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Nocturnal foraging and activity by diurnal lizards: Six species of day geckos (Phelsuma spp.) using the night-light niche

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Altered environments in urban areas are known to impact and change animal behaviour. In particular, artificial light at night (ALAN) affects behaviour across taxonomic groups, including reptiles. Geckos in the genus Phelsuma are predominantly diurnal, but some have been documented to alter their foraging behaviour from a diurnal to nocturnal activity period when they have access to artificial light sources. Herein, we report new observations of six Phelsuma spp. (Andaman day geckos, P. andamanensis; blue-tailed day geckos, P. cepedi-ana; Madagascar giant day geckos, P. grandis; Reunion ornate day geckos, P. inexpectata; gold dust day geckos, P. laticauda; Mahe day geckos, P. sundbergi longinsulae) using artificial lights to engage in nocturnal activity that includes foraging, courtship, and agonistic behaviour. Artificial light at night augments the amount of time predators, especially visual predators, can spend foraging. This can increase their overall daily activity period (i.e. the amount of time spent active within 24 h), and research is yet to fully understand the cost-benefit trade-offs this altered behaviour has on individual fitness. Overall, our novel accounts of six Phelsuma spp. contribute to knowledge regarding the diversity of animals that have altered their behaviour in response to ALAN and highlight the behavioural flexibility of this group of geckos.
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Nocturnal foraging and activity by diurnal lizards: Six
species of day geckos (Phelsuma spp.) using the night-light
niche
JAMES BAXTER-GILBERT,
1
*CL
AUDIA BAIDER,
2
F.B. VINCENT FLORENS,
3
OLIVER HAWLITSCHEK,
4
ASHWINI V. MOHAN,
5
NITYA P. MOHANTY,
1
CARLA WAGENER,
1
KATHLEEN C. WEBSTER
6
AND JULIA L. RILEY
7,8
1
Centre for Invasion Biology, Department of Botany and Zoology, Stellenbosch University, Matieland,
South Africa (Email: jx_baxtergilbert@laurentian.ca);
2
The Mauritius Herbarium, Agricultural
Services, Ministry of Agro-Industry and Food Security, R
eduit (Email: cbaider@govmu.org);
3
Tropical
Island Biodiversity, Ecology and Conservation Pole of Research, Faculty of Science, University of
Mauritius, R
eduit, Mauritius (Email: vin.orens@uom.ac.mu);
4
Centrum f
ur Naturkunde, Universit
at
Hamburg, Hamburg;
5
Department of Evolutionary Biology, Zoological Institute, Braunschweig
University of Technology, Braunschweig;
6
Zoologische Staatssammlung M
unchen (ZSM-SNSB),
Munich, Germany;
7
Department of Botany and Zoology, Stellenbosch University, Matieland, South
Africa; and
8
Department of Biology, Dalhousie University, Halifax, Nova Scotia, Canada
Abstract Altered environments in urban areas are known to impact and change animal behaviour. In particu-
lar, articial light at night (ALAN) affects behaviour across taxonomic groups, including reptiles. Geckos in the
genus Phelsuma are predominantly diurnal, but some have been documented to alter their foraging behaviour
from a diurnal to nocturnal activity period when they have access to articial light sources. Herein, we report
new observations of six Phelsuma spp. (Andaman day geckos, P.andamanensis; blue-tailed day geckos, P.cepedi-
ana; Madagascar giant day geckos, P.grandis;R
eunion ornate day geckos, P. inexpectata; gold dust day geckos,
P.laticauda; Mah
e day geckos, P.sundbergi longinsulae) using articial lights to engage in nocturnal activity that
includes foraging, courtship, and agonistic behaviour. Articial light at night augments the amount of time
predators, especially visual predators, can spend foraging. This can increase their overall daily activity period
(i.e. the amount of time spent active within 24 h), and research is yet to fully understand the costbenet trade-
offs this altered behaviour has on individual tness. Overall, our novel accounts of six Phelsuma spp. contribute
to knowledge regarding the diversity of animals that have altered their behaviour in response to ALAN and high-
light the behavioural exibility of this group of geckos.
Key words: articial light at night, behavioural shift, biological invasions, exibility, foraging, reptile, urban.
NATURAL HISTORY NOTE
Anthropogenic landscapes are known to dramatically
alter animal behaviour, including changes in beha-
vioural traits (e.g. boldness and exploration), habitat
use, and foraging, which relates to both the chal-
lenges and opportunities present in human-altered
environments (Lowry et al. 2013). Notably, articial
light at night (ALAN) affects reptiles in several ways,
including changes in antipredator behaviours, dis-
rupted navigation, and altering ecological and indi-
vidual interactions by centralising invertebrate prey
(Perry et al. 2008). One of the impacts easiest to
recognise is when diurnally active species increase
nocturnal activity to exploit feeding opportunities
around lights (i.e. within the night-light niche; Gar-
ber 1978; Perry et al. 2008). Previous research has
reported more than 40 diurnal reptile species using
this night-light niche for foraging (Deso 2007; Perry
et al. 2008; Maurer et al. 2019; Dubos et al. 2020)
with the list growing annually. These accounts
include three species of day gecko: R
eunion ornate
day geckos (Phelsuma inexpectata, introduced popula-
tion), gold dust day geckos (P.laticauda, invasive
Hawaiian population), and Kochs giant day geckos
(P.kochi; native population; Garc
ıa & Vences 2002;
Perry & Fisher 2006; Dubos et al. 2020). Here we
report new observations of six day geckos using the
night-light niche to engage in nocturnal activity: (i)
Andaman day gecko (P.andamanensis, native popula-
tion), (ii) blue-tailed day geckos (P.cepediana, native
*Corresponding author. Centre for Invasion Biology, Depart-
ment of Botany and Zoology, Natural Sciences Building, Pri-
vate Bag X1, University of Stellenbosch, Matieland, Western
Cape 7602, South Africa.
