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Hotspots of subterranean biodiversity in caves and wells

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Abstract

We documented 18 caves and two karst wells that have 20 or more stygobites and troglobites. Crustacea dominated the aquatic fauna. Taxonomic composition of the terrestrial fauna varied, but Arachnida and Insecta together usually dominated. Geographically, the sites were concentrated in the Dinaric Karst (6 caves). Sites tended to have high primary productivity or rich organic input from the surface, be large caves, or have permanent groundwater (phreatic water). Over the past few years, there has been a growing aware-ness and concern with biodiversity worldwide. Books and monographs with a focus on biodiversity have appeared (e.g., Wilson 1992; Master et al. 1998) and a rapidly increasing amount of information is available about patterns of biodiver-sity for many groups of organisms. The same can be said for the fauna of caves and other subterranean habitats. Tabulations and often lists of cave and subsurface-limited species are avail-able for many countries in Stygofauna Mundi (Botosaneanu 1986) and in the multi-volume Encyclopaedia Biospeologica published by the Societe de Biospeologie in Moulis, France. Extensive lists of the caves and wells in which a particular sub-terranean species is found have been published. Prominent examples include Virginia (Holsinger & Culver 1988), the Iberian Peninsula (Belles 1987), and Slovenia (Bole et al. 1993). While not as well studied as temperate areas, similar information exists for many tropical regions (Peck & Finston 1993; Deharveng & Bedos 2000). Understanding patterns of subterranean biodiversity requires an understanding of regional patterns. In general, the number of species found in any one cave or subsurface site is small relative to the number of species in the region. Cave habitats (as opposed to small cavity, interstitial habitats such as the underflow of rivers) are especially fragmented, with differ-ent species occurring in caves only a few kilometers apart. For example, of the more than 500 caves biologically investigated in West Virginia, the maximum number of obligate species in any cave is 14, but the state, with a karst area of 2500 km², has 76 obligate species. It is the documentation of these regional patterns and their explanation that is one of the major tasks of speleobiologists over the next several decades (Peck & Finston 1993; Sket 1999a). Nevertheless, it is important not to neglect diversity pat-terns at individual sites. Even though most subterranean bio-diversity results from the accumulation of different species from nearby sites, there are some outstanding examples of high biodiversity from individual caves and wells that are worth documenting. Protection and concern for the subterranean fauna of a region often begin with protection and concern for a particular cave. It is, after all, individual caves and wells that provide the building blocks for regional biodiversity. The purpose of this short communication is to enumerate those caves and wells that are particularly rich in subterranean species and to offer some preliminary explanations for these biodiversity hotspots, both in terms of their geographic distri-bution and in terms of the types of sites. We use the terms troglobite for terrestrial, cave-limited species and stygobite for aquatic, cave-limited species. Stygobites also include intersti-tial species but they are not considered here.
Journal of Cave and Karst Studies, April 2000 • 11
David C. Culver and Boris Sket - Hotspots of Subterranean Biodiversity in Caves and Wells. Journal of Cave and Karst Studies 62(1):11-17.
HOTSPOTS OF SUBTERRANEAN
BIODIVERSITY IN CAVES AND WELLS
DAVID C. CULVER
Department of Biology, American University, 4400 Massachusetts Ave., NW, Washington, DC 20016, USA,
dculver@american.edu
BORIS SKET
Department of Biology, Biotechnical Faculty, University of Ljubljana, P.O. Box 2995, 1001 Ljubljana, SLOVENIA,
b.sket@uni-lj.si
We documented 18 caves and two karst wells that have 20 or more stygobites and troglobites. Crustacea
dominated the aquatic fauna. Taxonomic composition of the terrestrial fauna varied, but Arachnida and
Insecta together usually dominated. Geographically, the sites were concentrated in the Dinaric Karst (6
caves). Sites tended to have high primary productivity or rich organic input from the surface, be large
caves, or have permanent groundwater (phreatic water).
Over the past few years, there has been a growing aware-
ness and concern with biodiversity worldwide. Books and
monographs with a focus on biodiversity have appeared (e.g.,
Wilson 1992; Master et al. 1998) and a rapidly increasing
amount of information is available about patterns of biodiver-
sity for many groups of organisms. The same can be said for
the fauna of caves and other subterranean habitats. Tabulations
and often lists of cave and subsurface-limited species are avail-
able for many countries in Stygofauna Mundi (Botosaneanu
1986) and in the multi-volume Encyclopaedia Biospeologica
published by the Societe de Biospeologie in Moulis, France.
Extensive lists of the caves and wells in which a particular sub-
terranean species is found have been published. Prominent
examples include Virginia (Holsinger & Culver 1988), the
Iberian Peninsula (Belles 1987), and Slovenia (Bole et al.
1993). While not as well studied as temperate areas, similar
information exists for many tropical regions (Peck & Finston
1993; Deharveng & Bedos 2000).
Understanding patterns of subterranean biodiversity
requires an understanding of regional patterns. In general, the
number of species found in any one cave or subsurface site is
small relative to the number of species in the region. Cave
habitats (as opposed to small cavity, interstitial habitats such as
the underflow of rivers) are especially fragmented, with differ-
ent species occurring in caves only a few kilometers apart. For
example, of the more than 500 caves biologically investigated
in West Virginia, the maximum number of obligate species in
any cave is 14, but the state, with a karst area of 2500 km², has
76 obligate species. It is the documentation of these regional
patterns and their explanation that is one of the major tasks of
speleobiologists over the next several decades (Peck & Finston
1993; Sket 1999a).
Nevertheless, it is important not to neglect diversity pat-
terns at individual sites. Even though most subterranean bio-
diversity results from the accumulation of different species
from nearby sites, there are some outstanding examples of high
biodiversity from individual caves and wells that are worth
documenting. Protection and concern for the subterranean
fauna of a region often begin with protection and concern for a
particular cave. It is, after all, individual caves and wells that
provide the building blocks for regional biodiversity.
