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© Biospeologica Bibliographia - Publications 2010-2

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<strong>©</strong> <strong>Biospeologica</strong> <strong>Bibliographia</strong><br />

<strong>Publications</strong> <strong>2010</strong>-1<br />

Page 14 sur 116<br />

première fois, une espèce stygobie (vivant dans les grottes) de copépodes<br />

a été découverte en Thaïlande. Elle appartient à l'ordre des Harpacticoida<br />

et a été reconnue comme une espèce nouvelle: Elaphoidella namnaoensis<br />

n. sp. Les spécimens ont été recueillis seulement dans les bassins remplis<br />

d'eau de percolation. Ceci indique une écologie particulière pour cette<br />

nouvelle espèce, liée à la zone insaturée de l'aquifère karstique, où<br />

l'hydrologie est déterminée exclusivement par les précipitations. Une<br />

description détaillée de la nouvelle espèce est présentée ici, complétée par<br />

des informations sur son écologie et ses adaptations morphologiques. Ces<br />

adaptations sont comparées à celles rencontrées chez d'autres<br />

Elaphoidella de la zone insaturée des aquifères karstiques d'Europe.<br />

BRANNEN (K. M.), BIRDWELL (J. E.) & ENGEL (A.<br />

S.), <strong>2010</strong>. Creating humic matter indices for the<br />

interpretation of ecosystem energetics:98. In: 20 th<br />

International Conference on Subterranean Biology,<br />

Postojna, Slovenia, 29 August-3 September <strong>2010</strong>, ICSB<br />

<strong>2010</strong> Abstract Book, edited by: Ajda MOŠKRIČ and Peter<br />

TRONTELJ, ISBN 978-961-269-286-5. ABS: Cave and karst<br />

ecosystem energetics are an important factor in understanding the<br />

microbial processes in aquifers. Determining the flux of dissolved organic<br />

matter (DOM), a source of organic carbon for heterotrophic<br />

microorganisms within an aquifer, from the surface into the subsurface is<br />

one method of tracking ecosystem energetics. The relative contributions<br />

of different sources of DOM can be evaluated using excitation-emission<br />

matrix (EEM) fluorescence spectroscopy since no photodegradation of<br />

OM occurs in cave and karst waters. This method can characterize DOM<br />

at natural, low abundance levels, and can differentiate recalcitrant DOM<br />

(e. g., humic substances) from more biologically labile material (e. g.,<br />

proteins, peptides, and amino acids). Consequently, in karst<br />

environments, the influence of surface derived (allochthonous) DOM can<br />

be distinguished from autochthonous DOM produced by microbial<br />

chemolithoautotrophy. Karst environments are heavily influenced by<br />

surface water recharge and allochthonous DOM. Autochthonous OM in<br />

karst is poorly understood because it is unclear how microbes contribute<br />

to DOM types and abundances, as either primary DOM sources or during<br />

degradation processes of allochthonous material. It is important to<br />

differentiate allochthonous from autochthonous humic matter for the<br />

interpretation of cave and karst ecosystem energetics. Autochthonous<br />

humic matter is often overshadowed by allochthonous matter; meaning<br />

allochthonous humic matter fluoresces brighter than autochthonous<br />

matter. In this study, our aim was to create an index of humic/fulvic acids<br />

and protein (tryptone) mixtures to help differentiate the overshadowing<br />

effects of the brighter humic substances by using difference mg/L<br />

concentrations of tryptone, Suwannee River Fulvic Acid (SRFA), and<br />

Pony Lake Fulvic Acid (PLFA), and different mixtures of these<br />

standards. Although the SRFA and PLFA standards mixed in different<br />

ratios with the protein tryptone will be less complex than natural cave<br />

waters, we will be able to see if there is any substantial fluorescence<br />

overshadowing of tryptone by SRFA and PLFA. This index, coupled with<br />

a detailed analysis of microbial communities in specific subsurface<br />

environments could allow for a greater understanding of microbial<br />

processes and metabolisms within the subsurface.<br />

http://www.icsb<strong>2010</strong>.net/<br />

BRINKLØV (S.), KALKO (E. K. V.) & SURLYKKE (A.),<br />

<strong>2010</strong>. Adaptation of echolocation call intensity to<br />

ecological constraints in phyllostomid bats:106-107. In:<br />

15 th International Bat Research Conference, Prague, 22-<br />

27 August <strong>2010</strong>, the conference manual: Programme,<br />

abstracts, list of participants, edited by: Ivan HORÁČEK<br />

and Petr BENDA, ISBN 978-80-87154-46-5, 380 p. ABS:<br />

In two previous papers we have shown, first, that two phyllostomids, the<br />

trawling bat, Macrophyllum macrophyllum and the fruit-eating bat,<br />

Artibeus jamaicensis can emit echolocation calls of considerable intensity<br />

and, second, that M. macrophyllum dynamically adapts call intensity to<br />

habitat complexity. Here, we investigate on a broader scale the ecological<br />

correlates of echolocation call intensity in phyllostomids. We recorded<br />

bats with multi-microphone arrays at several sites in Panamá and Cuba.<br />

For example, at cave openings as the bats left their day roost, at fruiting<br />

fig trees along a shoreline and at ca. 40 m height from a canopy crane<br />

immersed into a fruiting fig tree. Assuming that habitat does indeed act as<br />

a unifying constraint on call intensity, we expected to record relatively<br />

similar source levels at each individual site. The sites were chosen to<br />

represent different perceptual tasks (leaving the roost; approaching a<br />

foraging site) and thus different sonar challenges. We discuss flexibility<br />

Bernard LEBRETON & Jean-Pierre BESSON<br />

Créé le : 01.01.<strong>2010</strong><br />

Modifié le : 30.06.<strong>2010</strong><br />

in sonar call intensity of phyllostomid bats, which often forage in highly<br />

cluttered space, but also use echolocation range to orient in situations<br />

where intense calls might be advantageous, for example when commuting<br />

in open space to a feeding site.<br />

British Cave Research Association, <strong>2010</strong>. Abstracts from the<br />

