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The threat of discarded food and drinks containers to monitor lizards

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Zdunek, P. and Kolenda, K. 2022. The threat of discarded food and drinks containers to monitor lizards. Herpetological Bulletin 161: 28-30 ___________________________________________________________________________________ The aim of this note is to show that littering is a serious threat to monitor lizards. We present 30 cases where varanids got stuck inside discarded beverage or food containers. These include eight species of which Varanus acanthurus was the most common. The accidents took place in at least six countries. The most common traps were drink and food cans. In five containers lizards were found dead.
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28 Herpetological Bullen 161 (2022)
INTRODUCTION
Monitor lizards (family Varanidae) have a wide distribuon
in the tropics and sub-tropics including Australasia,
south and south-east Asia, Africa, and the Middle East (Koch
et al., 2013; Auliya & Koch, 2020). They have an important
role in ecosystem as predators, scavengers, and creators
of microhabitats for other animals (Doody et al., 2021).
Typically, monitors are big lizards and the family includes the
largest living lizard, the Komodo dragon Varanus komodoensis
whose adult males measure up to 3.1 m and weigh up to
100 kg (Jessop et al., 2006). However, there are some small
species, e.g. Varanus sparnus the adults of which may have a
body length of only 23 cm and mass of 17 g (Koch et al., 2013;
Auliya & Koch, 2020).
Only 14 of the 68 species listed by IUCN are considered to
be of conservaon concern although 10 other species are Data
Decient (IUCN, 2021). Currently, the major anthropogenic
threats to monitor lizards include the degradaon of their
natural habitats, uncontrolled tourism, and pet trade (Koch et
al., 2013; Zdunek, 2019; Arieandy et al., 2021). Locally, road
mortality may also limit their populaons (Hasngs et al.,
2019; Ayob et al., 2020). Moreover, monitor meat is traded
and consumed as a novelty food, a tradional remedy for a
range of ailments (skin diseases, eczema, asthma, blindness),
as an aphrodisiac (Uyeda et al., 2014; Nijman, 2015; Zdunek,
2019), and there is sll demand for monitor skin from the
leather industry (Boscha et al., 2020). Progressive global
warming may also cause a decrease in their habitat patch
occupancy (Jones et al., 2020).
It is well known that many monitor lizards exploit urban
habitats, especially rubbish dumps, which provide food
(Kulabtong & Mahaprom, 2015; Karunarathna et al., 2017).
Indeed, such liered areas are characterised by higher
populaon abundance compared to undisturbed habitats
(Uyeda, 2009; Jessop et al., 2012). Although feeding on
organic waste can improve the lizards’ body condion and
reduce the parasite load (Jessop et al., 2012), availability
of such food alters their behaviour and presents them with
many threats. Associaon with rubbish dumps impacts some
important aspect of monitor biology including - sex rao
(male-biased; Jessop et al., 2012); movement paerns by
reducing species home ranges (Stanner & Mendelssohn,
1987); increased antagonisc interacons and social
hierarchy (Uyeda et al., 2015); reduced ospring survival due
to cannibalism or predaon (Jessop et al., 2012); and reduce
reproducve success due to high levels of mate compeon
(Jessop et al., 2012). Moreover, feeding on anthropogenic
food waste can lead to internal injuries and consequently to a
slow death (Trembath & Freier, 2005; Gillet & Jackson, 2010).
Another, but sll understudied threat is geng stuck in food
or drinks containers. A monitor lizard may put its head into a
container or enter it completely to eat food leovers or other
animals that got stuck therein before. However, geng the
head out of the container may be a problem, and such an
incident is oen fatal. A recent study revealed that beside
invertebrates and mammals, reples are quite oen exposed
to such danger. Among 77 reple-container interacons, 13
(17 %) concerned monitor lizards (Kolenda et al., 2021).
Herein, we highlight the problem of discarded food/
drinks containers by presenng new observaons of monitor
lizards that we obtained from other sciensts and naturalists
combined with those reported previously (Kolenda et al.,
2021). Full details are presented in Supplementary Materials
(Table 1S) and include a total of 32 cases of monitors stuck
in discarded containers (Fig. 1). Most events occurred in
Australia (18, 56 % of all cases). Observaons were made
on eight monitor species, of which Varanus acanthurus
was the most common (9 cases, 28 %). None of the species
observed were in an IUCN Red List threatened category
although Varanus nebulosus and Varanus similis have not
been evaluated. In six containers (19 %), the monitors were
found dead. In the remaining 26 (81 %), they were alive at
the me of observaon, and at least in 22 of these cases
they were rescued by an observer or transported to a wildlife
rescue. The most common container in which the trapped
animals were observed was drinks cans (18, 56 %), followed
by food cans (12, 38 %), and a single plasc jar (3 %), and an
unrecorded type of container (3 %).