Accepted for publication January 2021.
© 2021 Ecological Society of Australia doi:10.1111/aec.13012
Austral Ecology (2021) ,
population), (iii) Madagascar giant day geckos
(P.grandis, invasive population), (iv) R
eunion ornate
day geckos (P. inexpectata, native population), (v)
gold dust day geckos (P. laticauda, invasive popula-
tion), and (vi) Mah
e day gecko (P.sundbergi longinsu-
lae, native population). These observations were
made by different authors over many years of work-
ing in the Mascarenes, Comoros, Andamans and
Seychelles archipelagos.
Andaman day gecko, Phelsuma andamanensis
Blyth, 1861
Andaman day geckos are medium-sized diurnal gekko-
nids (maximum snoutvent length (SVL) 57 mm,
AVM unpublished) endemic to the Andaman archipe-
lago. On 19 November 2016 (sunset at 16:48 h),
between 19:00 and 22:00 h, we captured a juvenile
that was foraging alongside invasive Asian house
geckos (Hemidactylus frenatus) and common four-
clawed geckos (Gehyra mutilata) inside a building on
walls close to a white light source (bulb type unknown;
incandescent or LED). This observation was made in
Chainpur Village, Middle Andaman Island
(12.7418°N, 92.8048°E). Another observation of
Andaman day geckos nocturnally foraging was made
on 14 March 2017 (sunset at 17:28 h), between
19:0022:00 h, in Mount Harriet National Park
(11.7204°N, 92.7337°E). Like the previous observa-
tion, this was observed inside a cabin with a white light
source (bulb type unknown; incandescent or LED).
Blue-tailed day gecko, Phelsuma cepediana
Milbert, 1812
Blue-tailed day geckos are medium-sized diurnal gek-
konids (maximum SVL 58 mm; Rocha et al. 2010)
that are endemic to the Mascarene archipelago. At
20:15 h on 11 July 2019 (sunset at 17:45 h), we
observed a blue-tailed day gecko foraging around a
white, uorescent light source (i.e. a tube light;
Fig. 1) in the village of Notre Dame on Mauritius
(20.1397°S, 57.5618°E). At this time, most insects
found around the lights were moths, ying ants, and
beetles, and on several occasions, these geckos cap-
tured prey. Over the previous fortnight, we had made
several undocumented observations of these geckos
feeding around the same outdoor lights nightly, sug-
gesting this was not a once-off event. We were able
to distinguish between individuals due to tail damage
and determine that at least two individuals were feed-
ing around this light source. During these observa-
tions, we also noted several invasive Asian house
geckos foraging around the same lights; however, no
physical heterospecic interactions were observed
(e.g. biting, ghting, chasing, or following). Addi-
tionally, during the early 2000s, we also observed
hatchling, juvenile, and adult blue-tailed day geckos
active on the walls in the early evenings (~20:00
21:30 h) inside a residence in Vacoas, Mauritius,
illuminated with a white, incandescent light source.
Additionally, we saw an adult foraging on ants and
moths at 22:45 h above a white, incandescent light
source on an outside wall at the same location on 14
November 2020 (sunset at 18:26 h).
Madagascar giant day gecko, Phelsuma grandis
Gray, 1870
Madagascar giant day geckos are large diurnal gekko-
nids (maximum SVL 102.4 mm; Rocha et al. 2010)
native to Madagascar and invasive on the Mascarene
archipelago where these observations were made.
During March and August of 2016, we observed
many individuals feeding in urban areas near articial
lights in Mauritius. One specic example of this
occurred on the evening of 3 March 2016 (sunset at
18:34 h), when various individuals were foraging
around white, uorescent light sources for insects on
the hotel walls and in the restaurant area of Les Lata-
niers Bleus, Tamarin (20.3483°S, 57.3634°E)
between 19:00 and 21:00 h. In 2018, we also saw
this species foraging for insects shortly after dark
(~20:00 h) near a white, incandescent light source in
Vacoas, Mauritius.
R
eunion ornate day gecko, Phelsuma
inexpectata Gray, 1825
R
eunion ornate day geckos are medium-sized diurnal
gekkonids (maximum SVL 58 mm; Rocha et al.
Fig. 1. A blue-tailed day gecko (Phelsuma cepediana) verti-
cally perched below a 91 cm white, uorescent light source,
nocturnally foraging for insects in Notre Dame, Mauritius.