The purpose of this short communication is to enumerate
those caves and wells that are particularly rich in subterranean
species and to offer some preliminary explanations for these
biodiversity hotspots, both in terms of their geographic distri-
bution and in terms of the types of sites. We use the terms
troglobite for terrestrial, cave-limited species and stygobite for
aquatic, cave-limited species. Stygobites also include intersti-
tial species but they are not considered here.
M
ETHODS AND MATERIALS
We used an arbitrary cutoff of 20 or more obligate subter-
ranean species for a site to be included. This resulted in a man-
ageable number of sites to enumerate, representing less than
one-tenth of one per cent of the sites sampled. We limited our
attention to large cavities—caves and wells that intersect large
cavities. According to Curl (1964), proper caves are large
enough for humans to enter (and proper entrances are
entrances large enough for humans to enter). We restricted our
attention to proper caves, whether they do or do not have prop-
er entrances, since many wells in carbonate rock intersect
proper caves that lack proper entrances. What constitutes a
single cave is a matter of considerable debate and confusion.
We restricted our attention to connected voids, either water- or
air-filled, regardless of how many separate entrances or names
Dokumentirala sva 18 jam in dva kraška vodnjaka, iz katerih je znanih 20 ali vec vrst troglobiontov in
stigobiontov. V vodni favni preladujejo raki. Taksonomski sestav kopenske favne je raznolik, vendar
pajkovci in zuzelke skupaj navadno prevladujejo. Najvec takšnih jam (šest) je v Dinarskem krasu.
Nadpovprecno so zastopane jame z lastno primarno produkcijo ali bogatim vnosom hrane s površja,
obsezne jame in jame, ki vkljucujejo tudi freatsko plast.
12 • Journal of Cave and Karst Studies, April 2000
HOTSPOTS OF SUBTERRANEAN BIODIVERSITY IN CAVES AND WELLS
the cave had. We specifically excluded porous aquifers—they
have been less thoroughly studied and are likely to have a pat-
tern very different than that of proper caves. We also exclud-
ed the few known fungal parasites.
In order to generate the list, we consulted with many col-
leagues throughout the world with the request for information
about any particular cave or well fauna. We consulted avail-
able species lists from throughout the world. An Excel file of
the species list is available from the authors. We are aware of
the fact that a number of caves may be missing from our list
because we lack a faunal list. We also expect some species to
be shown eventually not to be limited to caves. However, none
of the sites enumerated here is likely to be excluded from the
list owing to such changes.
R
ESULTS
Eighteen caves and two wells have 20 or more obligate
species. Of the 20 sites, fourteen are from Europe (five of
them from Slovenia and five from France), three from North
America, one from Australia, one from southeast Asia, and one
from an island in the Atlantic (Fig. 1). The major taxonomic
composition of these faunas is listed in Table 1. Each site is
briefly described below.
San Marcos Spring, Texas, USA—This artesian spring
serves as an exit point for water from the Edwards Aquifer.
Two-thirds of its aquatic species are crustaceans, of which 11
are amphipods (Holsinger & Longley 1980, Table 1).
Endemism is high, with 11 endemics representing 40% of the
fauna. The aquifer itself is about 280 km long and 8-64 km
wide. Oil and peat deposits above the aquifer may be the pri-
mary energy input into the system (Longley 1981). The
aquifer is threatened by excessive drawdown, both by agricul-
tural interests and the City of San Antonio.
Shelta Cave, Alabama, USA—Slightly over 700 m long,
Shelta Cave consists of three large rooms of considerable vol-
ume that intersect permanent groundwater. Pioneering biolog-
ical studies by Cooper (1975) led to the purchase of the
entrance sink by the National Speleological Society. Half of
the species are aquatic (Table 1). No group dominates the ter-
restrial fauna, but crustaceans dominate the aquatic fauna.
Installation of a bat-unfriendly gate apparently led not only to
a loss of bats, but to a major decline in the population sizes of
the aquatic species (Hobbs & Bagley 1989; Culver 1999).
Mammoth Cave, Kentucky, USA—Mammoth Cave is the
longest known cave in the world, with over 500 km of sur-
veyed passages. Most of the cave is within the boundaries of
Mammoth Cave National Park. It rivals the Postojna-Planina
Cave system of Slovenia in the amount of study devoted to the
biota. Major discussions of the fauna of Mammoth Cave
include Packard (1888), Barr (1967), and Poulson (1992).
One-third of the fauna is aquatic, two-thirds terrestrial.
Figure 1. Location of hotspots of subterranean biodiversity: 1—San Marcos Spring,Texas; 2—Shelta Cave,Alabama; 3—
Mammoth Cave, Kentucky; 4—Walsingham Caves, Bermuda; 5—Triadou Wells, France; 6—Baget/Grotte de Sainte
Catherine, France; 7—Goueil di Her/Reseau Trombe, France; 8—Résurgence de Sauve/Vidourle souterrain, France; 9—
Cent-fons, France; 10—Grotta dell’Arena, Italy; 11—Buso della Rana, Italy; 12—Sistem Postojna-Planina; 13—Šica-Krka
Sistem, Slovenia; 14—Jama Logarcek, Slovenia; 15—Grad (Osapka Jama), Slovenia; 16—Krizna Jama, Slovenia; 17—
Vjetrenica Jama, Bosnia & Hercegovina; 18: Pestera de la Movile, Romania; 19—Salukkang-Kallang/Towakkalak,
Indonesia; 20—Bayliss Cave, Australia.
Journal of Cave and Karst Studies, April 2000 • 13
CULVER AND SKET
Taxonomically, arachnids dominate the terrestrial fauna and
crustacea dominate the aquatic fauna (Table 1). Noteworthy is
the co-occurrence of five species of trechine beetles in the
closely related genera Neaphaenops and Pseudanophthalmus.
Walsingham Caves, Bermuda—This complex of anchiha-
line caves (ones with a direct connection to the sea), including
Walsingham Sink Cave, Walsingham Cave, and Tuckers Town
Cave, is ~1 km long, with most of the passages submerged.
