Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
TAXON 61 (2) • April 2012: 402–418
Revised generic delimitations for Oxypolis and Ptilimnium (Apiaceae)
based on leaf morphology, comparative fruit anatomy, and
phylogenetic analysis of nuclear rDNA ITS and cpDNA trnQ-trnK
intergenic spacer sequence data
Mary Ann E. Feist,1 Stephen R. Downie,2 Anthony R. Magee3,4 & Mei (Rebecca) Liu5
1 Illinois Natural History Survey, Prairie Research Institute, University of Illinois at UrbanaChampaign, Champaign,
Illinois 61820, U.S.A.
2 Department of Plant Biology, University of Illinois at UrbanaChampaign, Urbana, Illinois 61801, U.S.A.
3 Compton Herbarium, South African National Biodiversity Institute, Private Bag X7, Claremont 7735, South Africa
4 Department of Botany and Plant Biotechnology, University of Johannesburg, P.O. Box 524, Auckland Park 2006,
Johannesburg, South Africa
5 Department of Biology, Harbin Normal University, Hexing Road 50, Harbin 150080, People’s Republic of China
Author for correspondence: Mary Ann E. Feist, mfeist@illinois.edu
Abstract A phylogenetic study of Oxypolis and Ptilimnium, two small genera of tribe Oenantheae (Apiaceae: subfamily Apioideae), was carried out. Generic circumscriptions and infrageneric and infraspecific relationships were investigated through
parsimony and Bayesian inference analyses of nuclear rDNA ITS and cpDNA trnQ5′rps16 and 3′rps165′trnK intergenic spacer
sequences. Fruit anatomical characters were also examined and used in conjunction with leaf morphology to corroborate the
results of the phylogenetic analyses. Each genus as currently delimited has both compound-leaved and rachis-leaved species.
Results of the phylogenetic analyses show that neither Oxypolis nor Ptilimnium is monophyletic; each genus is split into two
strongly supported clades that correspond to differences in leaf morphology within the groups. Fruit anatomical characters
support these splits. The fruits of compound-leaved and rachis-leaved Oxypolis species differ in the number of commissural
vittae per mericarp, the branching of the vittae, and the lignification of mericarp around the seed. The fruits of compoundleaved and rachis-leaved Ptilimnium species differ in the compression of the mericarps and the development of the marginal
ribs. The fruits of rachis-leaved Oxypolis and rachis-leaved Ptilimnium species also differ in the compression of the mericarps
and the development of the marginal ribs. Based on analyses of molecular data and corroboration with morphological and fruit
anatomical data, new circumscriptions for the genera Oxypolis and Ptilimnium are formalized. Each of the two polyphyletic
genera (Oxypolis and Ptilimnium) is split, two genera (Tiedemannia and Harperella) are resurrected, and three new combinations are made.
Keywords Harperella; new combinations; Oenantheae; Oxypolis; Ptilimnium; rachis leaves, Tiedemannia
INTRODUCTION
Oxypolis Raf. and Ptilimnium Raf. are two small genera of tribe Oenantheae (Apiaceae: subfamily Apioideae). As
currently circumscribed, the genus Oxypolis is comprised of
seven species and the genus Ptilimnium of six species. These
names with taxonomic authorities are presented in Table 1.
Most species of Oxypolis and Ptilimnium are endemic to North
America, but each genus has one species (i.e., O. filiformis,
P. capillaceum) with a range that extends into the West Indies
(Brace, 1929; Liogier & Martorell, 2000). Each genus also has
one species (i.e., O. canbyi, P. nodosum) listed as federally
endangered in the U.S.A. (U.S. Fish and Wildlife Service, 1986,
1988). The genera Oxypolis and Ptilimnium share several ecological and morphological traits including glabrous leaves and
stems, fascicled roots, globose to broadly ovate fruits, and a
preference for wet habitats. In addition, two very different leaf
morphologies are found within each genus. While most species of Oxypolis and Ptilimnium have compound leaves, as is
402
typical in subfamily Apioideae, others share an unusual leaf
morphology known as rachis leaves. Rachis leaves are linear,
terete, hollow, and septate and are equivalent to the rachis of a
pinnately compound leaf in which the pinnae are not fully expressed. Instead, the pinnae are highly reduced and transformed
into nodal appendages that function as hydathodes (Kaplan,
1970). One other genus within tribe Oenantheae, Lilaeopsis
Greene, also has species with rachis leaves, but this genus has
no compound-leaved species. Cynosciadium DC. and Limno
sciadium Mathias & Constance, also of tribe Oenantheae, have
rachis-like basal leaves (linear and septate, but flattened and
not hollow), but their cauline leaves are palmately and pinnately lobed, respectively. Rachis leaves are thought to be an
adaptation to an aquatic or semi-aquatic habitat, and species
of Oxypolis and Ptilimnium with rachis leaves (i.e., O. canbyi,
O. filiformis, O. greenmanii, and P. nodosum) spend much of
the growing season at least partially submerged.
The compound-leaved species of Oxypolis have pinnately
or ternately compound leaves with pinnae that are generally
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Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
somewhat broad (except for O. ternata in which they are long
and narrow). Compound-leaved Ptilimnium species have finely
dissected, pinnately decompound leaves with linear or filiform
pinnae. Despite having radically different leaf morphologies
from their compound-leaved congeners, the rachis-leaved Oxy
polis and Ptilimnium species were placed in their respective
genera based primarily on fruit morphology (Elliott, 1817;
Mathias, 1936). Elliott (1817) placed the compound-leaved Sium
rigidius L. (now O. rigidior) and the rachis-leaved S. tereti
folium Elliott (now O. filiformis) in the same genus based on the
shared features of their fruit, including their strong dorsal compression and broad marginal wings. Candolle (1829) created
separate genera for the rachis-leaved and compound-leaved
Oxypolis species (Tiedemannia and Archemora, respectively),
but Coulter & Rose (1887, 1888) united them once again arguing that “no fruit character can be made to separate them, and
the only distinction would have to be drawn from the leaves”.
The rachis-leaved Ptilimnium (then divided into three species)
were originally placed in their own genus, Harperella Rose, but
Mathias (1936) moved them into the genus Ptilimnium based
on morphological similarities of the fruit, including the corkythickened marginal ribs. Easterly (1957a), in his monograph of
the genus Ptilimnium, agreed with Mathias stating that “the
strikingly different vegetative character” of the leaves was not
sufficient to warrant generic recognition for Harperella.
Traditional higher-level classifications within Apiaceae
have relied heavily on fruit characters. These classifications,
however, have not always held up to molecular systematic studies (Downie & Katz-Downie, 1996; Downie & al., 1996, 1998,
2001; Plunkett & al., 1996; Calviño & Downie, 2007; Magee
& al., 2010a). This is the result of a complex pattern of parallelisms and convergences of fruit characters within the family
(Plunkett & al., 1996; Downie & al., 1998; Lee & al., 2001;
Liu & al., 2009, Magee & al., 2009b). For example, characters
such as dorsal flattening and wing formation have evolved in
several independent lineages of Apioideae, most likely as a
dispersal mechanism (Theobald, 1971; Downie & al., 2000c;
Spalik & Downie, 2001; Winter & al., 2008), and therefore
cannot necessarily be taken as evidence of close relationship.
This has brought the taxonomic value of fruit characters into
question (Downie & al., 2001; Spalik & Downie, 2001; Calviño
& al., 2006; Liu & al., 2006). Liu & al. (2006), however, are
against abandoning the use of these characters altogether. They
argue that “fruit anatomy, if studied carefully, can provide an
excellent source of characters to test, support, and supplement
findings based on molecular evidence”.
In the past decade, tribe Oenantheae has been the subject
of several studies utilizing DNA sequence data to examine
phylogenetic relationships (Downie & al., 2004, 2008; Hardway
& al., 2004; Lee & Downie, 2006; Spalik & Downie, 2006;
Feist & Downie, 2008; Spalik & al., 2009). Results of these
studies have shown that as many as five genera within the
tribe are not monophyletic. Two of these studies examined
the relationship of the rachis-leaved Ptilimnium and Oxypolis
species to their compound-leaved congeners (Downie & al.,
2008; Feist & Downie, 2008). The Feist & Downie (2008) study
was based solely on nrDNA internal transcribed spacer (ITS)
sequences. The Downie & al. (2008) study incorporated both
ITS and cpDNA psbI-5′trnK sequences but took a broader look
at relationships within the whole tribe Oenantheae and did not
thoroughly sample Oxypolis and Ptilimnium. The results of
both studies agreed that Oxypolis and Ptilimnium as currently
delimited are not monophyletic and should each be split into
two genera. For each genus, the suggested split corresponds
to the split between rachis-leaved and compound-leaved taxa.
Although these two previous studies suggested the polyphyly of both Oxypolis and Ptilimnium, nomenclatural changes
were postponed until confirmation from additional data could
be obtained. In this paper we present additional sequences
from the chloroplast genome and combine these with ITS and
cpDNA sequences from these earlier studies. We also examine leaf morphology and an additional independent source of
Table 1. Current circumscription of Oxypolis and Ptilimnium and proposed new combinations for taxa included in this study.
Current classification
New combinations and reinstatements
Oxypolis canbyi (J.M. Coult. & Rose) Fernald
Tiedemannia canbyi (J.M. Coult. & Rose) Feist & S.R. Downie
Oxypolis fendleri (A. Gray) A. Heller
Oxypolis filiformis (Walter) Britton
Tiedemannia filiformis (Walter) Feist & S.R. Downie subsp. filiformis
Oxypolis greenmanii Mathias & Constance
Tiedemannia filiformis subsp. greenmanii (Mathias & Constance) Feist & S.R. Downie
Oxypolis occidentalis J.M. Coult. & Rose
Oxypolis rigidior (L.) Raf
Oxypolis ternata (Nutt.) A. Heller
Ptilimnium ahlesii Weakley & G.L. Nesom
Ptilimnium capillaceum (Michx.) Raf.
Ptilimnium costatum (Elliott) Raf.
Ptilimnium nodosum (Rose) Mathias
Harperella nodosa Rose
Ptilimnium nuttallii (DC.) Britton
Ptilimnium texense J.M. Coult. & Rose
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Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
evidence, fruit anatomical data, to determine if they corroborate the molecular results. We then provide new circumscriptions for the genera Oxypolis and Ptilimnium based on these
multiple lines of evidence. Each of the two polyphyletic genera
(Oxypolis and Ptilimnium) is split, two genera (Tiedemannia
and Harperella) are resurrected, and three new combinations
are made. A key to these four genera is included in the Taxonomic Treatment section below. Infrageneric and infraspecific
relationships are also examined and our results are compared
to former taxonomic treatments.
MATERIALS AND METHODS
Taxon sampling and outgroup selection. — In a study of
tribe Oenantheae which included several species of Oxypolis
and Ptilimnium, Downie & al. (2008) found that among the
five noncoding plastid DNA loci they examined, the trnQ5′rps16 and 3′rps16-5′trnK intergenic spacers (hereafter, trnQ
and trnK) were the most variable. Therefore these regions were
used for this study. Complete sequences of the trnQ and trnK
regions from 76 accessions and complete sequences of the
nrDNA ITS region from 66 accessions were used in this study
(Appendix 1). Sequences were obtained for all seven species
of Oxypolis and six species of Ptilimnium. Sequence data for
one accession of the purported hybrid Oxypolis filiformis ×
O. greenmanii were also included. All Oxypolis and Ptilimnium
taxa were represented by multiple accessions to assess infraspecific variation. Two species of Perideridia Rchb. were chosen as outgroups (Appendix 1). Previous phylogenetic studies
which have included the Oenanthe clade or tribe Oenantheae
(Plunkett & al., 1996; Downie & al., 1996, 1998, 2000b) have
shown the genus Perideridia to be sister group to a clade comprising all other members of the tribe. The genera Atrema DC.,
Cynosciadium, Daucosma Engelm. & A. Gray ex A. Gray,
Lilaeopsis, Limnosciadium, Neogoezia Hemsl., and Trepocar
pus Nutt. ex DC. have allied with Ptilimnium and Oxypolis in
previous studies and together make up what has become known
as the North American Endemics Clade (Hardway & al., 2004;
Downie & al., 2008). Accessions of these genera were included
in the phylogenetic analyses to show their placements relative to
Oxypolis and Ptilimnium (Appendix 1). Nomenclature follows
Kartesz (2010), except Oxypolis ternata which follows Feist
(2009), Atrema americanum DC. (= Bifora americana Benth.
& Hook. f. ex S. Watson) which follows Hardway & al. (2004),
and Lilaeopsis which follows Affolter (1985).