Photo credited to JLR.
doi:10.1111/aec.13012 © 2021 Ecological Society of Australia
2 J. BAXTER-GILBERT ET AL.
2010) endemic to R
eunion. Between 10 and 16 July
2015 (sunset at 17:52 h) in Manapany-Les-Bains,
R
eunion (21.3737°S, 55.5887°E), we observed one
to two individuals active around a white, uorescent
light source at night (18:3020:00 h; Fig. 2). The
animals actively positioned themselves under the
light, suggesting their preference for the night-light
niche. Since this light was inside a bathroom, there
were very few insects, and no predation events were
observed. Yet, they would remain beside the light
while it was illuminated and exhibited behaviours
normally associated with daytime activity (e.g. court-
ship; Fig. 2c). Previous records note this species
feeding on moths near the articial lights in the city
of Le Tampon, R
eunion, where a small, introduced
population occurs (Deso 2007). However, we here
report the rst nocturnal behaviour within the spe-
ciesnative distribution (Sanchez & Probst 2011).
Gold dust day gecko, Phelsuma laticauda
Boettger, 1880
Gold dust day geckos are medium-sized diurnal gek-
konids (maximum SVL 58 mm; Rocha et al. 2010),
which are native to northern Madagascar but occur
extensively as introduced species in tropical regions
throughout the Indian and Pacic Oceans. At
23:46 h on 19 March 2019 (sunset at 18:11 h), an
individual was observed foraging and successfully
capturing an ant (Fig. 3) near an amber, incandes-
cent light source on the wall of a resort near Mt.
Combani on Mayotte (12.8071°S, 45.1534°E) adja-
cent to degraded forest habitat. On the same night,
we also observed a gold dust day gecko interacting
with a athead leaf-toed gecko (Hemidactylus platy-
cephalus)a nocturnal gekkonid also introduced to
Mayotte around the amber, incandescent light. The
two species lunged aggressively at one another when
in close contact during foraging. Despite the consid-
erably larger size of the athead leaf-toed gecko, it
did not attempt to eat the day gecko. Interspecic
interactions like these were also documented in
Hawaii, where gold dust day geckos, Asian house
geckos, and green anoles (Anolis carolinensis) were
foraging at the same night-light source (Perry &
Fisher 2006). Nocturnal foraging behaviour was pre-
viously recorded for this species, but mostly from
highly urbanised locations (e.g. in the capital city of
Mamoudzou; Dubos et al. 2020). This account
demonstrates this behaviour occurs in more natural
areas as well.
Mah
e day gecko, Phelsuma sundbergi
longinsulae Rendahl, 1939
Mah
e day geckos are medium-sized diurnal gekko-
nids (maximum SVL 65 mm; Rocha et al. 2010)
endemic to Seychelles. On 14 March 2017 (sunset at
18:31 h), between 19:00 and 22:00 h, we docu-
mented nocturnal activity of Mah
e day geckos at a
white, uorescent light source near Anse Takamaka
(4.7790°S, 55.5000°E) on Mah
e Island (Fig. 4).
Fig. 2. R
eunion ornate day geckos (Phelsuma inexpectata) engaging in nocturnal activity under a white, uorescent light
source inside a bathroom in Manapany-Les-Bains, R
eunion (a,b). This observation included courtship behaviour between
conspecics (c). Photos credited to CB and FBVF.
© 2021 Ecological Society of Australia doi:10.1111/aec.13012
NIGHT-ACTIVE DAY GECKOS 3
These geckos were foraging for insects that were
attracted to this articial light. Other nocturnal
geckos, tentatively identied as invasive Asian house
geckos, were also present at the same light source;
however, no physical interactions between any of
these geckos were observed.
DISCUSSION
Geckos of the genus Phelsuma are predominantly diur-
nal, except for the now-extinct Rodrigues giant day
gecko (P.gigas; Cheke & Hume 2008) and the extant
G
unthers day gecko (P.guentheri, Gerner 2008). Phel-
suma spp. are typically visual foragers, using colour
cues to detect and assess resources (Hansen et al.
2006). The night-light niche and ALAN environments
augment the amount of time visual predators can
spend foraging, thereby increasing the duration of their
overall activity time. However, such alterations to the
sleep-wake cycle may negatively affect individual t-
ness (Aulsebrook et al. 2018).
Phelsuma spp. feed heavily on fruit, oral nectar,
pollen, and insects (Staub 1988; Nyhagen et al.
2001) and are important pollinators and seed dis-
persers in island ecosystems (Nyhagen et al. 2001;
Olesen & Valido 2003; Hansen et al. 2007; Hansen
&M
uller 2009; but see Bissessur et al. 2019).
Anthropogenic factors have previously been seen to
alter day gecko diets (Gardner & Jasper 2015), and
the reported nocturnal foraging on light-attracted
insects we present here could augment and/or alter
their nutritional intake, at least in urban areas. For
example, urban-dwelling Malagasy day geckos
(P. modesta leiogaster) feed heavily on anthropogenic
sugar-rich foods, with foraging on insects being gen-
erally rare despite an abundant availability (Gardner
& Jasper 2015). This behavioural and dietary plastic-
ity may predispose Phelsuma spp. to rapidly adjust to
anthropogenic areas (Gardner & Jasper 2015). Such
exibility could also potentially increase the invasion
success of Phelsuma spp., the epicentres of which are
generally urban areas (Gaertner et al. 2017).