With a freshwater lens and a redox boundary between fresh
and saltwater, Walsingham Cave likely has considerable sec-
ondary and possibly primary productivity. The fauna is entire-
ly aquatic and dominated by Crustacea from many orders (Sket
& Iliffe 1980, Table 1). Some of the micro-crustacean species
may occur outside the hypogean realm.
Triadou Wells, France—Two wells (F1 and P1) only a few
meters apart in the Lez Basin in southern France at a depth of
50 m yielded a variety of stygobites, especially crustaceans
(Malard et al. 1994, Table 1). Located in a major karst area,
the wells tap a network of fissures and solution tubes begin-
ning at a depth of ~35 m.
Baget—Sainte Catherine System, France—This subter-
ranean system is situated in the Pyrenees, near Moulis, in the
small valley of Lachein. The basin occupies an area of 13.25
km². The object of intense study by R. Rouch and his col-
leagues for more than 20 years (e.g., Rouch & Danielopol
1997), three components have been extensively sampled—the
outlet of the subterranean stream, a mostly flooded conduit
(Aven de la Peyrere), and Grotte de Sainte-Catherine. The
aquatic fauna is especially diverse, with 21 species of
Crustacea (Table 1).
Goueil di Her/Reseau Trombe, France—The Trombe sys-
tem is located in the Pyrenees in the Arbas Massif. The sub-
terranean system consists of over 100 km of air- and water-
filled passages, with numerous pits providing access to the
submerged part of the system. The most extensively studied
part of the system is Goueil di Her and its resurgence. The ter-
restrial and aquatic fauna are about equally diverse (Table 1),
with Crustacea and Coleptera predominating.
Resurgence de Sauve and subterreanean Vidourle,
France—The fountain of Sauve, near Montpelier, is the resur-
gence of the subterranean Vidourle River, which drains about
75 km² of area. The fountain is well known on account of the
violence of its floods. Twenty stygobites have been collected
from the watercourse, and most of these are crustaceans
(Juberthie & Juberthie-Jupeau 1975, Table 1).
Cent-fons, France—The cave, which is flooded, and its
resurgence are located at the southern border of the Massif
Central. There are ten resurgences. The populations are
diverse (Table 1) and abundant—about 16,500 crustaceans
have been ejected out of the resurgence in ten weeks (C.
Juberthie, pers. comm., October, 1999).
Grotta dell’Arena, Italy—This fossil cave is located in an
alpine pasture (1512 m msl) and consists of a single large
gallery less than 100 m long with the floor covered by large
blocks of limestone. Percolating water forms some small, per-
manent pools at the end of the gallery. The stygobitic fauna
consists of six, mostly tiny crustaceans (Table 1). Beetles and
archnids dominate the richer terrestrial fauna.
Cave Buso della Rana, Italy—This large and complex cave
system, with more than 20 km of passage, shows a high habi-
tat diversity, with an alternation of inactive and active branch-
es. A small permanent brook flows along the main passage and
emerges at the entrance. During the rainy season, most of the
cave may be flooded. Crustaceans dominate the aquatic fauna
(Table 1). None of the terrestrial groups is particularly diverse.
Grad (Osapska Jama), Slovenia—The entrance is a boiling
spring with 1070 m of passage accessible during the dry sea-
son. After rains, the water can rise 50 m and flood most of the
cave. There is no connection with a surface stream except at
the periodically emerging spring. Terrestrial fauna is largely
un-investigated, and the stygobitic fauna includes 17 crus-
taceans (including two amphibious Oniscoidea) and among
them the large cirolanid isopod Sphaeromides virei (Brancelj
1992, Table 1).
Krizna Jama, Slovenia—This is a hydrologically active but
nevertheless beautifully decorated cave of more than 8000 m
length. It is isolated from permanent surface rivers and, there-
fore, has very few non-stygobitic animals. The fauna is very
scarce but species rich. Crustaceans (Table 1) dominate the
rich aquatic fauna. Remarkable is the high number of gas-
tropods: 2 terrestrial and 6 aquatic species have been found.
Jama Logarcek, Slovenia—A multi-level cave with a river
in its deepest corridors; it measures 2300 m. It is situated close
to Postojna-Planina Cave System, but with less apparent habi-
tat diversity. Two-thirds of the fauna is aquatic, with gastropod
and crustacean species predominating (Table 1). There also is
an exceedingly rich epizoic ciliate protozoan fauna, described
from one specimen of the bizarre isopod Monolistra spinosis-
sima (Hadzi 1940).
Sistem Postojna-Planina, Slovenia—There are 17 km and 6
km of passages connected by 2 km of flooded corridors. The
sinking river in the main passages is inhabited by a rich assort-
ment of stygobites, stygophiles, and accidental surface species
(Sket 1979). Hydrologically inactive parts of the system con-
tain other aquatic and terrestrial habitats. This is the type
locality of a number of “first cave” animals, including the first
described troglobite, the beetle Leptodirus hochenwarti and
the European cave salamander, Proteus anguinus. It also is a
site of long-term ecological studies (Sket & Velkovrh 1981).
Slightly over half of the species are aquatic, with a rich crus-
tacean, snail and oligochaete fauna. Beetles dominate the ter-
restrial troglobitic fauna (Table 1). Some of the cave has been
heavily visited by tourists since 1818.
Šica-Krka Sistem, Slovenia—Šica-Krka Sistem consists of
two caves 1700 m and 250 m long, hydrologically connected
by 5 km of underground flow. This sinking river is inhabited
mostly by surface animals at the sink and mostly by stygobites
at the resurgence. Most parts of the cave are hydrologically
active and more than 70 percent of the cave fauna is aquatic,
primarily crustacean (Table 1).