DNA extraction, purification, and sequencing. — For
this study, trnQ, trnK, and ITS sequences were newly generated for 55, 44, and 9 accessions, respectively. The remaining
sequences used had already been published (Downie & KatzDownie, 1996; Downie & al., 2000a, 2008; Hardway & al.,
2004; Feist & Downie, 2008). The new sequences were generated according to the following methods. Leaf material was
taken from either herbarium specimens or field-collected and
silica-dried samples. DNA was isolated using a DNeasy Plant
Mini Kit (Qiagen, Valencia, California, U.S.A.) according to
the manufacturer’s instructions. The entire ITS region (ITS-1,
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TAXON 61 (2) • April 2012: 402–418
5.8S rDNA, ITS-2) was amplified using primers 18S-ITS1-F
(Spalik & Downie, 2006) and C26A (Wen & Zimmer, 1996) or
primers 18S-for (Feist & Downie, 2008) and C26A. The PCR
amplification methods used are described elsewhere (Downie
& al., 2000a). PCR products (templates) were purified using
either a QIAquick Gel Extraction Kit or a QIAquick PCR Purification Kit (Qiagen) following manufacturer’s instructions.
For cpDNA, sequences were obtained for the trnQ(UUG)-rps16
5′ exon and rps16 3′ exon-trnK (UUU) intergenic spacers using
the primers trnQ, rps16-1R, rps16-2, and trnK (Downie & KatzDownie, 1996; Lee & Downie, 2006; Downie & al., 2008). The
“rpl16” program of Shaw & al. (2005) was used for the cpDNA regions because it is effective across a wide range of taxa
and genomic regions (Shaw & al., 2007). PCR products were
checked on 1% agarose gels and then purified according to the
ExoSAP protocol of Werle & al. (1994) using 5 U of Exonuclease I (New England Biolabs, Ipswich, Massachusetts, U.S.A.)
and 0.5 U of Shrimp Alkaline Phosphatase (Promega, Madison, Wisconsin, U.S.A.). Sequence reactions for all sequences
were carried out using an ABI Prism Big Dye Terminator v.3.1
Ready Reaction Cycle Sequencing Kit (Applied Biosystems,
Foster City, California, U.S.A.). Sequence reaction products
were visualized using an ABI 3730XL high-throughput DNA
capillary sequencer. All newly acquired sequences used in this
study have been deposited in GenBank (www.ncbi.nlm.nih.gov/
genbank/). See Appendix 1 for GenBank accession numbers.
Sequence alignment and phylogenetic analysis. — Sequences were aligned using Clustal X v.1.83 (Thompson & al.,
1997) and manually adjusted as necessary using the alignment
editor Bioedit v.7.0.9.0 (Hall, 1999). For the trnQ and trnK datasets only, informative gaps were scored as additional binary
characters according to the “simple indel coding” method of
Simmons & Ochoterena (2000). Indels were not scored for the
ITS dataset, as they had been used in a previous study of the
group (Feist & Downie, 2008) and had not been useful. Three
matrices of sequence data were constructed. The first included
the aligned nucleotide data from the trnQ and trnK regions
(cpDNA), the second included these data and the binary-coded
indels (cpDNA/indels), and the third included the aligned nucleotide data from the trnQ, trnK, and ITS regions (cpDNA/ITS).
To facilitate analysis, identical sequences were represented by
single terminals, except where identical sequences were from
individuals from distinct geographic areas of interest (Table 2).
The cpDNA and cpDNA/indels datasets included sequences of
76 accessions (65 terminals). The cpDNA/ITS dataset included
sequences of 66 accessions (63 terminals). Most of the ITS
sequences used represented a subset of a larger ITS matrix
of 147 accessions used in Feist & Downie (2008). Sequence
characteristics were obtained for the ITS and cpDNA (trnQ/
trnK) regions. Uncorrected pairwise nucleotide distances were
calculated using the distance matrix option of PAUP* v.4.0b10
(Swofford, 2003). Before combining the ITS and cpDNA datasets, the incongruence length difference test of Farris & al.
(1995) was performed using the partition-homogeneity test in
PAUP* to evaluate the extent of conflict between them. This
test was executed with 100 replicate analyses, using the heuristic search option, simple stepwise addition of taxa, and TBR
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Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
Table 2. Summary of identical sequences that were represented by a single terminal accession in the
phylogenetic analyses, except when these sequences were from individuals from geographic areas
of interest. Accession numbers in the second column are those identifying terminals in Fig. 1 and/or
Fig. 2. Accession numbers in the third column have identical sequences to those presented in the second column for the regions indicated. Voucher information for all accessions is provided in Appendix 1.
Taxon
Accession
number
Accessions with identical sequences
(regions for which it is identical)
Daucosma laciniata
3411
3412 (trnQ/trnK)
Oxypolis canbyi
2937
2938 (trnQ/trnK)
Oxypolis fendleri
2350
2351, 2369 (trnQ/trnK)
Oxypolis greenmanii
2941
2717 (trnQ/trnK/ITS)
Oxypolis occidentalis
3464
2929
2928
2755
3465, 3466 (trnQ/trnK)
2937 (trnQ/trnK/ITS)
2927 (trnQ/trnK)
3442 (trnQ/trnK)
Ptilimnium nodosum
2784
2635 (trnQ/trnK/ITS)
branch swapping; MaxTrees was set to 20,000. The aligned
data matrices are available in TreeBASE (http://purl.org/phylo/
treebase/phylows/study/TB2:S12295).
Maximum parsimony (MP) analyses of each of the three
data matrices were implemented in PAUP*. All characters
were treated as unordered and all character transformations
were weighted equally. Heuristic MP searches were replicated
10,000 times with random addition of taxa and the following
options in effect: MULTREES, TBR branch swapping, and
gaps treated as missing data. Bootstrap (BS) analyses were
done on all datasets to assess clade support. For all datasets
1000 bootstrap replicates were performed with 100 random
sequence addition replicates. All BS analyses were performed
with the heuristic search option, TBR branch swapping, and
MULTREES options in effect. For the cpDNA and cpDNA/
indels datasets MaxTrees was set to 5000 trees per replicate; for
the cpDNA/ITS dataset it was set to 20,000 trees per replicate.
MrBayes v.3.1.2 (Huelsenbeck & Ronquist, 2001) was used
to conduct Bayesian inference (BI) analyses of the three datasets (cpDNA, cpDNA/indels, cpDNA/ITS). Modeltest v.3.7
(Posada & Crandall, 1998) was used to select the appropriate
evolutionary models of nucleotide substitution for each of the
three DNA regions. The models that best fit these data, as
selected by the Akaike information criteria (AIC) estimator,
were used in the BI analyses. A restriction site (binary) model
was implemented for the indels partition in the cpDNA/indels
dataset. For each dataset, two independent runs of four chains
each were conducted for 2,000,000 generations with a sample
frequency of 100. Plots of generation number vs. likelihood
value were inspected and stationarity was determined to have
been reached after 4000 trees were sampled. For each dataset,
the 4000 trees sampled prior to stationarity (the burn-in) were
discarded and a majority-rule consensus tree was constructed
from the remaining trees to show the posterior probability values of all observed bipartitions.
The MP and BI analyses were performed on cpDNA,
cpDNA/indel, and combined cpDNA/ITS datasets that both
included and excluded the single accession of the hybrid Oxypo
lis filiformis × O. greenmanii. This was done to assess whether
the inclusion of this hybrid had any effect on the placement of
other taxa in the phylogenetic trees.
Fruit anatomy. — Fruits from herbarium specimens were
used in an anatomical study (Appendix 2). Each of the seven
Oxypolis and six Ptilimnium species were represented. In addition, accessions of the closely related Cynosciadium digitatum,
Limnosciadium pinnatum, and L. pumilum were included. For
each species, fruits from between one and three accessions
were examined. To make transverse sections, fruits were first
rehydrated and then placed in FAA for a minimum of 24 h.
These samples were subsequently treated according to a modification of the method of Feder & O’Brien (1968) for embedding
in glycol methacrylate (GMA). Transverse sections of about
3 µm thick were made using a Porter-Blüm ultramicrotome
and stained using the periodic acid Schiff/toluidine blue (PAS/
TB) method of Feder & O’Brien (1968). To study the threedimensional structure of the vittae, fruits were placed in boiling
water and left to cool and soak for at least 24 h. Thereafter,
the exocarp was removed while keeping the fruit submerged
in water to prevent desiccation.
RESULTS
ITS dataset. — The ITS matrix had an aligned sequence
length of 639 positions. One hundred and four positions were
excluded from further analyses due to alignment ambiguities.
The number of parsimony-informative positions was 242 and
the number of autapomorphic positions was 30. The maximum
pairwise sequence divergence value for the ITS region across
all 63 terminals was 24.23%. Considering just Oxypolis s.l. and
Ptilimnium s.l., the maximum sequence divergence was 21.86%
between O. canbyi (a rachis-leaved species) and O. ternata
(a compound-leaved species). Phylogenetic analyses were not
carried out on this dataset alone since these analyses had been
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Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
performed on a larger ITS dataset previously (Feist & Downie,
2008). Modeltest selected the SYM + I + G model of evolution to
be used for the ITS region in the BI analysis of combined data.
cpDNA datasets. — The cpDNA dataset had an aligned
sequence length of 2813 positions. Due to alignment ambiguities 409 positions were excluded from further analyses. Of
the remaining 2404 aligned positions, 280 were parsimonyinformative and 88 were autapomorphic. The cpDNA/indel
dataset with 63 binary-scored alignment gaps had a total of
343 parsimony-informative characters. The maximum pairwise
sequence divergence value for the cpDNA region across all
65 terminals was 5.56%. Considering only Oxypolis s.l. and
Ptilimnium s.l., the maximum sequence divergence was 3.82%
between P. nodosum (rachis leaves) and O. ternata (compound
leaves). Modeltest selected the GTR + G and GTR + I + G models
for the trnQ and trnK regions, respectively, for use in the BI
analyses.
MP analysis of the cpDNA dataset resulted in 23,229 trees
of 473 steps each (consistency index CI = 0.854 and 0.824, with
and without uninformative characters, respectively; retention
index RI = 0.964).
MP analysis of the cpDNA/indel dataset resulted in 4698
trees of 554 steps each (CI = 0.843 and 0.811, with and without
uninformative characters, respectively; RI = 0.963). The addition of the binary-scored indels into the cpDNA matrix had only
a minimal effect on the resulting tree topologies and support
values. The only significant change was that all accessions of
P. costatum were resolved as monophyletic (BS = 79) in the
cpDNA/indels MP strict consensus tree (Fig. 1) but not in the
cpDNA MP strict consensus tree (not shown), and support for
this group was increased from PP = 0.51 in the cpDNA BI
majority-rule consensus tree (not shown) to PP = 0.89 in the
cpDNA/indels BI majority-rule consensus tree (not shown).
For this reason, only the results of cpDNA/indels analyses are
discussed hereafter.
The cpDNA/indels MP tree and cpDNA/indels BI tree
were congruent except that in the BI tree, all accessions of
Oxypolis rigidior formed a weakly supported monophyletic
group (PP = 0.54), whereas in the cpDNA/indels MP tree,
they did not. Other species not resolved as monophyletic in
the cpDNA/indels MP and BI trees were P. ahlesii, P. capil
laceum, O. filiformis, O. rigidior, and O. ternata. Ptilimnium
ahlesii formed a strongly supported monophyletic group with
P. capillaceum in the cpDNA/indels analyses (BS = 100, PP =
1.00), as did O. ternata with O. rigidior (BS = 96, PP = 1.00).
One accession of O. filiformis came out as sister group to the
clade which includes all accessions of O. canbyi (BS = 69, PP =
0.92), while the other accession of O. filiformis formed a weakly
supported clade with O. greenmanii and their purported hybrid
O. filiformis × O. greenmanii (BS = 64, PP = 0.79). These relationships did not change when O. filiformis × O. greenmanii
was excluded from the MP and BI analyses.
Oxypolis occidentalis is divided into two strongly to
moderately supported clades (Fig. 1). The two major clades
of O. occidentalis consist of populations that are separated
geographically and can be referred to as the North clade and
the South clade. The North clade (BS = 89, PP = 1.00) consists
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TAXON 61 (2) • April 2012: 402–418
of individuals from populations from Haida Gwaii (formerly
the Queen Charlotte Islands) in British Columbia, the Cascade Mountains in Oregon, and the Cascade Range Foothills in
northern California. The South clade (BS = 71, PP = 0.98) consists of individuals from populations in the Sierra Nevada, San
Bernardino, White, and Inyo mountain ranges in California.