Our accounts of six Phelsuma spp. engaging in noc-
turnal activity contribute to the growing knowledge
of impacts ALAN may have on herpetofauna and
underscores the behavioural exibility of these
geckos. We recommend that future research exami-
nes the individual repeatability of this behaviour to
determine if it is consistent over time, if it is more
prevalent within invasive populations compared to
Fig. 3. A gold dust day gecko (Phelsuma laticuada) hand
captured after successfully hunting an ant (Formicidae)
near an amber, incandescent light source on a small build-
ing near Mt. Combani, Mayotte. Photo credited to KCW.
Fig. 4. (a) Mah
e day geckos (Phelsuma sundbergi longinsu-
lae) active at night on the wall of a building near a white,
uorescent light source in Mah
e Island, Seychelles. The
grey gecko associated with them is likely an Asian house
gecko (Hemidactylus frenatus). (b) A close-up of the Mah
e
day gecko (P. sundbergi longinsulae) active at night. Photos
credited to OH.
doi:10.1111/aec.13012 © 2021 Ecological Society of Australia
4 J. BAXTER-GILBERT ET AL.
ones from a speciesnative range, and if there are
secondary impacts on plant communities that rely on
certain Phelsuma spp. for pollination and seed disper-
sal. Overall, our observations suggest that there is a
wealth of research potential surrounding the biologi-
cal strategies employed by these enigmatic lizards to
thrive regardless of environmental change whether
via urbanisation or biological invasions.
ACKNOWLEDGEMENTS
We would like to thank the DSI-NRF Centre for Excel-
lence in Invasion Biology, the Centre for Collaboration
in Africa at Stellenbosch University, the University of
Mauritius, and Prof. John Measey for their support. We
would also like to thank the staff of the National Parks
and Conservation Service in Mauritius and the Depart-
ment of Environment and Forests of the Andaman and
Nicobar Islands and the three reviewers whose sugges-
tions improved the manuscript.
CONFLICT OF INTEREST
The authors state they have no conicts of interest
with respect to this article or its content.
AUTHOR CONTRIBUTIONS
James Baxter-Gilbert: Investigation (equal); Writ-
ing-original draft (lead); Writing-review & editing
(equal). Cl
audia Baider: Investigation (equal);
Writing-original draft (equal); Writing-review & edit-
ing (equal). Vincent Florens: Investigation (equal);
Writing-original draft (equal); Writing-review & edit-
ing (equal). Oliver Hawlitschek: Investigation
(equal); Writing-original draft (equal); Writing-review
& editing (equal). Ashwini V. Mohan: Investigation
(equal); Writing-original draft (equal); Writing-review
& editing (equal). Nitya P. Mohanty: Investigation
(equal); Writing-original draft (equal); Writing-review
& editing (equal). Carla Wagener: Investigation
(equal); Writing-original draft (equal); Writing-review
& editing (equal). Kathleen C. Webster: Investiga-
tion (equal); Writing-original draft (equal); Writing-
review & editing (equal). Julia Riley: Investigation
(equal); Supervision (lead); Writing-original draft
(equal); Writing-review & editing (equal).
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6 J. BAXTER-GILBERT ET AL.
... Endangered 'Eua Forest Gecko Lepidodactylus euaensis from Tonga is of particular concern, given its conservation status and the very high invasion risk identified for this island. Both P. grandis and P. laticauda are diurnal, but can also be active at night due to artificial light (Dubos et al. 2020;Baxter-Gilbert et al. 2021), highlighting the risk of competition with nocturnal species living near anthropogenic structures such as the Critically Endangered Barbados leaf-toed gecko Phyllodactylus pulcher (Williams et al. 2016). The potential impact of invasive Phelsuma species on native fauna may be mitigated by potential plasticity, which could promote microclimatic and/or habitat partitioning (Noble et al. 2011;Porcel et al. 2021;Ryan and Gunderson 2021). ...
... Reptiles may shift their phenology in response to environmental change (Kearney et al. 2009), and this has already been observed in Phelsuma spp. (Dubos et al. 2020;Baxter-Gilbert et al. 2021). Behavioural response to climate change-and therefore phenological shifts-may interact with geographic response (Kearney et al. 2010). ...
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Full-text available
Invasion risks may be influenced either negatively or positively by climate change, depending on the species. These can be predicted with species distribution models, but projections can be strongly affected by input environmental data (climate data source, Global Circulation Models and Shared Socio-economic Pathways SSP). We modelled the distribution of Phelsuma grandis and P. laticauda , two Malagasy reptiles that are spreading globally. We accounted for drivers of spread and establishment using socio-economic factors (e.g., distance from ports) and two climate data sources, i.e., Climatologies at High Resolution for the Earth’s and Land Surface Areas (CHELSA) and Worldclim. We further quantified the degree of agreement in invasion risk models that utilised CHELSA and Worldclim data for current and future conditions. Most areas identified as highly exposed to invasion risks were consistently identified (e.g. in Caribbean and Pacific Islands). However, projected risks differed locally. We also found notable differences in quantitative invasion risk (3% difference in suitability scores for P. laticauda and up to 14% for P. grandis ) under current conditions. Despite both species native distributions overlap substantially, climate change will drive opposite responses on invasion risks by 2070 (decrease for P. grandis, increase for P. laticauda ). Overall, projections of future invasion risks were the most affected by climate data source, followed by SSP. Our results highlight that assessments of current and future invasion risks are sensitive to the climate data source, especially in Islands. We stress the need to account for multiple climatologies when assessing invasion risks.