14 • Journal of Cave and Karst Studies, April 2000
HOTSPOTS OF SUBTERRANEAN BIODIVERSITY IN CAVES AND WELLS
Higher Groups San Marcos Spring Shelta Cave Mammoth Cave Walsingham Caves Triadou Wells F1 & P1
TX, USA AL, USA KY, USA Bermuda France
AQUATIC
Protista: Ciliata (epizoic)
Cnidaria
Aschelminthes: Nematoda
Rotatoria
Nemertini
Turbellaria: Tricladida 1 1 2
Temnocephala
Annelida: Hirudinea
Oligochaeta 1 3
Polychaeta 4
Mollusca: 5 1 3 3
Crustacea: 18 8 11 29 28
Arachnida: Acarina 1
Insecta: 1
Vertebrata: Amphibia 2 1
Pisces 1
Aquatic Subtotal 27 12 15 37 34
TERRESTRIAL
Annelida: Oligochaeta
Mollusca: Gastropoda 1 1
Crustacea: Isopoda 1
Arachnida: 2 12
Symphyla:
Diplopoda: 1 2
Chilopoda:
Insecta: Collembola 2 4
Coleoptera 3 5
Other 2 2
Terrestrial Subtotal 12 26
TOTAL 27244137 34
Table 1. Taxonomic summary of stygobites and troglobites found in the 20 caves and karst wells. See Figure 1 for their
location.
Higher Groups
Baget—Ste. Catherine Goueil di Her Resurgence de Sauve Cent-fons Grotta dell’Arena
System Reseau Vidourle souterrain France Italy
France Trombe, France France
AQUATIC
Protista: Ciliata (epizoic)
Cnidaria
Aschelminthes: Nematoda
Rotatoria
Nemertini
Turbellaria: Tricladida 1
Temnocephala
Annelida: Hirudinea
Oligochaeta 1 1
Polychaeta
Mollusca: 2131
Crustacea: 21 11 14 20 6
Arachnida: Acarina 3 1
Insecta:
Vertebrata: Amphibia
Pisces
Aquatic Subtotal 24 14 20 22 6
TERRESTRIAL
Annelida: Oligochaeta
Mollusca: Gastropoda 1
Crustacea: Isopoda 1 1
Arachnida: 1 2 5
Symphyla:
Diplopoda: 1 2 1
Chilopoda:
Insecta Collembola 3 1
Coleoptera 4 6 6
Other
Terrestrial Subtotal 9 12 14
TOTAL 33262022 20
Higher Groups Buso della Rana Grad (Osapka Jama) Krizna Jama Jama Logarcek Sistem Postojna-Planina
Italy Slovenia Slovenia Slovenia Slovenia
AQUATIC
Protista:Ciliata (epizoic) 1 9 1
Cnidaria 1
Aschelminthes: Nematoda
Rotatoria
Nemertini
Turbellaria: Tricladida 1 1
Temnocephala 32
Annelida: Hirudinea 1
Oligochaeta 6 7
Polychaeta 1
Mollusca: 1167 8
Crustacea: 14 15 15 8 26
Arachnida: Acarina
Insecta:
Vertebrata: Amphibia 11
Pisces
Aquatic Subtotal 15 17 29 28 48
TERRESTRIAL
Annelida: Oligochaeta
Mollusca: Gastropoda 1 2 4 3
Crustacea: Isopoda 2 1 1 2
Arachnida: 1 4 3 9
Symphyla:
Diplopoda: 11 2
Chilopoda:
Insecta: Collembola 1 9
Coleoptera 3166 8
Other 1
Terrestrial Subtotal 5 3 16 15 36
TOTAL 20204543 84
Journal of Cave and Karst Studies, April 2000 • 15
CULVER AND SKET
Higher Groups
Sica-Krka Sistem Vjetrenica Jama Pestera de la Movile Salukkang Kallang Bayliss Cave
Slovenia Bosnia- Romania Towakkalak N. Queensland
Herzegovina Indoesia Australia
AQUATIC
Protista: Ciliata (epizoic)
Cnidaria 1 1
Aschelminthes: Nematoda 3 3
Rotatoria 2
Nemertini 1
Turbellaria: Tricladida 1 1
Temnocephala 3 3
Annelida: Hirudinea 1 1
Oligochaeta 1 2
Polychaeta 1
Mollusca: 6 8 1
Crustacea: 12 23 7 4
Arachnida: Acarina
Insecta: 1
Vertebrata: Amphibia 1 1
Pisces 2
Aquatic Subtotal 27 39 18 7
TERRESTRIAL
Annelida: Oligochaeta 1
Mollusca: Gastropoda 3 2
Crustacea: Isopoda 1343 2
Arachnida: 2 4 10 8 5
Symphyla: 1
Diplopoda: 3 1 3 4
Chilopoda: 1 3 1
Insecta: Collembola 1 3 4 1
Coleoptera 1641 3
Other 1 2 2 8
Terrestrial Subtotal 7 21 29 21 24
TOTAL 34604728 24
16 • Journal of Cave and Karst Studies, April 2000
HOTSPOTS OF SUBTERRANEAN BIODIVERSITY IN CAVES AND WELLS
Vjetrenica Jama in Popovo polje, Bosnia and
Hercegovina—This complex cave system has 7.6 km of pas-
sages, which include a number of small streams, pools, and
trickles of water. There are no sinking streams but there are
extensive opportunities for the import of organic debris
through crevices and shafts. About two-thirds of the fauna is
aquatic, and dominated by Crustacea (Pretner 1963, Sket
1999a, Table 1). Noteworthy are the amphibious catopid bee-
tle and amphipod species that occupy rock walls covered by a
film of water trickling from above (hygropetric habitat).
Movile Cave, Romania—Movile Cave is a small, mostly
water filled cave near the coast of the Black Sea. Slightly more
than a third of its fauna is aquatic. No one taxonomic group
dominates either the aquatic or terrestrial fauna (Table 1), and
the fauna, as a whole, has the remarkably high level of over
65% endemism (Sarbu 2000). Extensive chemoautotrophic
production occurs in the cave system (Sarbu, Kane et al. 1996).