BCRA Summer Cave Biology Field Meeting, 8 September<br />

<strong>2010</strong>, Arncliffe Village Hall and Scoska Cave, Littondale,<br />

Yorkshire, UK. Cave and Karst Science 37(2, this issue<br />

has a cover date of August <strong>2010</strong> and was published in<br />

December <strong>2010</strong>):67.<br />

http://bcra.org.uk/pub/candks/index.html?j=110<br />

BRITZKE (E. R.), SEWELL (P.), HOHMANN (M. G.),<br />

SMITH (R.) & DARLING (S. R.), <strong>2010</strong>. Use of<br />

Temperature-Sensitive Transmitters to Monitor the<br />

Temperature Profiles of Hibernating Bats Affected with<br />

White-Nose Syndrome. Northeastern Naturalist 17(2,<br />

June):239-246. DOI:<br />

http://dx.doi.org/10.1656/045.017.0207. ABS: In temperate<br />

ecosystems, hibernation allows bats to survive long periods of limited<br />

prey and water availability during colder months. Despite the extended<br />

amount of time some bats spend in hibernation, researchers have only<br />

recently been able to study the hibernation ecology of bats under natural<br />

conditions. With the emergence of white-nose syndrome (WNS), a<br />

mysterious disease presently killing large numbers of bats during the<br />

hibernation period in the northeastern United States, expanding our<br />

knowledge of hibernation ecology and natural history has become more<br />

crucial. To collect such data, we used temperature-sensitive radio<br />

transmitters and data loggers to monitor the skin temperatures (Tsk) of 6<br />

bats (5 Myotis lucifugus [Little Brown Bat], and 1 Myotis septentrionalis<br />

[Northern Long-eared Bat]) hibernating in Mount Aeolus Cave, VT in<br />

late winter 2008. We recorded Tsk every 14 minutes for the life of the<br />

transmitters. We were able to monitor Tsk from near ambient temperatures<br />

to above 30°C Arousals occurred immediately before the signals were<br />

lost and at a time of increased numbers of bats observed on the landscape,<br />

thereby suggesting the emergence (and subsequent death) of bats. Our<br />

observations provide first data on the hibernating ecology of WNSaffected<br />

bats under natural conditions.<br />

BROWN (B. V.) & KUNG (G.-A.), <strong>2010</strong>. Revision of the<br />

New World Dohrniphora Dahl species lacking large hind<br />

tibial setae (Diptera: Phoridae). Zootaxa 2699(December<br />

3):1-142, 43 pl., 41 réf.<br />

http://www.mapress.com/zootaxa/list/<strong>2010</strong>/2699.html<br />

BROWN (P. E.), <strong>2010</strong>. Bats and mine closure: a doubleedged<br />

sword:107. In: 15 th International Bat Research<br />

Conference, Prague, 22-27 August <strong>2010</strong>, the conference<br />

manual: Programme, abstracts, list of participants, edited<br />

by: Ivan HORÁČEK and Petr BENDA, ISBN 978-80-<br />

87154-46-5, 380 p. ABS: Much of the Western United States was<br />

settled as a result of mining. When the mines were abandoned, bats<br />

colonized these new "caves". Cities grew up around some mining<br />

districts. Even in remote areas, mines are visited by people exploring on<br />

off- highway vehicles. Abandoned mines can be hazardous, and accidents<br />

result. The recent influx of funds in the United States for mine closure has<br />

stimulated a rush to remediate mine hazards on federal lands. To attain<br />

the goal of the Economic Stimulus Package of putting more people to<br />

work, some people are involved who do not have experience in bat<br />

biology or bat-compatible closures. If done properly, bats in mines could<br />

be protected through the installation of bat gates and cupolas. However if<br />

bat habitat is not identified, mines could be closed through foam and<br />

backfill that would deprive bats of roosting habitat and potentially kill<br />

them, especially if exclusions are not done properly at the appropriate<br />

time of year. Most bat species use a variety of roosts throughout the<br />

annual cycle as dictated by physiological and behavioral needs. The<br />

timing of surveys will influence the ability to detect bat use of a mine<br />

feature, which can affect the treatment that a mine may receive (hard or<br />

bat-compatible closure). There is no substitute for site-specific bat<br />

surveys using established protocols to detect bat use, nor is there a<br />

universal style of mine closure. Some bat colonies do not accept culverts<br />

or even gates. To understand the importance of a single mine feature,<br />

most of the mines in a geographic unit may need to be evaluated in order<br />

to determine those with the most significant bat use at different times of<br />

the year. The scope of the "landscape" will depend on the species of bat

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