... The Critically Endangered 'Eua Forest Gecko Lepidodactylus euaensis from Tonga is of particular concern, given its conservation status and the very high invasion risk identified for this island. Both P. grandis and P. laticauda are diurnal, but can also be active at night due to artificial light (Dubos et al. 2020;Baxter-Gilbert et al. 2021), highlighting the risk of competition with nocturnal species living near anthropogenic structures such as the Critically Endangered Barbados leaf-toed gecko Phyllodactylus pulcher (Williams et al. 2016). The . ...
... Reptiles may shift their phenology in response to environmental change (Kearney et al. 2009), and this has already been observed in Phelsuma spp. (Dubos et al. 2020;Baxter-Gilbert et al. 2021). Behavioural response to climate change-and therefore phenological shifts-may interact with geographic response (Kearney et al. 2010). ...
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Invasion risks may be influenced either negatively or positively by climate change, depending on the species. These can be predicted with species distribution models, but projections can be strongly affected by input environmental data (climate data source, Global Circulation Models and Shared Socio-economic Pathways SSP). We modelled the distribution of Phelsuma grandis and P. laticauda, two Malagasy reptiles that are spreading globally. We accounted for drivers of spread and establishment using socio-economic factors (e.g., distance from ports) and two climate data sources, i.e., Climatologies at High Resolution for the Earth's and Land Surface Areas (CHELSA) and Worldclim. We further quantified the degree of agreement in invasion risk models that utilised CHELSA and Worldclim data for current and future conditions. Most areas identified as highly exposed to invasion risks were consistently identified (e.g. in Caribbean and Pacific Islands). However, projected risks differed locally. We also found notable differences in quantitative invasion risk (3% difference in suitability scores for P. laticauda and up to 14% for P. grandis) under current conditions. Despite both species native distributions overlap substantially, climate change will drive opposite responses on invasion risks by 2070 (decrease for P. grandis, increase for P. laticauda). Overall, projections of future invasion risks were the most affected by climate data source, followed by SSP. Our results highlight that assessments of current and future invasion risks are sensitive to the climate data source, especially in Islands. We stress the need to account for multiple climatologies when assessing invasion risks.
... [25][26][27] The night-light niche influences both diurnal predators, which increase their activity patterns during typically dark periods, as well as nocturnal visual predators, which typically alter their hunting patterns in response to changes in natural light levels such as cycles of the moon. 28,29 In cases in which urban-rural gradients are used to look for evidence of night-light niche, increased predation may instead be responding to underlying changes in urban environments or supplemental food sources that are unrelated to increased artificial light. 30,31 Additionally, because these studies compare communities impacted and unaffected by ALAN, they lack comparisons to pre-light Using an array of pitfall traps and artificial lights, we seek to document the extent and temporal speed of artificial-light-induced community-level shifts by experimentally investigating how naive forest arthropod communities (i.e., a community that has not previously experienced light pollution) respond to the introduction of ALAN. ...
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While recent studies explore the negative impacts of light pollution on arthropods, few studies investigated community-level responses to artificial light. Using an array of landscaping lights and pitfall traps, we track community composition over 15 consecutive days and nights, including a five-night pre-light period, a five-night during-light period, and a five-night post-light period. Our results highlight a trophic-level response to artificial nighttime lighting with shifts in the presence and abundance of predators, scavengers, parasites, and herbivores. We show that associated trophic shifts occurred immediately upon the introduction of artificial light at night and are limited to nocturnal communities. Lastly, trophic levels reverted to their pre-light state, suggesting many short-term changes in communities are likely the result of behavioral shifts. These trophic shifts may become common as light pollution increases, implicating artificial light as a cause of global arthropod community change and highlighting light pollution’s role in global herbivorous arthropod decline.
... However, the environment created by ALAN sometimes provides benefit to nocturnal predators. Several studies have reported that insectivores and plankton feeders in a wide range of taxonomic groups come to the artificial light environment (e.g., mammals, Rydell, 1992;Blake et al., 1994;Spoelstra et al., 2015;birds, Santos et al., 2010;reptiles, Case et al., 1994;Thirakhupt et al., 2006;Perry et al., 2008;Martín et al., 2018;Baxter-Gilbert et al., 2021;amphibians, Jaeger and Hailman, 1973;Baker, 1990;Van Grunsven et al., 2017;fish, Ragesh et al., 2014;arachnids, Heiling, 1999). In most cases, these nocturnal predators efficiently forage in the artificial light environment where prey animals (insects and planktons) are clumped (Spooner, 1933;Petren and Case, 1996;Zozaya et al., 2015;Utne-Palm et al., 2018). ...
Article
Nocturnal predators of many taxa are known to come to artificial light at night for foraging on clumped food resources. Both innate and acquired light preferences seem to be possible mechanisms of light approaching behavior although empirical tests are lacking in most nocturnal predators. Here, using a Japanese gecko Gekko japonicus, we investigated whether geckos have a light preference and how foraging experiences under the light reinforce light approaching tendency. In a comparative experiment, there was no difference in light approaching behavior between urban and suburban geckos irrespective of their original light habitats. In an associative learning experiment, geckos did not significantly change light approaching behavior even after repeated opportunities to forage crickets near a lamp in the laboratory setting. These results imply that light approaching behavior of Japanese geckos may not be easily reinforced by foraging experiences under the light. Although we often witness geckos coming to artificial light at night, our findings may not suggest their light preference. Geckos may approach the light-up foraging spot based on other cues relating to the artificial light environment.