At the generic level, the MP and BI trees of the cpDNA/
indels data matrix were completely congruent. Ptilimnium s.l.
and Oxypolis s.l. were each not monophyletic. Ptilimnium s.l.
was split between two clades: Clade 1 (Ptilimnium) comprised
of the compound-leaved species of Ptilimnium (i.e., P. ahlesii,
P. capillaceum, P. costatum, P. nuttallii, and P. texense) and
Clade 2 (Harperella) containing the single rachis-leaved species of Ptilimnium (i.e., P. nodosum). Oxypolis s.l. was also
split between two clades: Clade 3 (Tiedemannia) comprised of
the rachis-leaved species of Oxypolis (i.e., O. canbyi, O. fili
formis, and O. greenmanii) and Clade 4 (Oxypolis) containing
the compound-leaved species of Oxypolis (i.e., O. fendleri,
O. occidentalis, O. rigidior, and O. ternata). Clade 3 (Tiede
mannia) is sister to Clade 1 (Ptilimnium) and quite distant in
the tree from Clade 4 (Oxypolis). Clades 1, 2, and 3 were each
strongly supported, whereas Clade 4 (Oxypolis) had moderate
support (BS = 83, PP = 0.99).
In previous analyses based on ITS sequences (Feist
& Downie, 2008), the evolutionary relationships among the
following five groups were not resolved: Clade 1 (Ptilimnium),
Clade 2 (Harperella), Clade 3 (Tiedemannia), Limnosciadium,
and Cynosciadium. These five groups formed what was essentially a polytomy (fig. 1 in Feist & Downie, 2008). The results of
the cpDNA/indels analyses presented herein, however, strongly
support the sister relationship between Clade 1 (Ptilimnium)
and Clade 3 (Tiedemannia) (BS = 98, PP = 1.00). Together,
these two groups form a strongly supported sister relationship
with Clade 2 (Harperella) (BS = 86, PP = 0.99), followed by
the successively basal sister groups Limnosciadium (BS = 66,
PP = 0.85) and Cynosciadium (BS = 100, PP = 1.00).
Two new accessions of Daucosma laciniata Engelm. &
A. Gray were used in this study. As a result, the placement of
Daucosma differs from that found in previous studies where the
accession D. laciniata 2397, a misidentified specimen of Lim
nosciadium pinnatum (DC.) Mathias & Constance, was used
(Hardway & al., 2004; Downie & al., 2008; Feist & Downie,
2008). In this study, the two accessions of D. laciniata are
monophyletic and are sister to a clade formed by Atrema ameri
canum and Trepocarpus aethusae Nutt. (BS = 87, PP = 1.00).
Combined dataset (cpDNA/ITS). — The results of the
partition homogeneity test for 63 terminals common to both
the cpDNA and ITS datasets revealed that these loci do not
yield significantly different phylogenetic estimates (ILD probability value = 0.21). Therefore, these datasets were combined
for simultaneous analysis. The combined cpDNA (without
binary-scored indels) and ITS data matrix (cpDNA/ITS) had
an aligned sequence length of 3452 positions. Due to alignment ambiguities 513 positions were excluded from further
analyses. Of the remaining 2939 aligned positions, 522 were
parsimony-informative and 118 were autapomorphic. Adding
the cpDNA trnQ and trnK sequences to the ITS matrix more
TAXON 61 (2) • April 2012: 402–418
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
than doubled the number of parsimony-informative characters
from the previous study by Feist & Downie (2008).
The maximum pairwise sequence divergence value for the
combined cpDNA/ITS dataset across all 63 terminals was 9.74%
between Oxypolis canbyi and Daucosma laciniata. Considering
just Oxypolis s.l. and Ptilimnium s.l., maximum sequence divergence was 7.62% between O. canbyi (a rachis-leaved species) and
64/0.99
100/1.00
63/0.87
87/1.00
79/0.89
100/1.00
62/0.99
100/1.00
98/1.00
98/1.00
100/1.00 75/0.97
69/0.92
86/0.99
100/1.00
64/0.79
65/0.96
66/0.85
100/1.00
100/1.00
64/0.89
100/1.00
80/0.99
100/1.00
99/1.00
100/1.00
100/1.00
99/1.00
100/1.00
87/1.00
100/1.00
100/1.00
63/0.99
100/1.00
89/1.00
98/1.00
71/0.98
63/0.76
83/0.99
96/1.00
100/1.00
100/1.00
O. ternata (a compound-leaved species). Maximum sequence divergence among compound-leaved Oxypolis species was 2.40%,
whereas among rachis-leaved Oxypolis species it was 2.99%.
Maximum sequence divergence among Ptilimnium s.l. species
was 6.22%; however, it was just 1.43% among compound-leaved
Ptilimnium species and just 0.19% among the rachis-leaved Ptili
mnium. All species of Ptilimnium s.l. and Oxypolis s.l. showed
Ptilimnium ahlesii 2648
Ptilimnium capillaceum 2701
Ptilimnium ahlesii 2969
Ptilimnium capillaceum 2703
Ptilimnium costatum 1646
Ptilimnium costatum 1970
Ptilimnium costatum 2402
Ptilimnium costatum 2707
Ptilimnium nuttallii 2165
Ptilimnium nuttallii 2617
Ptilimnium nuttallii 2623
Ptilimnium texense 1981
Ptilimnium texense 2905
Oxypolis canbyi 2744
Oxypolis canbyi 2747
Oxypolis canbyi 2751
Oxypolis canbyi 2937 (2)
Oxypolis filiformis 2713
Oxypolis filiformis 2371
Oxypolis greenmanii 2941 (2)
Oxypolis filiformis × O. greenmanii 2714
Ptilimnium nodosum 2787
Ptilimnium nodosum 2900
Ptilimnium nodosum 2931
Ptilimnium nodosum 2934
Ptilimnium nodosum 2902
Ptilimnium nodosum 2930
Ptilimnium nodosum 2936
Limnosciadium pinnatum 1511
Limnosciadium pinnatum 2395
Limnosciadium pumilum 3742
Cynosciadium digitatum 1571
Cynosciadium digitatum 1986
Lilaeopsis carolinensis 2148
Lilaeopsis mauritiana 2150
Lilaeopsis novae-zelandiae 2152
Lilaeopsis occidentalis 1999
Daucosma laciniata 2912
Daucosma laciniata 3411 (2)
Atrema americanum 1160
Trepocarpus aethusae 1660
Neogoezia gracilipes 2770
Neogoezia minor 2774
Oxypolis occidentalis 2755 (2)
Oxypolis occidentalis 2756
Oxypolis occidentalis 2928 (2)
Oxypolis occidentalis 3413
Oxypolis occidentalis 3417
North
Oxypolis occidentalis 2899
clade
Oxypolis occidentalis 3528
Oxypolis occidentalis 1142
Oxypolis occidentalis 1153
Oxypolis occidentalis 3376
South
Oxypolis occidentalis 3464 (3)
clade
Oxypolis occidentalis 3532
Oxypolis ternata 2940
Oxypolis ternata 2738
Oxypolis ternata 2735
Oxypolis rigidior 2003
Oxypolis rigidior 1998
Oxypolis rigidior 1927
Oxypolis fendleri 2350 (3)
Oxypolis fendleri 2368
Perideridia americana 2033
Perideridia kelloggii 778
Clade 1
Ptilimnium
(compound leaves)
Clade 3
Tiedemannia
(rachis leaves)
Clade 2
Harperella
(rachis leaves)
Clade 4
Oxypolis
(compound leaves)
Fig. 1. Strict consensus tree of 4698 minimal-length 554-step trees obtained from the MP analysis of the cpDNA/indels dataset (CI = 0.843 and
0.811, with and without uninformative characters, respectively; RI = 0.963). Numbers on branches represent bootstrap estimates and Bayesian
posterior probability values, respectively. Numbers in parentheses following the name of a taxon indicate the number of accessions of that taxon
having identical DNA sequences (Table 2).
407
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
intraspecific variation, except for P. ahlesii and P. capillaceum
which had sequences that were identical to one another.
MP analysis resulted in 32 trees of 1184 steps each (CI =
0.689 and 0.634, with and without uninformative characters,
respectively; RI = 0.919). The BI majority-rule consensus tree
is presented in Fig. 2 with branch lengths. The topology of the
BI tree is consistent with that of the MP strict consensus tree
TAXON 61 (2) • April 2012: 402–418
(not shown) except at the nodes where an asterisk (*) is given
to indicate that the BS value was less than 50%.
As in the cpDNA/indels analyses, Ptilimnium ahlesii and
P. capillaceum are each not monophyletic, but together they
form a strongly supported monophyletic group (BS = 100,
PP = 1.00). Oxypolis filiformis is also not monophyletic, but
it forms a monophyletic group with O. greenmanii and their
64/.99 Ptilimnium ahlesii 2648
Ptilimnium capillaceum 2701
Ptilimnium ahlesii 2969
Ptilimnium capillaceum 2703
*/0.60 86/1.00
Ptilimnium costatum 1646
94/1.00
Ptilimnium costatum 1970
Ptilimnium costatum 2402
100/1.00
Ptilimnium texense 1981
100/1.00 Ptilimnium texense 2905
Ptilimnium nuttallii 2165
96/1.00
100/1.00 Ptilimnium nuttallii 2623
96/1.00 Oxypolis canbyi 2744
100/1.00
Oxypolis canbyi 2747
Oxypolis canbyi 2937
65/0.98
100/1.00
Oxypolis canbyi 2938
Oxypolis filiformis 2371
100/1.00
Oxypolis filiformis 2713
80/1.00
Oxypolis greenmanii 2941 (2)
74/0.99
Oxypolis filiformis × O. greenmanii 2714
Ptilimnium nodosum 2784 (2)
Ptilimnium nodosum 2787
*/0.90
Ptilimnium nodosum 2934
*/0.94
Ptilimnium nodosum 2936
*/88
Ptilimnium nodosum 2900
100/1.00
Ptilimnium nodosum 2931
Ptilimnium nodosum 2902
Ptilimnium nodosum 2930
100/1.00
100/1.00 Limnosciadium pinnatum 1511
100/1.00
Limnosciadium pinnatum 2395
Limnosciadium pumilum 3742
100/1.00
100/1.00
Cynosciadium digitatum 1571
Cynosciadium digitatum 1986
99/1.00
Lilaeopsis carolinensis 2148
100/1.00
Lilaeopsis mauritiana 2150
100/1.00
Lilaeopsis novae-zelandiae 2152
100/1.00
Lilaeopsis occidentalis 1999
100/1.00
Daucosma laciniata 3411
96/1.00
Daucosma laciniata 3412
95/1.00
Atrema americanum 1160
Trepocarpus aethusae 1660
100/1.00
Neogoezia gracilipes 2770
Neogoezia minor 2774
Oxypolis occidentalis 2755
84/0.99 Oxypolis occidentalis 2756
*/0.90 Oxypolis occidentalis 2928
100/1.00
Oxypolis occidentalis 2929 (2)
North clade
100/1.00 Oxypolis occidentalis 3417
Oxypolis occidentalis 2899
Oxypolis occidentalis 3528
97/1.00
Oxypolis occidentalis 1153
Oxypolis occidentalis 3376
Clade 4
South clade
100/1.00 Oxypolis occidentalis 3466
Oxypolis
73/0.77
(compound
Oxypolis occidentalis 3532
88/0.99
Oxypolis ternata 2735
100/1.00
Oxypolis ternata 2738
Oxypolis ternata 2940
99/1.00
Oxypolis rigidior 1927
98/1.00
99/1.00 Oxypolis rigidior 1998
Oxypolis fendleri 2350
100/1.00
Oxypolis fendleri 2351
Oxypolis fendleri 2369
Perideridia americana 2033
Perideridia kelloggii 778
100/1.00
Clade 1
Ptilimnium
(compound leaves)
Clade 3
Tiedemannia
(rachis leaves)
Clade 2
Harperella
(rachis leaves)
leaves)
0.3
Fig. 2. Majority-rule consensus tree obtained from the BI analysis of the cpDNA/ITS dataset. Numbers on branches represent bootstrap estimates
and Bayesian posterior probability values, respectively; a bootstrap estimate of less than 50% is indicated with an asterisk (*). Numbers in parentheses following the name of a taxon indicate the number of accessions of that taxon having identical DNA sequences (Table 2).
408
TAXON 61 (2) • April 2012: 402–418
hybrid, O. filiformis × O. greenmanii (BS = 100, PP = 1.00).
When O. filiformis × O. greenmanii is excluded from the MP
and BI analyses, the relationships among the remaining taxa
do not change.
Both the North and South clades of O. occidentalis are
again apparent and strongly supported (BS = 100, PP = 1.00,
for both clades). Ptilimnium costatum is resolved as monophyletic (BS = 94, PP = 1.00) as it was in the cpDNA/indel
strict consensus tree. In contrast to the results of the cpDNA/
indel analyses, O. ternata and O. rigidior are each resolved as
monophyletic with strong support (BS = 100, PP = 1.00; BS =
99, PP = 1.00, respectively).