The cave is threatened by extensive trash dumping in the sink-
hole in which the entrance is located.
Gua Salukkan Kallang—Towakkalak, Indonesia—This
immense river cave system has over 20 km of passage, a large
bat population, and 25% of the obligate cave fauna is aquatic.
Comprising mostly undescribed species, crustaceans predomi-
nate in the aquatic fauna and arachnids in the terrestrial cave
fauna (Deharveng & Bedos 2000, Table 1).
Bayliss Cave, Australia—Bayliss Cave is a small (900 m)
cave formed in lava. It is a “bad-air” cave, with up to 200
times the ambient atmospheric level of carbon dioxide
(Howarth & Stone 1990), likely the result of in situ production
of CO
2 from the oxidation of organic matter (James 1977).
The cave-limited fauna is entirely terrestrial with no one group
dominating (Table 1).
D
ISCUSSION
It is worthy reiterating that, compared to surface habitats,
diversity in caves is low (Sket 1999a) and that most diversity
in caves and wells is expressed regionally rather than locally.
Sket (1999a) gives a variety of reasons for the low diversity
compared to surface habitats, including reduced area of eco-
tonal regions between surface and subsurface, reduced subter-
ranean habitat diversity, and reduced food resources. The frag-
mented nature of the cave habitat and restricted opportunities
for dispersal keep local diversity much lower than regional
diversity.
One obvious difference, even among the caves and wells
listed in Table 1, is the breadth of taxonomic scrutiny. In only
a scattering of caves have epizoic ciliates been collected, let
alone described (Walsingham Cave and Logarèek Cave in
Table 1). Likewise, microcrustaceans have not been collected
from all sites; even those listed in Table 1. It seems that
Copepoda in North American subterranean waters have been
nearly completely ignored. Nonetheless, most of the species in
all sites listed in Table 1 are easily observed and collected.
What in the way of generalities can be gleaned from the list
of caves and wells with high species diversity? First, there is
a remarkable concentration of sites in the Dinaric karst of
Slovenia, Croatia, and Bosnia-Herzegovina, which is also the
richest region of subterranean biodiversity (Sket 1999b). This
is particularly evident in the stygobitic fauna. Of the ten sites
with 25 or more stygobites (Table 1), six are in the Dinaric
karst. France also has a concentration of sites, although, in
general, diversity at these sites is slightly less than that at
Dinaric karst sites. Sket (1996) points out that the Dinaric
Karst in general, and the Slovenia karst in particular, is exten-
sive in areal extent and with a rich geologic history. Poulson
(1992) makes a similar argument for Mammoth Cave. Second,
sites with high productivity, especially chemoautotrophy, com-
pared to other subsurface sites are well represented. These
include Washingham Cave, Movile Cave, Bayliss Cave, and
San Marcos Springs. Such high productivity caves are rare.
This reinforces the widely held view that caves are resource
poor (e.g. Sket 1999a). Gua Salukkang Kallang Towakkalak
and Sistem Postojna-Planina also can be counted as caves with
high (secondary) productivity, but the scarcity of high diversi-
ty caves in the tropics is still a puzzle. Another example of a
high diversity cave with high productivity is Cabaret Cave in
Western Australia. This small cave has extensive root mats
penetrating the aquatic habitat, with over 40 species in a 20 m
reach of stream (Jasinska et al. 1996; Jasinska & Knott 2000).
We did not include it in the list of hotspots because the major-
ity of species are probably not strictly stygobitic.
Nevertheless, it is a striking example of high diversity in a very
small cave. Third, caves and wells that intersect the perma-
nently saturated (phreatic) zone also are well represented.
These include Movile Cave, Shelta Cave, San Marcos Spring,
all six caves in the Dinaric karst, and all six caves in France.
This is an especially intriguing result, and suggests that there
are a great many undiscovered species at such sites. Finally,
many of the caves are long caves. Seven of the caves listed in
Table 1 (Mammoth Cave, Buso della Rana, Krizna Jama,
Sistem Postojna-Planina, Vjetrenica Jama, Reseau Trombe,
and Gua Salukkan Kallang—Towakkalak) are over 5 km long,
yet less than 1% of caves are this long, at least based on U.S.
cave data (Culver, unpublished). A longer cave usually means
a higher number of different habitats.
More complete explanations of the patterns of subterranean
biodiversity must await a more detailed regional analysis, but
we hope that this report sparks an increased interest in hotspots
of subterranean biodiversity.
A
CKNOWLEDGMENTS
Several colleagues, including T. Iliffe, C. Juberthie, S.
Sarbu, J. Holsinger, T. Kane, S. Peck, and F. Stoch, helped with
the compilation of the lists. F. Stoch provided descriptions of
the Italian caves and C. Juberthie provided descriptions of the
French caves. C. Belson provided Figure 1.
Journal of Cave and Karst Studies, April 2000 • 17
CULVER AND SKET
REFERENCES
Barr, T.C. (1967). Ecological studies in the Mammoth Cave system
of Kentucky I. The biota. International Journal of Speleology 3:
147-203.
Belles, X. (1987). Fauna cavernicola i intersticial de la Peninsula
Iberica i les iles Balears. Consell Superior d’Investigacions
Cientifiques. Madrid.
Bole, J., Drovenik, B., Mrsic, N & Sket, B. (1993). Endemic animals
in hypogean habitats in Slovenia. Nase Jame 35:43-56.
Brancelj, A. (1992). Podzemna favna rakov (Arthropoda: Crustacea)
v dveh vodnih jamah na Kra kem robu (Fauna sotterranea dei
gameri (Arthropoda: Crustacea) in due grotti del Ciglione carsi-
co). Annales 2(1992): 31-38.
Cooper, J.E. (1975). Ecological and behavioral studies in Shelta
Cave, Alabama, with emphasis on decapod crustaceans. PhD
Diss., University of Kentucky, Lexington.
