mett.— HE/TE
Blechnum acutum (Desv.) 292,
Anemiaceae
FM
Desv.— TE
Blechnum brasiliense 614, (Fig. 3)
Sw.—
FM
RU/TE L—
625,
FM
TE
3
Blechnum occidentale
1 6,
Brade—FM 1064.TE
'Blechnum organense
^iaphyllitidis Sw.-FM
(L) TE
789,
n.—FM1366.TE
1
Salpichlaena volubilis (Kaulf.) J.
FM
TE
Kaulf.— 447,
Alsophila setosa
FM
Conant— TE
384,
stembergii (Sternb.) D.S. 1
Alsophila
Domin— FM
1550,TE
(Raddi)
— Cyathea corcovadensis
—
FM
ex 1538.TE
^ich. Willd. FM
TE
— Cyathea delgadii Sternb. 382, (Fig. 3)
1
FM
F£e EP
‘X 448, Domin—FM TE
636,
Cyathea glaziovli (F6e)
kunzeanum
Klotzsch ex Rosenst.—PL 3730, TE/
Mart—FM
619,TE
Cyathea phalerata
Domin—FM
1088,TE
(Kunze)
Cyathea praecincta
Sgil
11562, EP/TE FM
103.TE
Lellinger—
'Cyathea rufa (F6e) 1
mpteropus
FM
Kaulf.—
EP
1567,
—
^scandidnum
FM
EP
Kaulf. 299,
mserra
Langsd. & AA
Fisch.— EP
m 5435,
Moore—FM
TE
295,
t!iWetrum N. Murak. & R.C.Moran—FM 313, RU Dennstaedtia dissecta (Sw.) T.
FM
TE
Hieron.—
529,
toncorum FM Dennstaedtia globulifera (Poir.) 1
& Sylvestre—
Matos, Labiak
F.B.
H L.
Moore— FM
1063.TE
EP
7, Dennstaedtia obtusifolia (Willd.) T.
(Fig.
2)
Sm.—
TE
PL 371
(Thunb.)
Histiopteris incisa J. 5,
.
342
FM
Hypolepis repens (L) C. Presl— 1522, TE Polyphlebium hymenophylloides (Bosch) Ebihara &
aff. Dubuis-
—
Maxon FM son—FM
arachnoideum EP
Pteridium 1368.TE 649,
(Kaulf.)
—
FM
Trichomanes elegans Rich. 371 TE (Fig
1 3)
Dryopteridaceae — ,
—
FM
Trichomanes pilosum Raddi EP
337,
1
FM
Copel 1332,TE
'Ctenitis aspidioides (C. Presl)
L—
FM
Trichomanes polypodioides EP
302,
Ching—FM
Ctenitisdistans (Brack.) 1372.TE
—
&
Vandenboschia collariata (Bosch) Ebihara Iwats.—FM
K.
& FM
Ctenitis submarginalis (Langsd. Fisch.) Ching 264, TE
RU
304,
FM
sp.— TE
Ctenitis 787,
1
&
* Vandenboschia rupestris (Raddi) Ebihara Iwats.—FM
K.
Moore—FM
Cyclodium heterodon TE
(Schrad.) 095,
T. (Fig. 3)
1
RU
C 1555,
FM
Cyclodium meniscioides (Willd.) Presl— 321 ,TE
—
FM
Didymochlaena truncatula (Sw) J5m. TE Lindsaeaceae
383,
1
—
FM FM
Elaphoglossum sp.— EP Lindsaea lancea Bedd. TE
1329, 376,
(L.) 1
— —
'Elaphoglossum decoratum (Kunze) Moore FM RU 'Lindsaea quadrangularis Raddi FM1$51,TE
T. 445,
,
—
-JP
'Elaphoglossum gardnenanum (Kunze
e>
FM
marginata Kuhn HE
Lomariopsis (Schrad.) 074,
1
EP
446,
Hovenkamp & Miyam.—FM
Nephrolepis brownii (Desv.)
Sm.—FM
Elaphoglossum glabellum RU
607,
J.
610,TE
—
Brade—FM
Elaphoglossum insigne (Fee) 620, EP
FM
— Nephrolepis cordifolia (L) C. Presl 523, TE
1
|
FM
Elaphoglossum lingua RU Sm—
Brack. 060,
1 FM
— Nephrolepis pendula (Raddi) 1588, EP/TE
J.