At the generic level, Oxypolis s.l. and Ptilimnium s.l. are
again each shown not to be monophyletic. The sister relationship
of Clade 1 (Ptilimnium) and Clade 3 (Tiedemannia) continues to
be strongly supported (BS = 96, PP = 1.00), while the relationships of Clade 2 (Harperella), Limnosciadium and Cynoscia
dium to these groups and to each other are less well-supported.
Clade 4 (Oxypolis) is strongly supported (BS = 99, PP = 1.00).
As in the cpDNA/indels tree (Fig. 1), Daucosma laciniata is
monophyletic and is sister to a clade formed by Atrema ameri
canum and Trepocarpus aethusae (BS = 96, PP = 1.00).
Fruit anatomy. — Based on fruit anatomy, the species
previously recognized within Oxypolis s.l. and Ptilimnium s.l.
can be separated into four groups corresponding to Clades
1–4 recovered in the molecular analyses. All species have
homomericarpic fruits with a very broad commissure that
extends over the full width of the mericarp. The mericarps
are slightly to prominently dorsally compressed with narrow
to broadly winged marginal ribs, except those of P. nodosum
which are prominently isodiametric and with the marginal ribs
not winged (Fig. 3A). The compound-leaved species of Ptilim
nium (i.e., P. ahlesii, P. capillaceum, P. costatum, P. nuttallii,
and P. texense) have fruits with slightly dorsally compressed
mericarps and thick, narrowly winged marginal ribs that extend
only slightly beyond the marginal vascular bundles (Fig. 3B–F).
The fruits of the species of Ptilimnium s.l. (Fig. 3A–F) are distinguished from those of Oxypolis s.l. (Fig. 3G–L; O. ternata
not shown), as well as Cynosciadium (Fig. 3M) and Limno
sciadium (Fig. 3N–O), by the presence of prominent square or
somewhat elongated cells external to the vittae (not shown), a
character also reported for Dasispermum Raf. (Magee & al.,
2009a, 2010b). The fruits of the species of Oxypolis s.l. are
distinguished from the fruits of the species of Ptilimnium s.l.,
Cynosciadium, and Limnosciadium by their very broad, thin
marginal wings and usually smaller, less lignified vascular
bundles. While most of the species studied have a lignified
layer of mesocarp cells surrounding the endocarp, this character is conspicuously absent in the compound-leaved species
of Oxypolis (i.e., O. fendleri, O. occidentalis, O. rigidior, and
O. ternata; Fig. 3J–L; O. ternata not shown). This latter group
is distinguished furthermore from all other species studied by
the presence of four to eight, often branching commissural
vittae (Figs. 3J–L, 4A–C). The other species studied all have
two commissural vittae which are never branching (Fig. 3A–I,
M–O, 4D). The compound-leaved Oxypolis species are distinguished additionally from the rachis-leaved species of Oxypolis
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
(i.e., O. canbyi, O. filiformis, and O. greenmanii) in that the
vittae are smaller than or equal in size to the vascular bundles
(Fig. 3G–I). In the rachis-leaved Oxypolis species the vittae
are distinctly larger than the vascular bundles (Fig. 3J–L). The
fruits of the closely related genera Limnosciadium (Fig. 3N–O)
and Cynosciadium (Fig. 3M) can be distinguished from both
Oxypolis s.l. and Ptilimnium s.l. by the presence of a lignified
commissural keel, and furthermore in Limnosciadium by the
sclerification of the mesocarp between the vascular bundles so
that they appear continuous.
Oxypolis canbyi (a rachis-leaved species) has a unique
wing type not found in any of the other winged species examined in this study. In O. canbyi, the marginal wing is formed
through the expansion of the mesocarp between the vascular
bundle and the endocarp so that the vascular bundle is located
near the wing tip to form a pseudo-marginal wing (Fig. 3I).
Also, as mentioned by Tucker & al. (1983), a sclerified band
of mesocarp cells is formed between the vascular bundle and
the endocarp. In the other winged species examined, the wing
is formed through the expansion of the mesocarp beyond the
vascular bundle so that the vascular bundle is located at the base
of the wing (Fig. 3B–H, J–O) and a sclerified band of mesocarp
cells is not present between the vascular bundle and the endocarp. In the compound-leaved Ptilimnium, Cynosciadium, and
Limnosciadium species, the true marginal wing remains narrow and extends slightly beyond the marginal vascular bundle
(Fig. 3B–F, M–O). In the compound-leaved Oxypolis, O. fili
formis, and O. greenmanii, the true marginal wing extends
significantly beyond the vascular bundle (Fig. 3G, H, J–M).
DISCUSSION
Ptilimnium/Harperella. — Morphological and molecular
results from this study confirm what was proposed in previous studies (Downie & al., 2008; Feist & Downie, 2008), that
the genus Ptilimnium is not monophyletic. Differences in leaf
morphology, fruit anatomy, and DNA sequence data, as well
as reproductive strategy and chromosome number, support
removing P. nodosum from the genus. Ptilimnium nodosum has
rachis leaves whereas the other members of the genus have pinnately decompound leaves that are finely dissected. The fruits
of P. nodosum are isodiametric and prominently five-ribbed
but not winged, whereas the fruits of the compound-leaved
Ptilimnium species are slightly dorsally compressed and have
thick, narrowly winged marginal ribs that extend beyond the
vascular bundles. In addition, P. nodosum can proliferate extensively through vegetative reproduction. Vegetative shoots
are produced at the nodes of decumbent flowering stems and
develop into individual plantlets when the flowering stalks die
back in winter (Marcinko & Randall, 2008). This method of
reproduction has not been observed in any of the compoundleaved Ptilimnium species. Furthermore, the chromosome number for P. nodosum is n = 6, whereas chromosome numbers for
the compound-leaved species are n = 16 (P. costatum), n = 7
(P. capillaceum, P. nuttallii), and n = 8 or 14 (P. capillaceum)
(Easterly, 1957a; Constance & al., 1976; Weakley & Nesom,
409
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
TAXON 61 (2) • April 2012: 402–418
Fig. 3. Transverse sections of fruits of Ptilimnium s.l. (A–F), Oxypolis s.l. (G–L), Cynosciadium (M), and Limnosciadium (N–O). A, Ptilimnium
nodosum (Feist & MolanoFlores 2967.1, ILLS); B, Ptilimnium ahlesii (Bozeman 6100, NCU); C, Ptilimnium capillaceum (Valentine s.n., BRITSMU); D, Ptilimnium costatum (Feist s.n., ILLS); E, Ptilimnium texense (Shinners 11830, BRIT-SMU); F, Ptilimnium nuttallii (Cory 53275,
BRIT-SMU); G, Oxypolis filiformis (Feist & MolanoFlores 3197, ILLS); H, Oxypolis greenmanii (Godfrey 53756, NCSC); I, Oxypolis canbyi
(Nelson 4269, USCH); J, Oxypolis fendleri (Sturges 205, RM); K, Oxypolis occidentalis (Feist & MolanoFlores 4106, ILLS); L, Oxypolis rigid
ior (Webster & Webster 7206, DUKE); M, Cynosciadium digitatum (Sundell 15406, BRIT); N, Limnosciadium pumilum (Gentry 1996, BRIT);
O, Limnosciadium pinnatum (Lundell 14012, LL). — Abbreviations: aod, additional oil duct; cv, commissural vitta; lck, lignified commissural
keel; mr, marginal rib; pmw, pseudo-marginal wing; rod, rib oil duct; sm, sclerified mesocarp; vb, vascular bundle; vv, vallecular vitta. — Scale:
A = 500 µm; B–O = 2 mm. — Additional voucher information is provided in Appendix 2.
410
TAXON 61 (2) • April 2012: 402–418
2004). Maximum pairwise sequence divergence is much
greater between P. nodosum and the compound-leaved Ptili
mnium species (6.22%) than it is among all compound-leaved
species of Ptilimnium (1.43%), or among the nine accessions
of P. nodosum (0.19%) included in the study. In addition, the
compound-leaved Ptilimnium are more closely related to the
rachis-leaved Oxypolis, with which they form a strongly supported sister group, than they are to P. nodosum.
The type of the genus Ptilimnium is P. capillaceum. Ptili
mnium ahlesii, P. costatum, P. nuttallii, and P. texense form a
monophyletic group with P. capillaceum in the phylogenetic
analyses and share a common fruit and leaf structure. These
taxa should therefore remain together in the genus Ptilimnium.
Prior to 1936 (Mathias, 1936), P. nodosum s.str. was recognized as belonging to the genus Harperella Rose. Three species
of Harperella were recognized (H. nodosa Rose, H. fluvia
tilis Rose, H. vivipara Rose). Easterly (1957b) synonymized
P. viviparum (Rose) Mathias with P. fluviatile (Rose) Mathias
based on their shared habitat type, phenology, and lack of clear
morphological differences. Ptilimnium nodosum s.str. was still
recognized as a separate species due to its unique habitat, phenology, and perceived larger size. Also, it was not thought to
be able to proliferate through asexual reproduction, rooting at
the nodes and producing individual plantlets, as P. fluviatile
was known to do. Kral (1981) conducted a morphological study
comparing P. fluviatile and P. nodosum s.str. Finding no consistent morphological differences he further grouped the taxa
and included P. fluviatile within P. nodosum s.l. Furthermore,
the ability to reproduce asexually, as described above, has been
observed in populations of P. nodosum s.str. (Feist, pers. obs.)
and so cannot be used to differentiate these taxa. Results from
the ITS analyses of Feist & Downie (2008) showed some geographic separation of populations that conformed to the previous delimitations of P. nodosum as three species, however, the
current analyses based on trnQ and trnK data and combined
cpDNA and ITS data do not support these relationships. As we
have found no consistent molecular or morphological evidence
to suggest otherwise, the authors agree with the assessment of
Kral (1981) that these three taxa should be recognized as one
species. We propose the reinstatement of the genus Harperella
Rose with the single species H. nodosa Rose, including H. flu
viatilis and H. vivipara as taxonomic synonyms.
The results of this study support the recent reinstatement
of the species Ptilimnium texense (Feist, 2010). In the combined
cpDNA/ITS analyses, P. texense and P. costatum are sister
to one another but form separate strongly supported clades.
The separation of P. ahlesii from P. capillaceum (Weakley
& Nesom, 2004), however, is not supported. In this study and
in the two previous studies where these two taxa have been included (Downie & al., 2008; Feist & Downie, 2008), P. ahlesii
and P. capillaceum always form a strongly supported monophyletic group, but the two taxa are never separated. DNA
sequences for both accessions of P. ahlesii used in this study
were identical to sequences of accessions of P. capillaceum.
This alone, however, is insufficient evidence for not recognizing P. ahlesii as a distinct species. While writing the treatment
of the genus for the Flora of North America (Feist, unpub. data),
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
the morphological characters used to separate the two taxa
were found to be inconsistent when specimens from across the
geographic range of P. capillaceum were examined. Therefore,
a morphological study is being conducted by the first author to
determine the true status of P. ahlesii.
Oxypolis/Tiedemannia. — Morphological and molecular
results from this study confirm what was proposed in previous studies (Downie & al., 2008; Feist & Downie, 2008), that
the genus Oxypolis is not monophyletic. As with Ptilimnium,
differences in leaf morphology, fruit anatomy, and DNA sequence data support splitting the genus Oxypolis into two genera. Oxypolis canbyi, O. filiformis, and O. greenmanii have
rachis leaves whereas the other members of the genus have
pinnately or palmately compound leaves. Although the fruits
of the compound-leaved and rachis-leaved Oxypolis species are
Fig. 4. Three-dimensional structure of the commissural vittae in the
fruit of Oxypolis s.l. A, Oxypolis rigidior (Oldham 6994, CAN); B,
Oxypolis occidentalis (Feist & MolanoFlores 4106, ILLS); C, Oxy
polis fendleri (Sturges 205, RM); D, Oxypolis filiformis (Feist &
MolanoFlores 3197, ILLS). — Arrows indicate commissural vittae.
Scale: A–D = 1.4 mm.