Culver, D.C. (1999). A history of management of biological
resources of Shelta Cave, Alabama, U.S.A. In Proceedings of the
Meeting on Caves of Natural Origin under Cities and Urban
Areas. Hungarian Speleological Society, Budapest: 130-131
Curl, R. (1964). On the definition of a cave. National Speleological
Society, Bulletin 26: 1-6.
Deharveng, L. & Bedos, A. (2000). The cave fauna of Southeast
Asia. Origin, evolution, and ecology, pp. 613-642. In Wilkens,
H, Culver, D. & Humphreys, W. [eds.]. Subterranean ecosystems.
Elsevier, London.
Hadzi, J. (1940). Favnula epizoicnih infuzorijev na jamski mokrici
(Microlistra spinosissima Rac.). Razprave matematicno-priro-
doslovegna Razreda Akademije Znanosti. In Umetnosti v
Ljubljani. 1: 121-148.
Hobbs, H.H. & Bagley, F.M. (1989). Shelta Cave management plan.
Report of the Biology Subcommittee of the Shelta Cave
Management Committee to the National Speleological Society,
Huntsville, AL.
Holsinger, J.R. & Culver, D.C. (1988). The invertebrate cave fauna
of Virginia and a part of eastern Tennessee: Zoogeography and
ecology. Brimleyana 14:1-162.
Holsinger, J.R. & Longley, G. (1980). The subterranean amphipod
crustacean fauna of an artesian well in Texas. Smithsonian
Contributions to Zoology, No. 308: 62 pp.
Howarth, F.G. & Stone, F.D. (1990). Elevated carbon dioxide levels
in Bayliss Cave, Australia: Implications for the evolution of
obligate cave species. Pacific Science 44: 207-218.
James, J.M. (1977). Carbon dioxide in the cave atmosphere.
Transactions of the British Cave Research Association 4: 417-
429.
Jasinska, E.J., Knott, B. & McComb, A.J. (1996). Root mats in
ground water: A fauna-rich cave habitat. Journal of the North
American Benthological Society 15: 508-519.
Jasinska, E.J. & Knott, B. (2000). Root-driven faunas in cave waters.
In Wilkens, H. Culver, D. & Humphreys, W. [eds.]. Subterranean
ecosystems. Elsevier, London: 291-314.
Juberthie, C. & Juberthie-Jupeau, L. (1975). La réserve biologique
du Laboratoire souterrain à Sauve (Gard). Annales de
Spéléologie 30: 539-551.
Longley, G. (1981). The Edwards Aquifer: Earth’s most diverse
groundwater ecosystem? International Journal of Speleology 11:
123-128.
Malard, F., Gibert, J. Laurent, R. & Reygrobellet, J-L. (1994). A new
method for sampling the fauna of deep karstic aquifers. Comptes
Rendus Academie de Sciences 317: 955-966.
Master, L.L., Flack, S.R. & Stein, B.A. (1998). Rivers of life.
Critical watersheds for protecting freshwater biodiversity. The
Nature Conservancy, Arlington, VA.
Packard, A.S. (1888). The cave fauna of North America, with
remarks on the anatomy of the brain and origin of the blind
species. Memoirs of the National Academy of Sciences 4: 1-156.
Peck, S.B. & Finston, T.L. (1993). Galapagos Islands troglobites:
the questions of tropical troglobites, parapatric distributions with
eyed-sister-species, and their origin by parapatric speciation.
Mémoires de Biospéologie 20: 19-37.
Poulson, T.L. (1992). The Mammoth Cave ecosystem. In Camacho,
A. [ed.]. The natural history of biospeleology. Museo Nacional
de Ciencias Nataurales. Madrid: 569-611.
Pretner, E. (1963). Kako zaštititi pecinsku faunu Vjetrenice kod
Zavale. Treci jugoslavenski speleoloski Kongres, Savajeva 1962:
169-174.
Pretner, E. (1968). Zivalstvo Postojnske jame. 150 let Postojnske
jame, Postojna: 59-78.
Rouch, R. & Danielopol, D.L. (1997). Species richness of
Microcrustacea in subterranean freshwater habitats. Comparative
analysis and approximate evaluation. Internationale Revue der
Gesamten Hydrobiologie 82°: 121-145.
Sarbu, S. (2000). Movile Cave: A chemoautotrophically based
groundwater ecosystem. In Wilkens, H., Culver, D., Humphreys,
W. [eds.]. Subterranean ecosystems. Elsevier, London: 325-350.
Sarbu, S.M., Kane, T.C. & Kinkle, B.K. (1996). A chemoautotroph-
ically based groundwater ecosoystem. Science 272: 1953-1955.
Sket, B. (1979). Jamska favna Notranjskega trikotnika (Cerknica -
Postojna - Planina), njena ogrozenost in naravovarstveni pomen
(The cave fauna in the triangle Cerknica - Postojna - Planina
/Slovenia, Yugoslavia, its conservational importance). Varstvo
narave, Ljubljana 12: 45-59
Sket, B. (1996). Biotic diversity in hypogean habitats in Slovenia and
its cultural importance, pp. 59-74. In A. Cimerman and N.
Gunde-Cimerman [eds.], International Biodiversity Seminar Ecco
XIV. Meeting, Ljubljana.
Sket, B. (1999a). The nature of biodiversity in hypogean waters and
how it is endangered. Biodiversity Conservation 8(10): 1319-
1338.
Sket, B. (1999b). High biodiversity in hypogean waters and its
endangerment – the situation in Slovenia, Dinaric Karst, and
Europe. Crustaceana 72: 767-780.
Sket, B. & Iliffe, T. (1980). Cave fauna of Bermuda. Internationale
Revue der Gesamten Hydrobiologie 65: 871-882.
Sket, B. & Velkovrh, F. (1981). Postojnsko-planinski jamski sistem
kot model za proucevanje onesnazenja podzemeljskih voda (The
Postojna-Planina Cave System as a model for the investigations of
the polluted subterranean rivers). Naše jame 22: 27-44
Wilson, E.O. (1992). The diversity of life. Harvard Univ. Press,
Cambridge, MA.