FM
'Elaphoglossum peltatum EP
(Sw.) Urb. 1584,
(Fig, 2) Krug—FM
ex 1589, EP/TE
Nephrolepis rivularis (Vahl) Mett.
'Elaphoglossum rigidum Urb.—FM EP
(Aubl.) 1331,
Lycopodiaceae
Moore—
'Elaphoglossum strictum (Raddi) T. JP 449, EP —
FM
FM Huperzia acerosa (Sw.) Holub 319, EP/RU
'Elaphoglossum vagans Hieron.— EP
(Mett.) 1583,
—
FM
EP
Sm.—FM *Huperzia (Fee) 0llg. 1571,
'Elaphoglossum villosum (Sw.) 1572, EP flexibilis B. —
J.
—
FM EP/RU
FM *Huperzia heterocarpon (Fee) Holub 1581,
Lastreopsis amplissima Tindale TE
(C. Presl) 284, j
FM EP
a Ching—FM HE Huperzia mandiocana (Raddi) Trevis— 1 553, (Fig. 2)
guianensis (Aubl.) 1047, —
FM
EP
Huperzia martii (Wawra) Holub 1777,
Serm.— FM TE
Lycopodiella cernua (L) Pic 653,
Lygodiaceae
—
FM
TE
Lygodium Sw.
volubile 265,
n—
FM
—
FM
Danaea geniculata Raddi 1335.TE
°Megalastn &
Prado
Labial
Sm.—FM 1067,TE
Eupodium
kaulfussii Sm.)
(J. J.
TE
365,
1 (Fig.
*Megalastrum umbrinum (C Sm. & Moran—FM Oleandraceae
Chr.) A.R. R.C.
FM EP
1076,TE Presl— 440,
Oleandra articulata (Sw.) C.
Kunze—FM
Otfersia cervina (L) RU/TE
096,
1
Ophioglossaceae
ML —
*Polybotrya speciosa Schott— HE
788,
L FM EP
Ophioglossum palmatum 375,
1
C
FM
Chr.—
Stigmatopterisprionites (Kunze) 1548.TE
Osmundaceae
3731
cinnamomeum Presl—
Osmundastrum PL.
(L) C.
|
Underw.—FM ,
Dicranopteris flexuosa (Schrad.) TE
1804,
Polypodiaceae
Gleichenella pectinata Ching—FM TE
(Willd.) 652,
(Fig. 3)
WT
Fee— EP
4230,
Sticherus bifidus (Willd.) Ching—FM 657, TE * Campyloneurum acrocarpon 1
Fee—FM 41
Campyloneurum angustifolium (Sw.) ,
Nakai—FM
Sticherus lanuginosus (F£e) TE aff.
654,
FM
Presl— 290,
Campyloneurum decurrens (Raddi) C.
*
j
Hymenophyllaceae
FM
Presl— 273,
Campyloneurum
* nitidum (Kaulf.) C.
Abrodictyum rigidum & Dubuisson—FM
Ebihara
(Sw.) 301, FM
Bishop—
Cochlidium serruhtum (Sw.) LE.
FM
Moran—
& >
Sm.
suspensa R.C.
Lellingeria (L) A.R.
Morans*
&
Sm. R-C-
'Melpomene melanosticta (Kunze) A.R.
EP
6497,
—
___
FM 577, EP
Microgramma Alston
acatallela 1
Hymenophyllum caudiculatum Mart—FM EP RM Tryon"
303, & Af.
Tryon
— Microgramma geminata
(Schrad.)
'Hymenophyllum
elegans Spreng. PL 371 EP
1, FM315
EP
‘
Hymenophyllum Sw.— FM
hirsutum (L) 646, EP F.M U** !
Copel.— T
— Microgramma tycopodioides 1
(L.)
Hymenophyllum FM
polyanthos (Sw.) Sw. 645, EP Sota—FM 544,
Microgramma de 1
percussa (Cav.) la ^
—
Polyphlebium angustatum & Dubuisson—
(Carmich.) Ebihara
FM EP
327,
Microgramma Alston
tecta (Kaulf.)
FM
EP
1068, Cope
&
Microgramma (Langsd. Fisch.)
— vacciniifolia
Polyphlebium diaphanum & FM
(Kunth) Ebihara Dubuisson
EP
650,