411
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
superficially similar in that they are all prominently dorsally
compressed and have broadly winged marginal ribs, they can
readily be distinguished anatomically. The mesocarp is lignified around the seed of the rachis-leaved Oxypolis species,
but not of the compound-leaved species. The vittae are larger
than the vascular bundles in the rachis-leaved taxa, but smaller
than or equal to the vascular bundles in the compound-leaved
species. The rachis-leaved Oxypolis taxa have four vallecular
vittae and two commissural vittae, whereas the compoundleaved species have four vallecular vittae and four to eight
commissural vittae, the latter often branching. Maximum pairwise sequence divergence is much greater between the rachisleaved and compound-leaved Oxypolis species (7.62%) than it
is among all compound-leaved species of Oxypolis (2.40%),
or among all rachis-leaved species of Oxypolis (2.99%). The
clade formed by the rachis-leaved Oxypolis is quite distant
from the compound-leaved Oxypolis clade. In fact, the rachisleaved Oxypolis species are more closely related to all the other
genera within the North American Endemics Clade (i.e., Ptili
mnium, Limnosciadium, Cynosciadium, Lilaeopsis, Atrema,
Trepocarpus, Daucosma, and Neogoezia) than they are to the
compound-leaved Oxypolis species. The chromosome numbers
for the rachis-leaved Oxypolis taxa are all n = 14, whereas the
chromosome numbers for the compound-leaved species are n =
16 or n = 18 (Bell & Constance, 1957, 1960; Crawford & Hartman, 1972; Tucker & al., 1983; Pimenov & al., 2003).
The type of Oxypolis is O. rigidior. Oxypolis rigidior forms
a monophyletic group with the other compound-leaved Oxy
polis. We propose to split the genus Oxypolis into two genera
conforming to the compound-leaved and rachis-leaved clades.
In 1829 Candolle created the genus Tiedemannia (Candolle,
1829). He believed that the plant placed in the genus Oenanthe
by Walter and Persoon (i.e., Oenanthe filiformis Walter, 1788;
Oenanthe carolinensis Persoon, 1805) and Sium by Elliott (i.e.,
Sium teretifolium Elliott, 1817), all homotypic synonyms of
O. filiformis, belonged in its own genus (i.e., Tiedemannia)
based on the uniqueness of its fruit and its reduced leaf morphology. We agree with this assessment and propose the reinstatement of the genus Tiedemannia to accommodate the three
rachis-leaved taxa, O. canbyi, O. filiformis, and O. greenmanii.
Oxypolis filiformis is a widespread species, abundant in
Florida and common in the Southeastern U.S.A. and occurs in
a variety of different wetland habitats. Oxypolis greenmanii
has a more restricted range, occurring in just a few counties in
Florida, and seems to have a preference for Hypericum bogs,
although it can be found in flatwoods, swamps, marshes, and
roadside ditches as well. Although at first glance O. greenmanii
appears to be strikingly different from O. filiformis, with its
larger stature and maroon-colored flowers and fruits, Judd
(1982) found that standard populations of O. greenmanii and
O. filiformis are connected by an extensive series of intermediate populations that completely bridge the morphological
gap between the two taxa. Judd (1982) hypothesized that these
populations resulted from gradual geographic intergradation.
In addition to these intermediate populations, populations
that appear to be the result of recent hybridization also exist.
These populations are not uniformly intermediate but are rather
412
TAXON 61 (2) • April 2012: 402–418
highly variable being composed of standard O. greenmanii
and O. filiformis individuals, as well as a complete range of
intermediate plants. Most plants within both the intermediate
and highly variable populations were found to be highly fertile
(ca. 90% to nearly all pollen grains stained with cotton-blue
in lacto-phenol; Judd, 1982). Oxypolis filiformis and O. green
manii also share the same chromosome number and flowering phenology (Judd, 1982). Furthermore, DNA sequence data
provide no support for recognizing the two as distinct species.
Maximum pairwise sequence divergence between O. filifor
mis and O. canbyi is 2.99%, whereas maximum pairwise sequence divergence between O. filiformis and O. greenmanii is
just 0.11%. Therefore, we accept the conclusion of Judd (1982)
that Oxypolis greenmanii is a subspecies of O. filiformis (i.e.,
O. filiformis subsp. greenmanii (Mathias & Constance) Judd).
Finally, the two major clades of Oxypolis occidentalis that
were seen in previous analyses based on ITS sequence data
(Feist & Downie, 2008) are again recovered in all analyses in
this study. The cpDNA sequence data presented herein support the findings of the ITS data alone. A North clade and
a South clade of O. occidentalis are recovered and strongly
supported. Our results suggest that populations of O. occiden
talis from Haida Gwaii, the Cascade Mountains of Oregon,
and the Cascade Range Foothills in northern California are
quite different from those of the Sierra Nevada and the other
more southern mountain ranges of California (South clade).
The maximum sequence divergence among the North clade is
0.24% and among the South clade 0.32%, whereas the maximum sequence divergence between the North clade and the
South clade is 1.49%. This is greater than the maximum pairwise sequence divergence between O. rigidior and O. ternata
(1.31%). The populations represented by the South clade are
within a geographic region known as the California Floristic
Province, which harbors more endemic plant and animal taxa
and more identifiable subspecies than any other area of comparable size in North America (Calsbeek & al., 2003). Populations
from this area could represent a new taxon and another example
of a California Floristic Province endemic.
There is a major disjunction between the populations of
Oxypolis occidentalis that are represented in the North clade.
The northernmost populations of O. occidentalis in Oregon
are approximately 1400 km from the populations on Haida
Gwaii (Cheney & Marr, 2007). Haida Gwaii, located approximately 80 km off the west coast of British Columbia, is an
intriguing geographic area. It has been proposed that during
the last glacial maximum (ca. 15,000 years ago), when glaciers
covered much of present-day British Columbia and extended
into present-day Washington State, much of Haida Gwaii remained ice-free (Heusser, 1960; Lacourse & al., 2005) and
provided a refugium to plants and animals living there. The
glacial refugium hypothesis may explain why O. occidentalis
occurs on these islands and their highly disjunct geographic
distribution. The distribution of this species might have once
extended from Oregon to British Columbia with intervening
populations being wiped out by glaciers. The morphology and
phylogeography of O. occidentalis is currently being studied
to confirm the taxonomic status of these plants.
TAXON 61 (2) • April 2012: 402–418
TAXONOMIC TREATMENT
Key to the genera
1.
Leaves simple; blades reduced to the rachis (thus appearing
linear, terete, hollow, and septate) ......................... 2
1. Leaves 1-pinnate, 1-ternate, or pinnately decompound;
blades with well-developed lamina ....................... 3
2. Mericarps isodiametric, 1–2 × 1–2 mm; marginal ribs not
winged; carpophore 2-fid at apex; plants without a rhizome
or caudex ...................................... 1. Harperella
2. Mericarps strongly dorsally compressed, 4–9 × 3–5.5 mm;
marginal ribs broadly winged; carpophore 2-cleft nearly
to the base; plants with a rhizome or short caudex .......
............................................... 2. Tiedemannia
3. Mericarps strongly dorsally compressed; marginal ribs
broadly winged, thin, not corky; carpophore 2-cleft nearly
to the base; leaves 1-pinnate or 1-ternate; ultimate leaf
segments linear, lanceolate, ovate, or orbiculate; roots
tuberous-thickened ............................. 3. Oxypolis
3. Mericarps slightly dorsally compressed; marginal ribs narrowly winged, thick, corky; carpophore 2-fid at the apex;
leaves pinnately decompound; ultimate leaf segments filiform; roots fibrous........................... 4. Ptilimnium
1. Harperella Rose in Proc. Biol. Soc. Washington 19: 96. 1906 ≡
Harperia Rose in Proc. U.S. Natl. Mus. 29: 441. 1905, nom.
illeg. non Fitzg. (1904) – Type: Harperella nodosa Rose.
1.1 Harperella nodosa Rose in Proc. Biol. Soc. Washington
19: 96. 1906 ≡ Harperia nodosa Rose in Proc. U.S. Natl.
Mus. 29: 441. 1905, nom. illeg. ≡ Carum nodosum (Rose)
Koso-Pol. in Bull. Soc. Imp. Naturalistes Moscou, n.s., 29:
199. 1916 ≡ Ptilimnium nodosum (Rose) Mathias in Brittonia 2: 244. 1936 – Type: U.S.A., Georgia, Schley County,
10 July 1902, Harper 1411 (US!, holotype; BM!, E!, MO,
2 sheets!, NY, 2 sheets!, US!, isotypes).
= Harperella fluviatilis Rose in Contr. U.S. Natl. Herb. 13: 290.
1911 ≡ Ptilimnium fluviatile (Rose) Mathias in Brittonia
2: 244. 1936 – Type: U.S.A., Alabama, Dekalb County, 24
Nov. 1905, Harper 8 (US!, holotype; MO!, isotype).
= Harperella vivipara Rose in Contr. U.S. Natl. Herb. 13: 290.
1911 ≡ Carum viviparum (Rose) Koso-Pol. in Bull. Soc. Imp.
Naturalistes Moscou, n.s., 29: 199. 1916 ≡ Ptilimnium vivipa
rum (Rose) Mathias in Brittonia 2: 244. 1936 ≡ Ptilimnium
fluviatile var. viviparum (Rose) Reveal & C.R. Broome in
Castanea 46(1): 67. 1981 – Type: U.S.A., Maryland, on the
banks of the Potomac River near Hancock, 5 Oct. 1910, Rose
s.n. (US!, holotype; NY, 2 sheets!, isotypes).
The genus name Harperia Rose was found to be a later
homonym for Harperia Fitzg. (1904) and, therefore, Rose
replaced it with the name Harperella. Rose designated Har
perella nodosa Rose as the type for this genus. Harperella
nodosa, H. fluviatilis, and H. vivipara were transferred to the
genus Ptilimnium by Mathias (1936). Easterly (1957a) synonmized P. viviparum under P. fluviatile and Kral (1981) later
synonomized P. fluviatile under P. nodosum. Morphological
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
and molecular evidence shows that P. nodosum (Rose) Mathias
does not belong in the genus Ptilimnium but rather should be
placed in its own genus. Therefore the genus Harperella and
the species name H. nodosa are reinstated and P. nodosum is
synonymized under H. nodosa.
2. Tiedemannia DC., Coll. Mém. 5: 51. 1829 – Type: T. filifor
mis (Walter) Feist & S.R. Downie
Candolle (1829) created the genus Tiedemannia because
he felt that the plant placed in Oenanthe by Walter and Persoon
(i.e., Oenanthe filiformis Walter, 1788; Oenanthe carolinensis
Persoon, 1805) and in Sium by Elliott (i.e., Sium teretifolium
Elliott, 1817) did not belong in either of these genera based on
the uniqueness of its fruit and reduced leaf morphology. The
names Oenanthe carolinensis and Sium teretifolium are both
homotypic synonyms of Oenanthe filiformis, and due to the
rules of priority (Art. 11.2 of the International Code of Botani
cal Nomenclature, McNeill & al., 2006) are illegitimate names.
Candolle made the new combination Tiedemannia teretifolia
based on an illegitimate name and, therefore, his name is also
illegitimate. The correct combination is Tiedemannia filifor
mis. Because Candolle indicated that the name Tiedemannia
teretifolia is a synonym of Oenanthe filiformis, this latter name
represents the type species of Tiedemannia. This is according
to Art. 7.5 of the ICBN (McNeill & al., 2006) which states
“a name that is illegitimate under Art. 52 is typified either by
the type of the name that ought to have been adopted under the
rules (automatic typification), or by a different type designated
or definitely indicated by the author of the illegitimate name”.
2.1 Tiedemannia canbyi (J.M. Coult. & Rose) Feist & S.R.
Downie, comb. nov. ≡ Oxypolis filiformis var. canbyi
J.M. Coult. & Rose in Contr. U.S. Natl. Herb. 7: 193. 1900
≡ Oxypolis canbyi (J.M. Coult. & Rose) Fernald in Rhodora
41: 139. 1939 – Type: U.S.A., Delaware, Ellendale, Aug.
1867, Canby s.n. (US!, holotype; E!, PH!, isotypes).
2.2 Tiedemannia filiformis (Walter) Feist & S.R. Downie,
comb. nov. ≡ Oenanthe filiformis Walter, Fl. Carol.: 113.
1788 ≡ Oxypolis filiformis (Walter) Britton in Mem. Torrey Bot. Club 5: 239. 1894 ≡ Oenanthe carolinensis Pers.,
Syn. Pl. 1: 318. 1805, nom. illeg. ≡ Oxypolis caroliniana
(Pers.) Raf. in Bull. Bot. (Geneva) 1: 218. 1830, nom. illeg.
≡ Oenanthe teretifolia Muhl., Cat. Pl. Amer. Sept.: 32.
1813, nom. illeg. ≡ Sium teretifolium (Muhl.) Elliott, Sketch
Bot. S. Carolina 1: 354. 1817, nom. illeg. ≡ Tiedemannia
teretifolia (Muhl.) DC., Coll. Mem. 5: 81. 1829, nom. illeg.