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... This is the first study describing sponge communities in submarine caves and tunnels in Brazil. The study of submarine cavities in Brazil is still incipient, and many additional steps are needed for a better knowledge of marine caves and tunnels along the Brazilian coast and oceanic islands: (1) to provide quantitative data and detailed mappings using photoquadrats, photogrammetry, transects, echo-sounders, light sensors, and compasses [80,81]; (2) to investigate the dark zones of Sapata Cave and Ilha do Meio Cave, which remain largely unexplored; (3) to carry out more collections of sponges in the three cavities studied here, because many species appeared only in photographs and were not collected yet; (4) to publish taxonomic descriptions of the species that remain undescribed; (5) to investigate the planktonic and sponge-associated microbiota in caves and tunnels on Fernando de Noronha; and (6) to explore other caves and tunnels on Fernando de Noronha and in other localities in Brazil such as Abrolhos, the Rocas Atoll, Trindade Island, Rio de Janeiro, and Arraial do Cabo. support during the expeditions to Fernando de Noronha. ...
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... The Cent Fonts aquifer is located in the southern region of France, in the Mediterranean basin, and is part of a larger karstic system comprising the Hérault (2600 km 2 ), Vidourle (800 km 2 ), and Lez (200 km 2 ) river basins. These regions are already acknowledged for their abundant and remarkable subterranean biodiversity [1,2]. ...
... The Lez system was considered to be the richest biodiversity hotspot for stygobiotic species in France [2]. We update here the checklist of stygobiotic species of the Lez basin given by Jourde et al. [15]: Paladilhia umbilicata (Locard, 1902) and Bythiospeum articense R. Bernasconi, 1985 are misidentifications, these species live far from the Lez system [16]; Paladilhia subconica Girardi, 2009 and Moitessieria magnanae Girardi, 2009 are considered endemic to their type locality in the Hérault basin; Phagocata vitta (Dugès, 1830) and Proasellus coxalis (Dollfus, 1892) are not stygobiotic species. ...
... Combining all this data, a total of 43 stygobiotic species have been identified, making the Cent Fonts system a hotspot of subterranean biodiversity in Europe (Table 1). Its stygobiont richness is higher than that of the better known Lez system (39 stygobionts), considered one of the most important biodiversity hotspots in the world [1,2]. The third-richest area of the southern Massif Central in France is the Sauve karstic system (29 stygobionts [44]), close to the Cent Fonts ( Figure 1B). ...
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The South of France is a biodiversity hotspot within Europe. Here, we present a comprehensive review of surveys conducted in the Cent Fonts aquifer, an overlooked subterranean biodiversity hotspot embedded in a region rich in stygobiotic species and threatened by climate change and water abstraction projects. Key studies, spanning from 1950 to 2006, show a progression in survey methods and results, although troglobiotic species remain poorly documented. With 43 stygobiotic species recorded, the Cent Fonts is the richest stygobiont hotspot in France. Most species are regional endemics, a quarter of which are considered vulnerable by the IUCN. The Cent Fonts also hosts several relict species and is the type locality of four species. Such a high biological value clearly deserves to be preserved. Our analysis warns of a possible decline in biodiversity, as eight of the species recorded in the 20th century were absent from the 2006 survey, suggesting potential threats of unknown origin. The capture of the Cent Font springs for water abstraction is discussed as a potential threat to this ecosystem and its unique biodiversity. Three new species of stygobiotic molluscs are described, one of which was collected in the Cent Fonts.
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Full-text available
The South of France is a biodiversity hotspot within Europe. Here, we present a comprehensive review of surveys conducted in the Cent Fonts aquifer, an overlooked subterranean biodiversity hotspot embedded in a region rich in stygobiotic species and threatened by climate change and water abstraction projects. Key studies, spanning from 1950 to 2006, show a progression in survey methods and results, although troglobiotic species remain poorly documented. With 43 stygobiotic species recorded, the Cent Fonts is the second richest stygobiont hotspot in Europe. Most species are regional endemics, a quarter of which are considered vulnerable by the IUCN. The Cent Fonts also hosts several relict species and is the type locality of four species. Such a high biological value clearly deserves to be preserved. Our analysis warns of a possible decline in biodiversity, as 8 of the species recorded in the 20th century were absent from the 2006 survey, suggesting potential threats of unknown origin. The capture of the Cent Font springs for water abstraction is discussed as a potential threat to this ecosystem and its unique biodiversity. Three new species of stygobiotic molluscs are described, one of which was collected in the Cent Fonts.
... There are a number of reasons for this, including difficulties in accessing habitats, incomplete taxonomy, and the dominance of β diversity over α diversity [4,5]. Culver and Sket attempted to circumvent and ignore these problems by concentrating on individual caves and aquifers, as opposed to just regions [6]. Their initial list of 20 caves and aquifers, with 20 or more species limited to subterranean habitats (stygobionts and troglobionts), stimulated interest among researchers in identifying species present in various caves and wells. ...
... Most of these sites are discussed in individual papers in two Special Issues of Diversity, the only exceptions being the Areias Cave System of Brazil [10] and Túnel de la Atlantida of Canary Islands [11]. There are only two sites that are claimed to contain 25 or more species and were not included-Logarček in Slovenia [6] and Sauve Spring in France [12]. The potential occurrence of high-diversity cave faunas in other tropical and temperate regions is briefly discussed further down. ...
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... In 2000, David Culver and Boris Sket published one of the most influential papers in subterranean biology, addressing a straightforward question: how many "species-rich" caves, each counting 20 or more troglobionts are there, and where in the world they are (Culver and Sket 2000). By introducing the arbitrarily defined measure of "richness" or "hotspot," this paper enabled the scaling of any faunistic list and established a comparative framework for studying species richness in individual caves. ...