... Urban animals shifting to nocturnal foraging may encounter novel food items, competitors, and contexts, leading to new foraging strategies. For example, urban peregrine falcons use artificial lighting to hunt migrating songbirds [41] and some diurnal geckos use fluorescent lights to hunt insects attracted to light [42]. Initial plastic temporal shifts toward nocturnal activity could become fixed over time if selection favors traits that improve nocturnal foraging, such as enhanced hearing, chemosensory abilities, etc. ...
Article
Plasticity-led evolution is central to evolutionary theory. Although challenging to study in nature, this process may be particularly apparent in novel environments such as cities. We document abundant evidence of plastic behavioral changes in urban animals, including learning, contextual, developmental, and transgenerational plasticities. Using behavioral drive as a conceptual framework, our analysis of notable case studies suggests that plastic behaviors, such as altered habitat use, migration, diurnal and seasonal activity, and courtship, can have faciliatory and cascading effects on urban evolution via spatial, temporal, and mate-choice mechanisms. Our findings highlight (i) the need to incorporate behavioral plasticity more formally into urban evolutionary research and (ii) the opportunity provided by urban environments to study behavioral mechanisms of plasticity-led processes.
... Wildlife are adapted to temporally cyclical patterns of light and dark, but artificial light has now illuminated the night skies. ALAN and associated light pollution have significant impacts on nocturnal wildlife, altering activity (Becker et al., 2013;Bird et al., 2018;Baxter-Gilbert et al., 2021), physiology (Bedrosian et al., 2011;Dominoni et al., 2013), and increasing mortality (Rodríguez et al., 2012). In addition, ALAN can alter community composition of invertebrates attracted to artificial lights (Davies et al., 2012), and associated predation patterns (Komine et al., 2020). ...
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Both natural and artificial light at night can strongly influence animal behavior. Nocturnal animals often alter activity dependent on lunar light levels, to increase prey capture, minimize detection by predators, or both. Trade-offs among these ecological effects are likely to have a strong influence on behavior and fitness. Here, we examined the influence of light at night on nocturnal geckos that are both predators and prey, and use both natural and anthropogenic habitats. We tested the influence of illumination on the relative abundance and behavioral activity of native geckos in natural woodlands and under laboratory conditions. We hypothesized that Australian native house geckos (Gehyra dubia) would avoid activity on nights with high moon brightness, to minimize exposure to predators, consistent with the predation risk hypothesis. Counter to our prediction, we found a positive relationship between house gecko activity and moon brightness, i.e., house geckos were more active on bright nights. This behavior may allow house geckos to better see their prey while also increasing the visibility of approaching predators. In the laboratory, house geckos had shorter latency times to emerge from a shelter under low light conditions compared to darkness equivalent to a new moon, a trend consistent with higher activity under brighter conditions in the field. Light at night, from both natural and artificial sources, clearly influences the behavior and activity of geckos, but perhaps not in the ways we expect. Reducing the risk of attack from predators in darkness, and increasing prey capture success using vision, may increase the benefits of activity in lit conditions, compared to total darkness.
... In the last decade, many studies on the foraging behavior and daily activities of geckos have been carried out (Tawa et al., 2014;Haley & Blackshaw, 2015;Bashaw et al., 2016;Baxter-Gilbert et al., 2021). A study on Gekko japonicus shows that the distribution of daily locomotor activity of this species is affected by temperature (Tawa et al., 2014). ...
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To understand the role of the flat-tailed gecko on pest control in urbanized areas, we observed the foraging behavior and daily activity of H. platyurus. It is one of the house geckos easily found but more studies on their behavior are still lacking. The observation was conducted between 14−27 May 2021, for 18 hours starting from 09.00 to 03.00 WIB using the ad libitum sampling method. Our result suggests that the foraging behavior was found almost every hour of observation, which is strongly influenced by relative humidity and insect abundance. This gecko was observed as a sit-and-wait predator or passively searching for prey. Our observation also indicated that this species has potential to control one of the household pests, the adult ants (alates). Hopefully, this study contributed to the understanding of the foraging behavior of the flat-tailed gecko. However, more studies are needed for better understanding of foraging behavior in the flat-tailed gecko.
... birds, de Jong et al., 2018;fish, Fobert et al., 2019;insects, McLay et al., 2018;anurans, Rand et al., 1997), foraging (e.g. lizards, Baxter-Gilbert et al., 2021;birds, Dwyer et al., 2013;bats, Rydell, 1992;spiders, Willmott et al., 2019), communication (e.g. anurans, Baker and Richardson, 2006;birds, Da Silva et al., 2016) and sleep (e.g. ...