≡ Peucedanum teretifolium (Muhl.) Wood, Amer. Bot.
Fl.: 136. 1870, nom. illeg. – Type: U.S.A., South Carolina,
Berkeley County, 17 Sept. 1981, Porcher 1977a (BM!, neotype, designated by A.O. Tucker & al. in Syst. Bot. 8: 300.
1983; CITA, DOV, isoneotypes).
= Tiedemannia bakeri H. Wolff ex Urb., Symb. Antill. 5: 452.
1908 ≡ Oxypolis bakeri (H. Wolff ex Urb.) Britton &
P. Wilson ex Bracelin in Torreya 29: 16. 1929 – Type:
Cuba, in Havana Province near Batabano, Oct. 1904, Baker
& Wilson 2215 (location unknown).
413
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
2.2.1 Tiedemannia filiformis (Walter) Feist & S.R. Downie
subsp. filiformis
2.2.2 Tiedemannia filiformis subsp. greenmannii (Mathias
& Constance) Feist & S.R. Downie, comb. nov. ≡ Oxypo
lis greenmanii Mathias & Constance in Bull. Torrey Bot.
Club 69: 152. 1942 ≡ Oxypolis filiformis subsp. greenmanii
(Mathias & Constance) Judd in Rhodora 84: 277. 1982 –
Type: U.S.A., Florida, Gulf County, Wewahitchka, Aug.
1896, Chapman s.n. (MO!, holotype).
3. Oxypolis Raf., Neogenyton: 2. 1825 – Type: Oxypolis ri
gidior (L.) Raf.
3.1 Oxypolis rigidior (L.) Raf. in Bull. Bot. (Geneva) 1: 218.
1830 ≡ Sium rigidius L., Sp. Pl. 1: 251. 1753 ≡ Oenanthe
rigidius (L.) Crantz, Cl. Umbell. Emend.: 85. 1767, ‘rigida’
≡ Pastinaca rigidior (L.) Spreng. in Roemer & Schultes,
Syst. Veg. 6: 586. 1820, ‘rigida’ ≡ Archemora rigidior
(L.) DC., Prodr. 4: 188. 1830, ‘rigida’ ≡ Peucedanum ri
gidius (L.) Wood, Amer. Bot. Fl.: 136. 1870, nom. illeg.,
non Bunge (1833), ‘rigidum’ ≡ Tiedemannia rigidior (L.)
J.M. Coult. & Rose in Bot. Gaz. 12: 74. 1887, ‘rigida’ –
Type: U.S.A. Virginia, Clayton 279 (BM!, lectotype, designated by J.L. Reveal in Taxon 55: 215. 2006).
= Archemora serrata Raf., Herb. Raf.: 78. 1833 – Type: U.S.A.,
Kentucky & Tennessee (location unknown).
= Archemora trifoliata Raf., Herb. Raf.: 78. 1833 – Type:
U.S.A., Missouri (location unknown).
= Oenanthe ambigua Nutt., Gen. N. Amer. Pl. 1: 189. 1818
≡ Pastinaca ambigua (Nutt.) Torr., Fl. N. Middle United
States: 315. 1824 ≡ Archemora ambigua (Nutt.) DC., Prodr.
4: 188. 1830 ≡ Archemora rigidior (L.) DC. var. ambigua
(Nutt.) A. Gray, Manual: 158. 1848, ‘rigida’ ≡ Peucedanum
rigidius (L.) Wood var. ambiguum (Nutt.) Wood, Amer.
Bot. Fl.: 136. 1870, ‘rigidum’ ≡ Tiedemannia rigidior
(L.) J.M. Coult. & Rose var. ambigua (Nutt.) J.M. Coult.
& Rose, Rev. N. Amer. Umbell.: 47. 1888, ‘rigida’ ≡ Oxy
polis rigidior (L.) Raf. var. ambigua (Nutt.) B.L. Rob. in
Rhodora 10: 35. 1908 – Type: U.S.A., banks of the Delaware near Philadelphia (PH!).
= Oxypolis turgida Small, Man. S.E. Fl.: 986. 1933 – Type:
U.S.A., Virginia, Staunton Co., Staunton, 2 Oct. 1895,
Murrill s.n. (lectotype, designated by M.A. Feist in J. Bot.
Res. Inst. Texas 6: 662. 2009: NY!).
= Sium denticulatum Baldwin in Elliott, Sketch Bot. S. Carolina 1: 354. 1817 ≡ Archemora denticulata (Baldwin) DC.,
Prodr. 4: 188. 1830 ≡ Oxypolis denticulata (Baldwin) Raf.
in Bull. Bot. (Geneva) 1: 218. 1830 ≡ Pastinaca denticulata
(Baldwin) D. Dietr., Syn. Pl. 2: 971. 1840 – Type: U.S.A.,
Georgia, 1817, Baldwin s.n. (lectotype, designated by Edmondson in Novon 15: 109. 2005: LINN-Smith, digital
image!).
= Sium longifolium Pursh, Fl. Amer. Sept.: 194. 1813 ≡ Oxypo
lis rigidior (L.) Raf. var. longifolia (Pursh) Britton in Mem.
Torrey Bot. Club 5: 239. 1894, ‘rigidus var. longifolius’ ≡
Oxypolis longifolia (Pursh) Small, Fl. S.E. U.S.: 875, 1336.
414
TAXON 61 (2) • April 2012: 402–418
1903 ≡ Oxypolis rigidior (L.) Raf. subsp. longifolia (Pursh)
Stone, Pl. S. New Jersey 2: 600. 1911 – Type: U.S.A., New
Jersey (lectotype, designated with reservations by J. Ewan
in the introduction to the facsimile reprint of F.T. Pursh’s
Flora Americae Septentrionalis, 1979: PH!).
= Sium tricuspidatum Elliott, Sketch Bot. S. Carolina 1: 354.
1817 ≡ Archemora tricuspidata (Elliott) DC., Prodr. 4:
188. 1830 ≡ Oxypolis tricuspidata (Elliott) Raf. in Bull.
Bot. (Geneva) 1: 218. 1830 ≡ Pastinaca tricuspidata
(Elliott) D. Dietr., Syn. Pl. 2: 971. 1840 – Type: U.S.A.,
South Carolina (CHARL!, holotype).
3.2 Oxypolis ternata (Nutt.) A. Heller, Cat. N. Amer. Pl.: 5.
1898 ≡ Peucedanum ternatum Nutt., Gen. N. Amer. Pl. 1:
182. 1818 ≡ Sataria linearis Raf., New Fl. 4: 21. 1838, nom.
illeg. ≡ Archemora ternata (Nutt.) Nutt. in Torr. & A. Gray,
Fl. N. Amer. 1: 631. 1840 ≡ Tiedemannia ternata (Nutt.)
J.M. Coult. & Rose in Bot. Gaz. 12: 74. 1887 – Type:
U.S.A., North and South Carolina, Nuttall s.n. (BM! lectotype, designated herein). This taxon was neotypified by
M.A. Feist in J. Bot. Res. Inst. Texas 3: 662. 2009. At that
time a type could not be located. This type specimen has
since been located, therefore the neotypification is revoked
and this specimen is designated as the lectotype.
= Sataria linearis Raf. var. longipes Raf., New Fl. 4: 21. 1838.
Rafinesque did not cite a specific collection or give a locality (location unknown).
= Neurophyllum longifolium Torr. & A. Gray, Fl. N. Amer. 1:
613. 1840 – Types: U.S.A., North Carolina, [Cravern Co.],
“Swamps near Newbern, North Carolina, Mr. Croom! Dr.
Loomis! Middle Florida, Mr. Croom! Sept.” (NY!, lectotype, designated by M.A. Feist in J. Bot. Res. Inst. Texas
3: 662. 2009).
3.3 Oxypolis fendleri (A. Gray) A. Heller in Bull. Torrey Bot.
Club 24: 478. 1897 ≡ Archemora fendleri A. Gray in Mem.
Amer. Acad. Arts, n.s., 4: 56. 1849 ≡ Tiedemannia fendleri
(A. Gray) J.M. Coult. & Rose, Rev. N. Amer. Umbell.: 48.
1888 – Type: U.S.A., New Mexico, Santa Fe Creek, Fendler
272 (GH!, holotype; GH!, BM!, isotypes).
3.4 Oxypolis occidentalis J.M. Coult. & Rose in Contr. U.S.
Natl. Herb. 7: 196. 1900 – Type: U.S.A., Oregon, west of
Crater Lake, Leiberg 4413 (US!, holotype; ORE!, isotype).
4. Ptilimnium Raf. in Amer. Month. Mag. & Crit. Rev. 4: 192.
1819 (nom. nud.). Neogenyton: 2. 1825 – Type: Ptilimnium
capillaceum (Michx.) Raf.
4.1 Ptilimnium capillaceum (Michx.) Raf. in Bull. Bot. (Geneva) 1: 217. 1830 ≡ Ammi capillaceum Michx., Fl. Bor.Amer. 1: 164. 1803 ≡ Sison capillaceum (Michx.) Spreng.,
Syst. Veg. 1: 897. 1825 ≡ Discopleura capillacea (Michx.)
DC., Coll. Mém. 5: 38. 1829 – Type: U.S.A., South Carolina
(P-MICH).
= Ammi junceum Raf., Neogenyton: 2. 1825 (nom. nud.) ≡ Ptilim
nium junceum (Raf.) Raf. in Bull. Bot. (Geneva) 1: 217. 1830
TAXON 61 (2) • April 2012: 402–418
≡ Discopleura juncea (Raf.) Steud., Nomcl. Bot., ed. 2., 1:
520. 1840 – Type: U.S.A., Kentucky (location unknown).
= Ammi majus Walter, Fl. Carol.: 113. 1788 non A. majus L.
(1753) ≡ Discopleura major (Walter) Britton & al., Prelim.
Cat.: 22. 1888 – Type: U.S.A., South Carolina (location
unknown).
= Ammi rubricaule Hornem., Hort. Bot. Hafn.: 272. 1813 ≡
Sison rubricaule (Hornem.) Eaton & Wright, Man. Bot.,
ed. 8 [= N. Amer. Bot]: 429. 1840 – Type: U.S.A., Maryland, Baltimore Co., near Baltimore (location unknown).
4.2 Ptilimnium ahlesii Weakley & G.L. Nesom in Sida 21:
744. 2004 – Type: U.S.A., North Carolina, Brunswick Co.,
tidal freshwater marsh of the Brunswick River, Weakley
& LeBlond 7317 (NCU!, holotype; MO!, NY!, isotypes)
4.3 Ptilimnium costatum (Elliott) Raf. in Bull. Bot. (Geneva) 1:
217. 1830 ≡ Ammi costatum Elliott, Sketch Bot. S. Carolina
1: 350. 1817 ≡ Discopleura capillacea var. costata DC., Coll.
Mem. 5: 39. 1829 ≡ Discopleura costata (Elliott) Steud., Nomencl. Bot., ed. 2, 1: 77, 520. 1840 – Type: U.S.A., Georgia,
“In inundatis, Ogeechee” (GH, photo of type!).
= Ptilimnium missouriense J.M. Coult. & Rose in Contr.
U.S. Natl. Herb. 12: 444. 1909 – Type: U.S.A., Missouri,
Allenton, 27 Aug. 1878, Letterman s.n. (US!, holotype).
4.4 Ptilimnium texense J.M. Coult. & Rose in Contr. U.S. Natl.
Herb. 12: 445. 1909 – Type: U.S.A., Texas, Near Hockley,
Sept. 1890, Thurow s.n. (US!, holotype).
4.5 Ptilimnium nuttallii (DC.) Britton in Mem. Torrey Bot.
Club 5: 244. 1894 ≡ Discopleura nuttallii DC., Coll. Mem.
5: 39. 1829 ≡ Discopleura capillacea var. nuttallii (DC.)
J.M. Coult. & Rose in Bot. Gaz. 12: 292. 1887 – Type:
U.S.A., Red River, Nuttall s.n. (G-DC!, holotype; BM! p.p.
the type is the specimen on the left side of the sheet, K!
p.p. the type is the specimen on the right side of the sheet,
PH!, NY!, isotypes).
Peucedanum verticillatum Raf., Fl. Ludov.: 81. 1817, nom. dub.
– Type: U.S.A., Louisiana (location unknown).
This name has been listed as a possible synonym of Ptilim
nium nuttallii (DC.) Britton. However, Rafinesque’s description
associated with this name is vague and could be applied to a
number of different species. It is unknown whether Rafinesque
based his description on an actual specimen and no type could
be located. Therefore, there is no way to determine for certain
that this name is a synonym of P. nuttallii and the designation
nomen dubium is applied.