... Furthermore, caves are challenging and extreme environments, mainly because they are highly oligotrophic, lack primary production and depend on limited nutrient input brought in with percolating water (Kováč 2018). Finally, the Dinaric karst underground is considered a hotspot of invertebrate biodiversity with one of the most complex and diverse subterranean faunas in the world, including many endemic and relict species (Culver and Sket 2000;Sket 2005;Ozimec et al. 2009). While most biospeleological studies of this hotspot focus on invertebrates (Bilandžija et al. 2013;Deharveng and Bedos 2018;Bedek et al. 2019;Kozel et al. 2020), studies on the microbial communities of the Dinaric karst are scarce and mainly describe limestone-associated biofilms (Mulec 2008;Pašić et al. 2010;Velikonja et al. 2014;Mulec et al. 2015). ...
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... The sampling has been most intensive in Slovenia and Dinarides, a karstic massif in the SE Europe (Fig. 3), for two reasons. First, Dinaric subterranean habitats have traditionally been at focus of many Slovenian and foreign researchers due to extremely high diversity of subterranean species 43,44 . Second, Niphargus diversity peaks in the Dinarides 45,46 , and sampling campaigns were often dedicated to collection of Niphargus for different taxonomic, ecological, and evolutionary studies. ...
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... The concept of HSB was originally introduced by Culver and Sket [3] to designate subterranean environments that host a minimum of 20 or more troglobitic/stygobitic species. More recently, there has been a movement to raise this threshold to a minimum of 25 cave-restricted species. ...
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The Água Clara Cave System was previously recognized as a prominent hotspot of subterranean biodiversity in South America, harboring 31 cave-restricted species. However, a recent expedition conducted in September 2023, coinciding with an exceptionally dry period in the region, provided access to previously unexplored areas. Therefore, the objective of this research was to investigate the cave-restricted invertebrate species, extending the findings from a previous article on the Agua Clara Cave System published in June 2023, and emphasizing the significance of this system as one of the most crucial tropical biodiversity hotspots. This survey unveiled an additional 10 species, raising the count of cave-restricted species within the system to an impressive 41. This remarkable diversity not only solidifies the Água Clara Cave System’s position as a paramount hotspot of subterranean biodiversity in the tropics but also serves as a stark warning about the imminent risks faced by these species. The escalating human-induced alterations in the region, notably deforestation, pose a significant risk to the survival of many of these unique and endemic species.
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Similarly to other animal communities, the diversity of subterranean aquatic fauna is influenced by several factors and processes, such as habitat fragmentation, dispersion, environmental heterogeneity, and physical and chemical water characteristics. Here, we studied cave aquatic communities of the Alto Ribeira hydrographic basin, regarding troglobitic and non-troglobitic species, located in a single karst area to evaluate the influence of sub-basins in fauna differentiation. We investigated how abiotic variables (flow, electrical conductivity, temperature, pH, and substrate) influence the fauna composition and the contribution of beta diversity components (nestedness and turnover) in explaining communities' dissimilarities. Fauna composition differed between sub-basins, as most species did not co-occur in different caves. Caves with higher flow and substrate diversity were the richest. In addition, each cave community was influenced by a unique set of abiotic variables. Dissimilarity among caves was mainly explained by turnover, and our findings suggest the restricted species distribution could be due to ecological (e.g., limited dispersion capacity, tolerance to abiotic variables), hydrogeological (e.g., dispersion barriers, isolation of sub-basins), and historical (e.g., colonization, paleoclimatic events) factors and processes. Therefore, different elements are responsible for determining the composition of cave aquatic communities in different sub-basins, reflecting the variability within a single karst area.
Chapter
The territory of Montenegro represents one of the impressive hotspots of cave-dwelling fauna diversity in the world. As many as 1600 speleological objects are registered in Montenegro, but only 5–10% of them have been explored in terms of biodiversity. An overview of literature data on cave biodiversity in Montenegro is given here. A total of 72 species of micromycetes were registered in 7 caves and the most abundant species were Acrodontium salmoneum, Aureobasidium pullulans, Cladosporium oxysporum, Mucor racemosus f. racemosus, Penicillium chrysogenum, and Rhizopus stolonifer. Regarding dwelling invertebrates, the following groups are represented in Montenegrin caves: Protozoa—ciliates; Turbelaria—tricladids and temnocephalids; Gastropoda; Oligochaeta and Hirudinea; Cladocera, Copepoda, and Ostracoda; Isopoda; Amphipoda; Aranea; Pseudoscorpiones; Palpigradi; Opiliones; Chilopoda; Diplopoda; Collembola; Coleoptera—over 80 species. According to the non-invasive survey method based on environmental DNA (eDNA), indications of the presence of the olm (Proteus anguinus Laurenti 1768) were reconfirmed by finding traces of environmental DNA at several sites in Montenegro.
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The Mammoth Cave system includes more than 175 kilometers of explored passages in Mammoth Cave National Park, Kentucky. Although biologists have explored the caves intermittently since 1822, the inventory of living organisms in the system is still incomplete. The present study lists approximately 200 species of animals, 67 species of algae, 27 species of fungi, and 7 species of twilight-zone bryophytes. The fauna is composed of 22% troglobites, 36% troglophiles, 22% trogloxenes, and 20% accidentals, and includes protozoans, sponges, triclads, nematodes, nematomorphs, rotifers, oligochaetes, gastropods, cladocerans, copepods, ostracods, isopods, amphipods, decapods, pseudoscorpions, opilionids, spiders, mites and ticks, tardigrades, millipedes, centipedes, collembolans, diplurans, thysanurans, cave crickets, hemipterans, psocids, moths, flies, fleas, beetles, fishes, amphibians, birds, and mammals. The Mammoth Cave community has evolved throughout the Pleistocene concomitantly with development of the cave system. The troglobitic fauna is derived from 4 sources: (1) troglobite speciation in situ in the system itself; (2) dispersal along a north Pennyroyal plateau corridor; (3) dispersal along a south Pennyroyal plateau corridor; and (4) dispersal across the southwest slope of the Cumberland saddle merokarst.