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Artificial light at night (ALAN) has rapidly and drastically changed the global nocturnal environment. Evidence for the effect of ALAN on animal behaviour is mounting and animals are exposed to both point sources of light (street and other surrounding light sources) and broadscale illuminance in the form of skyglow. Research has typically taken a simplified approach to assessing the presence of ALAN, yet to fully understand the ecological impact requires consideration of the different scales and sources of light concurrently. Bird song has previously been well studied for its relationship with light, offering an opportunity to examine the relative impact of different sources of light on behaviour. In this study, we combine correlational and experimental approaches to examine how light at night affects the nocturnal song behaviour of the largely diurnal willie wagtail (Rhipidura leucophrys). Observations of willie wagtails across urban and rural locations in southeastern Australia demonstrated that nocturnal song behaviour increased with the intensity of moonlight in darker rural areas but decreased in areas with high sky glow. In addition, willie wagtails were half as likely to sing at night in the presence of localized light sources such as streetlights in urban and rural areas. Experimental introduction of streetlights to a previously dark area confirmed this relationship: willie wagtail song rates declined when lights were turned on and returned to their original rates following streetlight removal. Our findings show that scale, as well as intensity, are important when considering the impact of light at night as moonlight, sky glow, and localized sources of artificial light have different effects on nocturnal song behaviour.
... We therefore suggest classifying this gecko's activity pattern as cathemeral, a term used when significant amounts of activity, such as feeding and foraging, occur during both day and night (Tattersall, 1987). This is in clear difference to other Phelsuma spp. that are classified as diurnal, however, use the artificial light at night (ALAN) niche by altering their foraging behaviour when they have access to artificial light sources (Baxter-Gilbert et al., 2021). Interestingly, P. ornata was reported to display some degree of nocturnal activity in the absence of artificial light sources from Ile aux Aigrettes (Cole and Harris, 2011). ...
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The island of Mauritius in the Mascarenes has already suffered high levels of extinction, and habitat destruction and invasive alien species have pushed many of the remaining endemic species to the brink of extinction. Round Island, a small island northeast of Mauritius, is home to remnant populations of several reptile species that were once distributed across Mauritius. One of the most threatened of these is Günther’s gecko Phelsuma guentheri, where despite extensive management efforts, population size remains small and below expectation. We identify determinants of nest-site suitability across Round Island, and examine whether suitable nest sites are a limiting factor for the abundance of P. guentheri. Over one breeding season, we recorded and monitored a high number (269) of nest sites harbouring a total of 1,475 eggs. We used the number of eggs at each nest, and the hatching success as proxies for nest-site suitability. To study the reproductive behaviour of P. guentheri, we installed trail cameras at three nest sites. We did not find the expected high frequency of use of hardwood trees as nest sites, as found on Ile aux Aigrettes to the southeast of Mauritius, probably because hardwood trees are still relatively sparse and small on Round Island. Instead, the endemic palm Latania loddigesii was the most used nest sites, harbouring 78.8% of all nests with 56.3% of all eggs. Hatching success was high for palm nest sites (90.6%), rock surfaces (91.8%), and on the endemic screw pine Pandanus vandermeeschii (96%), rates that are similar to that reported from hardwood trees on Ile aux Aigrettes (∼90%). Communal nesting occurred on all substrates, with up to five individuals using the same nest site. Egg-laying took place at dusk or at night, lasting around 30 minutes, whereas hatching occurred mostly during the day, lasting 2–107 minutes. Females laid eggs every 34 days on average, and produced up to four clutches of 1-2 eggs each within the season. We conclude that P. guentheri does not suffer from nest site limitation on Round Island, and that reproductive success is high in terms of both numbers of eggs laid and hatching success, likely due to ongoing habitat restoration. Further research is needed to investigate the factors inhibiting abundance and distribution of P. guentheri on Round Island.
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This paper presents a nocturnal activity of the Phelsuma inexpectata in population introduced of the Tampon town. The nocturnal activity in species of the genus Phelsuma should be mentioned
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Widespread human development has led to the proliferation of artificial light at night, an increasingly recognized but poorly understood component of anthropogenic global change. Animals specialized to diurnal activity are presented opportunities to use this night-light niche, but the ecological consequences are largely unknown. While published records make note of nocturnal activity in a diversity of diurnal taxa, few case studies have gone beyond isolated observations to quantify patterns of nocturnal activity, document animal behavior, and describe new species interactions. From 13 June to 15 July 2017, we conducted hourly nocturnal surveys to assess how two species of diurnal Anolis lizards (Leach's Anole, Anolis leachii, and Watt's Anole, A. wattsi) use artificial light on Long Island, Antigua. Our data show that both anole species foraged in artificially illuminated habitats and were more active prior to sunrise compared to the early night. Mark-resight data for a focal species, A. leachii, suggest that patterns of nocturnal activity were not significantly different between individuals. Finally, our behavioral observations for the two anoles and a third lizard species, the nocturnal Thick-tailed Gecko (Thecadactylus rapicauda), reveal a lack of agonistic interactions. Our study reveals an altered temporal niche for two diurnal Antiguan lizards and adds to a growing body of evidence documenting the broad influences of anthropogenic change on biodiversity.