ACKNOWLEDGEMENTS
The authors wish to thank the curators and collection managers
of the following herbaria for providing specimens for this study: AUA,
BAYLU, BRIT, CHICO, DAV, DOV, DUKE, EKY, F, FLAS, FSU, ILL,
ILLS, JEPS, LAF, LSU, MO, NCSC, NCU, NO, NY, OS, OSC, PH, RM,
Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
RSA-POM, TAMU, TENN, TEX, UARK, UC, US, USCH, USF, and
WVA. Thanks to Brenda Molano-Flores for accompanying M.A. Feist
on many collecting trips. Thanks to all the botanists, who are truly too
many to mention, that helped M.A. Feist to locate populations of her study
plants and even, in many cases, accompanied her into the field. This work
was partially supported by grants to M.A. Feist, including the Graduate
College Dissertation Research Travel Grant (University of Illinois), the
Francis M. and Harlie M. Clark Research Support Grant (School of Integrative Biology), the Herbert H. Ross Memorial Award (Illinois Natural
History Survey), the California Native Plant Society Research Award, the
Catherine H. Beattie Fellowship (Center for Plant Conservation and the
Garden Club of America), and the American Society of Plant Taxonomy
Graduate Student Research Grant. This work was also supported by funding from the National Science Foundation (DEB 0089452) to S.R. Downie.
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Appendix 1. Accessions from which nuclear rDNA ITS and cpDNA sequence data were obtained, with corresponding DNA accession and GenBank reference numbers and voucher information.
Taxon name — DNA accession number; voucher information; cpDNA GenBank accession number(s), ITS GenBank accession number. An asterisk (*)
indicates sequences newly generated for this study; a number sign (#) indicates the trnQ and trnK sequences used were part of a longer sequence of the entire
psbItrnK region deposited to GenBank; a paragraph sign (§) indicates the trnK sequence used was part of a longer sequence of the rps16 intron-trnK region
deposited to GenBank.
Atrema americanum Benth. & Hook. f. ex S. Watson — 1160; U.S.A., Texas, Williamson Co., jnt. Hwys. 183 and 29, Barclay & Perdue 785 (UC 184750);
EF185206#, EF177699. Cynosciadium digitatum DC. — 1571; U.S.A., Louisiana, Madison Parish, 1 mi E of Indian Lake, 28 May 1973, Jones 215 (ILL); EF185219#,
EF177704. 1986; U.S.A., Arkansas, Lafayette Co., 4 mi E of Red River, Hwy. 82, 24 May 1993, Sundell & al. 10,500 (ILL); EF185221#, EF177706. Daucosma
laciniata Engelm. & A. Gray — 2912; U.S.A., Texas, Uvalde Co., Garner State Park, 21 June 1958, Sullivan & Turner 33 (GA 114044); JQ652503*, JQ652549*.
3411; U.S.A., Texas, Bexar Co., San Antonio, 31 July 1921, Schulz 594 (US 1087113); JQ652500*, JQ652550*, JQ652463*. 3412; U.S.A., Texas, Hays Co., Wimberly,
5 July 1942, Fisher s.n. (F 1501788); JQ652501*, JQ652551*, JQ652464*. Lilaeopsis carolinensis J.M. Coult. & Rose — 2148; U.S.A., cultivated, origin unknown,
1985, Bogner s.n., material sent from Petersen GPL41 (C); EF185225#, AF466276. Lilaeopsis mauritiana G. Petersen & Affolter — 2150; Republic of Mauritius,
Le Val Nature Park, 3 May 1992, Windelov s.n., material sent from Petersen GPL81 (C); EF185226#, AF466277. Lilaeopsis novae-zelandiae (Gand.) A.W. Hill
— 2152; New Zealand. cultivated, origin unknown, material sent from Petersen GPL9 (C); EF185227#, AF466278. Lilaeopsis occidentalis J.M. Coult. & Rose
— 1999; U.S.A., Oregon, Douglas Co., East Gardiner, Hill & Dutton 32982 (ILLS 203634); EF185228#, AY360242. Limnosciadium pinnatum (DC.) Mathias &
Constance — 1511; U.S.A., Louisiana, Ouachita Parish, Ouachita W.M.A., 20 May 1987, Thomas & al. 99586I (MO 3680921); EF185229#, EF177717. 2395; U.S.A.,
Missouri, Stoddard Co., Otter Slough Conservation Area, 31 May 2000, Brant & al. 4380 (MO 5186226); EF185230#, EF177720. Limnosciadium pumilum (Engelm. & A. Gray) Mathias & Constance — 3742; U.S.A., Texas, San Ptricio Co., US 181 NW of Sinton, 5 Apr. 1984, Ertter 5263 (NY); JQ652499*, JQ652548*,
JQ652470*. Neogoezia gracilipes (Hemsl.) Hemsl. — 2270; Mexico, Oaxaca, Nochixtlan, N of La Joya, 2 Oct. 1993, Panero 3614 (UC 1611523); EF185232#,
EF177726. Neogoezia minor Hemsl. — 2274; Mexico, Oaxaca, Cerro San Felipe summit, Breedlove & Almeda 59951 (UC 1518420); EF185236#, EF177730.
Oxypolis canbyi (J.M. Coult. & Rose) Fern. — 2744; U.S.A., South Carolina, Richland Co., Carolina Bay on N side of Vero Road and ca. 0.3 mi E of Sec. Hwy.
2206, ca. 2 air mi NW of downtown Gadsden, 7 Sept. 1984, Nelson 3687 (NCU 537890); JQ652489*, JQ652540*, EF647756. 2747; U.S.A., North Carolina, Scotland Co., McIntosh Carolina Bay, US 401 NE of Laurinburg, 13 Sept. 1992, Sorrie 6946 (NCU 562048); JQ652490*, JQ652541*, EF647757. 2751; U.S.A., South
Carolina, Lee Co., just NE of Mt Pleasant Church, W of Lynchburg, 10 Sept. 1985, Nelson 4271 (NCU 537512); JQ652491*, JQ652542*. 2937; U.S.A., South
Carolina, Bamberg Co., Bamberg Bay Preserve, 28 Aug. 2005, Feist, MolanoFlores & Glitzenstein 3193 (ILLS); JQ652492*, JQ652543*, EF647759. 2938; U.S.A.,
South Carolina, Bamberg Co., Oxypolis Bay Preserve, 28 Aug. 2005, Feist, MolanoFlores & Glitzenstein 3194 (ILLS); JQ652493*, JQ652544*, EF647760. Oxypolis fendleri (A. Gray) A. Heller — 2350; U.S.A., Colorado, Boulder Co., Forth of July Canyon, 10 July 1962, Jones 34084 (ILL); JQ652502*, JQ652552*,
EF647767. 2351; U.S.A., Colorado, Boulder Co., along Boulder Creek, 24 June 1962, Jones 34450 (ILL); JQ652504*, JQ652553*, EF647768. 2368; U.S.A., New
Mexico, Rio Arriba Co., Ortega Mountains, 17 Aug. 1984, Hill 15181 (UC 1508862); JQ652505*, JQ652554*. 2369; U.S.A., Colorado, Chafee Co., CO 306, 14 mi
W of Buena Vista, 2 Aug. 1973, Haber & Given 2049 (CAN 370800); JQ652506*, EF185239§, EF177734. Oxypolis filiformis (Walter) Britton — 2371; U.S.A.,
Louisiana, Vernon Parish, E of Drake’s Creek, ca. 2 mi E of Johnsville Church and LA 10, ca. 7 mi E of Pickering, Kisatchie National Forest, 7 Sept. 1987, Thomas
101486 (DAO 574521); JQ652494*, EF185240§, EF177736. 2713; U.S.A., Florida, Alachua Co., Gainesville, N side of NE 39th Ave. N. just E of Main St., 9 Sept.
1987, Alcorn 155 (FLAS 166610); JQ652495*, JQ652545*, EF177737. Oxypolis filiformis × O. greenmanii — 2714; U.S.A., Florida, Bay Co., along US 231, 1.8
mi N of the junction with FL Rt. 388, N of Youngstown, 29 Aug. 1980, Judd & Perkins 2714 (FLAS 174297); JQ652498*, EF185242§, EF177739. Oxypolis greenmanii Mathias & Constance — 2717; U.S.A., Florida, Bay Co., Tyndall Airforce Base, 15 Sept. 1979, Judd & Perkins 2439 (FLAS 174274); JQ652496*, JQ652546*,
EF177738. 2941; U.S.A., Florida, Gulf Co., just E of Wetappo Creek and 3.6 mi S of FL 22, 2 Sept. 2005, Feist & MolanoFlores 3244 (ILLS); JQ652497*,
JQ652547*, EF647780. Oxypolis occidentalis J.M. Coult. & Rose — 1142; U.S.A., California, El Dorado County, Osgood Swamp, Follette s.n. (JEPS 82187);
EF185243#, AY360254. 1153; U.S.A., California: Fresno Co., Wishon Reservoir Dam, Call 2455 (UC 282880); EF185244#, EF177740. 2755; U.S.A., Oregon,
Douglas and Jackson Co., Abbott Creek Research Natural Area, ca. 20 mi W of Crater Lake near Abbott Butte, 29 July 1972, Mitchell 348 (USFS 406185),
JQ652507*, JQ652555*, EF647784. 2756; Canada. British Columbia: Queen Charlotte Islands, Graham Island, 2003, Cheney s.n. (ILLS), JQ652508*, JQ652556*,
EF647786. 2899; U.S.A., California: Tehama Co., Forest Rd. 26N09 at Cascade Creek, NW of Chico Meadows, 1.1 mi SE of Hwy. 32, 9 Sept. 1997, Oswald &
Ahart 8863 (JEPS 94369), JQ652509*, JQ652557*, EF647789. 2927; U.S.A., California: Sierra Co., ca. 1.25 mi N of Scales, ca. 2 mi (air) SE of Poverty Hill, 28
Sept. 2001, Ahart 9295 (JEPS 102455), JQ652510*, JQ652558*, EF647790. 2928; U.S.A., Oregon, Lane Co., Quaking Aspen Swamp, 6 mi W of S end of Cougar
Reservoir, 28 July 1979, Wagner 2318 (ORE 103195); JQ652511*, JQ652559*, EF647791. 2929; U.S.A., Oregon, Klamath Co., near W boundary of Crater Lake
Park, 24–29 Aug., Wynd 1745 (ORE 64782); JQ652512*, JQ652560*, EF647785. 3376; U.S.A., California, Kern Co., French Meadow, 3 Sept. 2007, Feist & Molano
Flores FM11; JQ652513*, JQ652561*, JQ652465*. 3413; Canada, Haida Guai, British Columbia, Feist & MolanoFlores Site 42; JQ652514*, JQ652562*. 3417;
U.S.A., California, Butte Co., 9 Sept. 2007, Feist & MolanoFlores BTC13; JQ652515*, JQ652563*, JQ652466*. 3442; U.S.A., Oregon, Lane Co., Quaking Aspen
Swamp, 13 Sept. 2007, Feist & MolanoFlores QAS25; JQ652516*, JQ652564*. 3464; U.S.A., California, San Bernardino Co., Lemon Lily Springs, 2 Sept. 2007,
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Feist & al. • Generic delimitations for Oxypolis and Ptilimnium
TAXON 61 (2) • April 2012: 402–418
Appendix 1. Continued.
Feist & MolanoFlores LLS24; JQ652517*, JQ652565*. 3465; U.S.A., California, San Bernardino Co., Lemon Lily Springs, 2 Sept. 2007, Feist & MolanoFlores
LLS16; JQ652518*, JQ652566*. 3466; U.S.A., California, San Bernardino Co., Lemon Lily Springs, 2 Sept. 2007, Feist & MolanoFlores LLS10; JQ652519*,
JQ652567*, JQ652467*. 3528; U.S.A., California, Sierra Co., Scales, 25 Oct. 2007, Feist & MolanoFlores S11; JQ652520*, JQ652568*, JQ652468*. 3532; U.S.A.,
California, Tulare Co., Nelson Trail, 4 Sept. 2007, Feist & MolanoFlores NT16; JQ652521*, JQ652569*, JQ652469*. Oxypolis rigidior (L.) Raf. — 1927; U.S.A.,
Illinois, Vermilion Co., Windfall Hill Prairie Nature Preserve, Windfall Prairie Seep, 17 July 1991, Phillippe, Morris, & Simon 19411 (ILLS 177487); JQ652522*,
EF185245§, AY360255. 1998; U.S.A., Louisiana, Winn Parish, along LA 126, 1.2 mi E of Jct. LA 1233, Kisatchie National Forest, 20 Sept. 1981, Kessler 1877
(ILL); EF185246#, EF177743. 2003; U.S.A., Illinois, Lake Co., SE corner of Tri-state Tollway and Buckley Rd. by RR, 13 Aug. 1981, Robertson 2640 (ILLS
166045); EF185247#, EF177744. Oxypolis ternata (Nutt.) A. Heller — 2735; U.S.A., South Carolina, Horry Co., 3.8 mi S. of Socastee and ca. 1 mi W. on dirt road,
25 Oct. 1970, Massey & Thomas 3480 (NCU 422851); JQ652523*, EF185248§, EF177745. 2738; U.S.A., North Carolina, Pender Co., Holly Shelter Game Land,
3 Oct. 1997, Horn & Dirig 362 (DUKE 363865); JQ652524*, EF185249§, EF177746. 2940; U.S.A., Florida, Wakulla Co., Saint Mark’s National Wildlife Refuge,
Panacea Unit Longterm Burn Plot (P13), ca. 2 km SE of Sopchoppy, 1 Sept. 2005, Feist, MolanoFlores & Glitzenstein 3222 (ILLS); JQ652525*, JQ652570*,
EF647809. Perideridia americana (Nutt. ex DC.) Reichenb. — 2033; U.S.A., Illinois, Shelby Co., NE of Assumption, 2 June 1981, Shildneck 12868 (ILL);
JQ652526*, JQ652527*, JQ652471*. Perideridia kelloggii (A. Gray) Mathias — 778; U.S.A., California, Sonoma Co., King Ridge Rd., 5 mi N. of Cazadero, 6 Aug.
1993, Ornduff & al. s.n. (UC), cult. University of California Botanical Garden, Berkeley (no. 81.0521); EF185251#, U78373. Ptilimnium ahlesii Weakley & G.L.
Nesom — 2648; U.S.A., South Carolina, Berkeley Co., Cooper River at the mouth of Durham Creek, 7 June 1990, McAninch 23 (NCU 557199); JQ652472*,
EF185252§, EF177747. 2969; U.S.A., North Carolina, Brunswick Co., just E of Brunswick River and just N of the 74–76 causeway, ca. 2 mi W of Wilmington,
10 June 2004, Weakley & LeBlond 7317 (sheet 2 of 2) (NCU); JQ652473*, JQ652528*, EF647814. Ptilimnium capillaceum (Michx.) Raf. — 2701; U.S.A., Virginia,
Lancaster Co., Bellwood Marsh, S of Rt. 3 bridge, W of Lancaster, 22 July 1994, Weldy 849 (BRIT); JQ652474*, JQ652529*, EF177748. 2703; U.S.A., Florida,
Nassau Co., White Oak Plantation in the wedge formed by the junction of the Little St. Mary’s River and St. Mary’s River about 8–10 mi NW of Yulee, 19 June
1997, Wilbur 67597 (BRIT); JQ652475*, JQ652530*, EF647822. Ptilimnium costatum (Elliott) Raf. — 1646; U.S.A., Illinois, Jackson Co., Shawnee National
Forest, 20 Sept. 1989, Stritch 2159 (ILLS 172136); EF185253#, EF177749. 1970; U.S.A., Illinois: Jackson Co., Shawnee National Forest, 11 Sept. 1989, Stritch 2124
(ILLS 172160); EF185254#, EF177750. 2402; U.S.A., Missouri, Wayne Co., Hattie’s Ford Fen Area, 12 Oct. 2001, Brant 4857 (MO 5573699); EF185256#, EF177752.
2707; U.S.A., Kentucky, Calloway Co., right 0.7 miles on KY 121S from KY 614, 9 Oct. 1972, Athey 2197 (NCU 473641); JQ652476*, JQ652531*. Ptilimnium
nodosum (Rose) Mathias — 2635; U.S.A., South Carolina; Aiken Co., Monetta, Windmill High Pond, Carolina Bay Road, 20 July 1992, Hill 23921 (USF 206922);
JQ652480*, JQ652533*, EF647843. 2784; U.S.A., South Carolina, Aiken Co., Maddox SC74; JQ652481*, EF185257§, EF177753. 2787; U.S.A., Maryland, Mad
dox MG4, JQ652482*, EF185258§, EF177754. 2900; U.S.A., South Carolina, Saluda Co., near Hibernia, Saluda Highpond, 11 May 2005, Feist & MolanoFlores
3287 (ILLS); JQ652483*, JQ652534*, EF647841. 2902; U.S.A., Georgia, Greene Co., Siloam Outcrop, 12 May 2005, Feist & MolanoFlores Siloam5; JQ652484*,
JQ652535*, EF177754. 2930; U.S.A., Arkansas, Yell Co., Ouachita Mountains, below the Hwy. 27 bridge over Irons Fork, 16 Oct. 1990, Bates 10558 (UARK);
JQ652485*, JQ652536*, EF647851. 2931; U.S.A., Alabama, DeKalb Co., Little River near AL Hwy. 35 bridge, DeSoto State Park, 15 July 1987, Freeman s.n. (AUA
46749); JQ652486*, JQ652537*, EF647853. 2934; U.S.A., West Virginia, Berkeley Co., along Back Creek, 25 Aug. 2005, Feist, Harmon & O’Malley 3285 (ILLS);
JQ652487*, JQ652538*, EF647854. 2936; U.S.A., North Carolina, Granville County, Tar River, 26 Aug. 2005, Feist 3286 (ILLS); JQ652488*, JQ652539*, EF647856.
Ptilimnium nuttallii (DC.) Britton — 2165; U.S.A. Oklahoma, Rogers Co., Claremore, along railroad in moist ground, 12 June 1974, Jones 3030 (ILL); EF185259#,
AY360256. 2617; U.S.A. Arkansas, Ashley Co., SE of Hamburg and NE of Ark. 52, 20 June 1986, Thomas 97154 (WVA 114836); JQ652478*, EF185260§, EF177758.
2623; U.S.A., Illinois, Randolph Co., W of Sparta, 16 July 2003, Feist 2510 (ILLS); JQ652477*, EF185261§, EF177759. Ptilimnium texense J.M. Coult. & Rose
— 1981; U.S.A., Louisiana, Natchitoches Parish, moist seepage area beside LA 479 at Strange Rd., W of Goldonna in Kisatchie National Forest, 14 Aug. 1989,
Thomas & Bell 112081 (ILL); EF185255#, EF177751. 2905; U.S.A., Texas, Anderson Co., Gus Engeling Wildlife Management Area, NW of Palestine, Lake 2 bog
area, pasture 2, 16 Oct. 1993, Dubrule Reed 1354 (TAMU 24011); JQ652479*, JQ652532*, EF647825. Trepocarpus aethusae Nutt. — 1660; U.S.A., Illinois, Saline
Co., US Rt. 45, E of Harrisburg levee, 7 July 1999, Hill 31876 (ILLS 201642); EF185279#, EF177761.
Appendix 2. Accessions from which fruit anatomical observations were made with voucher information.
Taxon name — voucher information.
Cynosciadium digitatum DC. — U.S.A., Arkansas, Monroe Co., Ark. Hwy. 1, ca. 2 mi NE of Cross Roads at Branch Missionary Baptist Church, Sundell
15406 (BRIT). — U.S.A., Louisiana, Morehouse Pa., ½ mi E of Jones, 2 July, 1968, J. Thieret s.n. (SMU 37382). Limnosciadium pinnatum (DC.) Mathias &
Constance — U.S.A., Texas, Red River Co., N of Clarksville, 28 June 1945, Lundell 14012 (LL). — U.S.A., Missouri, Stoddard Co., Otter Slough Conservation
Area, 31 May 2000, Brant & al. 4380 (MO 5186226). Limnosciadium pumilum (Engelm. & A. Gray) Mathias & Constance — U.S.A., Texas, Calhoun Co.,
vacant lot in Port O’Connel, 13 Apr. 1952, Gentry 1996 (BRIT). — U.S.A., Texas, San Patricio Co., US 181 NW of Sinton, 5 Apr. 1984, Ertter 5263 (NYBG).
Oxypolis canbyi (J.M. Coult. & Rose) Fern. — U.S.A., South Carolina, Lee Co., W of Lynchburg, 10 Sept. 1985, J. Nelson 4269 (USCH 032054). — U.S.A.,
Georgia, Lee Co., NE Leesberg, 22 Aug. 1948, Muenscher s.n. (NCU 65120). Oxypolis fendleri (A. Gray) A. Heller — U.S.A., Wyoming, Albany, Medicine
Bow Forest, Elk Creek Study Bog, Sturges 205 (RM 272453). — U.S.A., Wyoming, La Plata Mines, E. Nelson s.n. (RM 12350). — U.S.A., Colorado, Boulder
Co., Eldora, 22 July 1953, G.N. Jones 20071 (ILL). Oxypolis filiformis (Walter) Britton — U.S.A., South Carolina, Charleston Co., Francis Marion N.F., 29 Aug.
2009, Feist & MolanoFlores 3197 (ILLS). — U.S.A., Florida, Calhoun Co., 29 Aug. 1980, Judd & Perkins 2729 (FLAS 174320). Oxypolis greenmanii Mathias
& Constance — U.S.A., Florida, Gulf Co., 17 mi N of Port St. Joe, 7 Sept. 1955, Godfrey 53756 (NCSC 52879). — U.S.A., Florida, Bay Co., Tyndall Airforce
Base, 15 Sept. 1979, Judd & Perkins 2439 (FLAS 174274). Oxypolis occidentalis J.M. Coult. & Rose — U.S.A., California, Lemon Lily Springs, 2 Sept. 2007,
Feist & MolanoFlores 4106 (ILLS). — U.S.A., Oregon, Lane Co., Quaking Aspen Swamp, 17 Sept. 2007, Feist & MolanoFlores 4131 (ILLS). — U.S.A.,
California, Kern Co. Portuguese Meadow, 27 Sept. 1936, L. Benson 8007 (POM 287809). Oxypolis rigidior (L.) Raf. — Canada, Ontario, Essex Co., 5.3 km E
& 5.7 km N of Leamington, Oldham 6994 (CAN 522163). — U.S.A., Indiana, Tippecanoe Co., Ross Biological Reserve, 2 Oct. 1958, Webster & Webster 7206
(DUKE 147518). — U.S.A., Tennessee, Munroe Co., Cherokee N.F., 21 Sept. 1938, M. Shaver s.n. (UGA 79326). Oxypolis ternata (Nutt.) A. Heller — U.S.A.,
Florida, Franklin Co., near Wright Lake, Apalachicola N.F., 12 Nov. 1969, Godfrey 69254 (USF 88592). — U.S.A., North Carolina, Lee Co., 0.3 mi E of jct. of
1176 and 1179 on 1176, 17 Oct. 1967, Bozeman 11639 (NCU 303709). Ptilimnium ahlesii Weakley & G.L. Nesom — U.S.A., Georgia, Chatham Co., Savannah
National Wildlife Refuge, along Hwy 17, 14 July 1966, Bozeman 6100 (NCU 339364). — U.S.A., South Carolina, Beaufort Co., Trichinham Plantation, 27 June
1956, Bell 3767 (NCU 97910). Ptilimnium capillaceum (Michx.) Raf. — U.S.A., Louisiana, Vermillion Pa., Pecan Island, 28 June 1963, Valentine s.n. (SMU).
— U.S.A., South Carolina, Clarendon Co., at St. Paul, J. Nelson 13280 (USCH 58378). Ptilimnium costatum (Elliott) Raf. — U.S.A., Illinois, Washington Co.,
25 Sept. 2001, Feist s.n. (ILLS). U.S.A., Oklahoma, Pushtamaha Co., Antlers, 23 Oct. 1915, Palmer 8989 (MO 793414). Ptilimnium nodosum (Rose) Mathias
— U.S.A., South Carolina, Aiken Co., Janet Harrison High Pond, 11 May 2005, Feist & MolanoFlores 2967.1 (ILLS). — U.S.A., West Virginia, Morgan Co.,
along Sleepy Creek, 23 Aug. 2005, Feist 3188 (ILLS) — U.S.A., Alabama, Tuscaloosa Co., North River, 15 mi N of Tuscaloosa, Easterly Ala. 146 (WVA114892).
Ptilimnium nuttallii (DC.) Britton — U.S.A., Texas, Kaufman Co., 1.75 mi E of Terrell, 14 June 1946, Cory 53275 (SMU). — U.S.A., Kansas, Labette Co.,
Mound Valley, 19 July 1995, Freeman 7322 (WVU 114956). Ptilimnium texense J.M. Coult. & Rose — U.S.A., Texas, Freestone Co., 14.5 mi S. of Fairfield,
2 Oct. 1949, Shinners 11830 (SMU). — U.S.A., Texas, Tyler Co., ca. 2 mi E of Warren, 5 Oct. 1969, Correll 3813 (LAF 46206).
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