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Natural cycles of light and darkness govern the timing of most aspects of animal behavior and physiology. Artificial light at night (ALAN)—a recent and pervasive form of pollution—can mask natural photoperiodic cues and interfere with biological rhythms. One such rhythm vulnerable to perturbation is the sleep–wake cycle. ALAN may greatly influence sleep in humans and wildlife, particularly in animals that sleep predominantly at night. There has been some recent evidence for impacts of ALAN on sleep, but critical questions remain. Some of these can be addressed by adopting approaches already entrenched in sleep research. In this paper, we review the current evidence for impacts of ALAN on sleep, highlight gaps in our understanding, and suggest opportunities for future research. Artificial light at night can have profound impacts on sleep in diurnal species. Here, we review the evidence for impacts of light at night on sleep in humans and wildlife, and provide a prospectus for future research.
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The Manapany day gecko Phelsuma inexpectata Mertens, 1966 endemic to the south of Réunion Island, is a threatened species currently closely associated with the coastal habitat, one of the most endangered ecosystem on the island. We investigated the extent and the evolution of its distribution and its population size and density. We found that the species is extremely restricted, with an extent of occurrence (EOO) and an area of occupancy (AOO) of around 6 km² and 1 km² respectively. Since 1995, several sub-populations have disappeared and the population size has dropped to between 3 000 and 5 000 individuals. We located 15 populations, severely fragmented by urbanisation, agriculture and invasive vegetation. This habitat loss and fragmentation is perceived as the most serious threat, followed by interactions with alien animals (predation/competition) and by environmental pollution. The species qualifies as Critically Endangered according to the IUCN Red-List Criteria. We propose a first conservation strategy to avoid the possible extinction of the Manapany day gecko.
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We review the intrageneric systematics of day geckos, genus Phelsuma (Squamata: Sauria: Gekkonidae) in the light of a recently published multigene phylogeny, and provide an overview of 19 selected chromatic, morphological and behavioural characters for all currently recognized species and subspecies in the genus. To replace previous attempts of dividing the genus into phenetic species assemblages, we propose the following monophyletic species groups and summarize the morphological characters that partly support this grouping: Phelsuma barbouri group (P. barbouri, P. pronki); P. dubia group (P. berghofi, P. dubia, P. flavigularis, P. hielscheri, P. malamakibo, P. modesta, P. nigristriata, P. ravenala); P. mutabilis group (P. borai, P. breviceps, P. mutabilis); P. cepediana group (P. borbonica, P. cepediana, P. guentheri, P. guimbeaui, P. inexpectata, P. ornata, P. rosagularis as well as the extinct species P. edwardnewtonii and P. gigas); P. astriata group (P. astriata, P. sundbergi); P. madagascariensis group (P. abbotti, P. grandis, P. guttata, P. kochi, P. madagascariensis, P. parkeri, P. seippi and probably P. masohoala); P. lineata group (P. antanosy, P. comorensis, P. kely, P. lineata, P. pusilla, P. quadriocellata and probably P. hoeschi); P. laticauda group (P. laticauda, P. pasteuri, P. robertmertensi, P. v-nigra); P. klemmeri group (P. klemmeri); P. andamanense group (P. andamanense) and P. standingi group (P. standingi). Due to their equivocal placements based on different molecular markers, we refrain from assigning P. serraticauda and P. vanheygeni to any of these species groups at this time. We complement the molecular data with new trees based on partial sequences of the 16S rRNA gene for the P. madagascariensis- and P. lineata groups and propose to elevate P. lineata dorsivittata and P. quadriocellata parva to full species rank as P. dorsivittata and P. parva.
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Although urban ecosystems are hotspots for biological invasions, the field of invasion science has given scant attention to invasion dynamics and the challenges facing managers in towns and cities. This paper provides an introduction to the growing challenges of understanding and managing invasive species in urban systems, and the context for a special issue of Biological Invasions, comprising 17 papers, that arose from a workshop on “Non-native species in urban environments: patterns, processes, impacts and challenges” held in Stellenbosch, South Africa, in November 2016. Contributions explore the following key questions: Are patterns and processes of urban invasions different from invasions in other contexts? Why is it important to manage non-native species in urban ecosystems? What are the special management needs in an urban context? How can we bridge the gaps between science, management, and policy with regards to biological invasions in urban ecosystems? The papers in this special issue show that patterns and processes of urban invasions differ in many ways from invasions in other contexts, and that managing invasive species in cities poses unique and increasingly complex challenges. Progress in urban invasion science requires further work to: (1) address key limitations that hinder our understanding of invasion dynamics in cities; (2) clarify whether fundamental concepts in the field of invasion science are appropriate for urban ecosystems; (3) integrate insights from invasion science with those from the burgeoning literature on the “Anthropocene biosphere”, novel ecosystems, social–ecological systems, human–wildlife conflicts, urban green infrastructure, urban planning and design, and ecosystem services/disservices.
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The day gecko genus Phelsuma provides an ideal group in which to investigate the behavioural adaptations that permit survival in urban ecosystems, because it spans the spectrum of degradation tolerance from obligate forest specialists to human commensals. We opportunistically recorded foraging observations of Phelsuma modesta leiogaster in a house and garden in urban Toliara, southwest Madagascar, and found the diet to consist principally of natural and artificial sources of sugar (including fruits, honey, sugar, syrups and chocolate), with only 2 % of foraging observations consisting of invertebrates. Many Phelsuma species consume fruit, pollen or nectar in their diets, and we suggest that the specialisation on sugary foods may permit some species to adapt to urban environments where the availability of such food sources may be artificially high.