Discarded containers are common lier items in
terrestrial environments (Roman et al., 2020). They pose a
threat to various groups of animals, including arthropods and
small vertebrates as well as large animals such as ungulates,
leopards or bears (Kolenda et al., 2021). By themselves
mortality due to such containers would not be expected
to lead to a populaon decline, but they constute one of
The Herpetological Bulletin 161, 2022: 28–30
The threat of discarded food and drinks containers to monitor
lizards
PRZEMYSŁAW ZDUNEK1,2 & KRZYSZTOF KOLENDA3*
1Associaon du Refuge des Tortues (A.R.T.), 2920 Route de Paulhac, 31660 Bessières, France
2NATRIX Herpetological Associaon, ul. Opolska 41/1, 52-010 Wrocław, Poland
3Department of Evoluonary Biology and Conservaon of Vertebrates, University of Wrocław, Sienkiewicza 21, 50-335,
Wrocław, Poland
*Corresponding author e-mail: krzysztof.kolenda@uwr.edu.pl
hps://doi.org/10.33256/hb161.2830
SHORT NOTE
Herpetological Bullen 161 (2022) 29
The threat of discarded food and drinks containers to monitor lizards
many factors that synergiscally may limit the populaon
size, especially in urban habitats. However, in the case of
the Crically Endangered Bermuda rock skink Plesodon
longirostris, an endemic lizard of Bermuda, discarded
containers are indeed one of the main threats (Davenport et
al., 2001). It should be noted that containers such as boles
or cups are also a potenal trap for reples (for details see
Figure 4a in Kolenda et al., 2021), whereas other garbage
poses other direct threats to reples, e.g. by ingeson or
entanglement (Walde et al., 2007; Strine et al., 2014).
Due to the relave rarity of the above-menoned
observaons, the real impact of discarded containers on
monitor populaons remains poorly understood. Taking
into consideraon reports presented herein, we strongly
encourage conservaonists to pay aenon to this issue.
Workshops on conservaon of wildlife (such as presented
by Bhaacharya et al., 2019) that aim to raise public
awareness should menon the harmful eects of lier on
animals. Suggesons for liming impacts should include - to
implement strict regulaons regarding liering and waste
disposal; to install garbage bins along hiking paths and
ensure that they are emped regularly; and, to engage local
communies in rubbish clean-up acons.
ACKNOWLEDGEMENTS
Our thanks to the following for the use of their photographs:
Owen Gale (Fig. 1A), Ben Campbell (Fig. 1B), Zig Madycki
(Fig. 1C), Nicole Haigh (Fig. 1D) and Paul Vandersar (Fig. 1E).
We would also like to thank Ulysse Boiteau-Montéville and
Brian Bush for sharing their observaons of trapped monitor
lizards, and Chris van Kalken for his help in conrming the
idencaon of some species and all who sent us new
records published in the social media.
REFERENCES
Arieandy, A., Purwandana, D., Azmi, M., Nasu, S.A., Mardani,
J., Cio, C. & Jessop, T.S. (2021). Human acvies
associated with reduced Komodo dragon habitat use and
range loss on Flores. Biodiversity and Conservaon 30:
461–479.
Ayob, N., Muzneena, A.M., Senawi, J. & Ahmad, N. (2020).
Herpetofauna roadkills on Langkawi Island, Peninsular
Malaysia: The Inuence of landscape and season on
mortality distribuon. Sains Malaysiana 49: 2373–2382.
Auliya, M. & Koch, A. (2020). Visual Idencaon Guide for
the Monitor Lizard Species of the World (Genus Varanus):
Guidance for the Idencaon of Monitor Lizards with
Current Distribuon Data as well as Short Explanaons
on Reproducve Characteriscs and Capve Breeding
to Support CITES Authories. Bonn, Germany: Federal
Agency for Nature Conservaon, 202 pp.
Bhaacharya, S., Zia, S.Z., Mahato, S., Gangwar, R.K., Singh,
N., Auliya, M. & Koch, A. (2019). Report on the Awareness
Workshops “Percepons of Wildlife Conservaon of
Today’s Youth in West Bengal, India, with a Focus on
Monitor Lizards”. Biawak 13: 94–100.
Boscha, E., Arida, E. & Satria, D. (2020). Dorsal colour paerns
of Asian water monitor, Varanus salvator collected
for trade in Cirebon, Indonesia. Journal of Tropical
Ethnobiology 3: 133–138.
Davenport, J., Hills, J., Glasspool, A. & Ward, J. (2001).
Threats to the crically endangered endemic Bermudian
skink Eumeces longirostris. Oryx 35: 332–339.
Doody, J.S., Soennichsen, K.F., James, H., McHenry C. &
Clulow S. (2021). Ecosystem engineering in deep-nesng
monitor lizards. Ecology 18: e03271.
Gillet, A. & Jackson, R. (2010). Human food scrap ingeson in
two wild lace monitors Varanus varius. Biawak 4: 99–102.
Hasngs, H., Barr, J. & Bateman, P.W. (2019). Spaal and
temporal paerns of reple roadkill in the north-west
Australian tropics. Pacic Conservaon Biology 25:
370–376.
IUCN. (2021). The IUCN Red List of Threatened Species,
hp://www.iucnredlist.org [accessed on 2 March 2021].
Jessop, T.S., Madsen, T., Sumner, J., Rudiharto, H., Phillips,
J.A. & Cio, C. (2006). Maximum body size among insular
Figure 1. Examples of monitor lizards from Australia with
their heads stuck in discarded drinks cans - A–D. Varanus
acanthurus, C. Varanus similis
30 Herpetological Bullen 161 (2022)
Przemyslaw Zdunek & Krzysztof Kolenda
Komodo dragon populaons covaries with large prey
density. Oikos 112: 422–429.
Jessop, T.S., Smissen, P., Scheelings, F. & Dempster, T. (2012).
Demographic and phenotypic eects of human mediated
trophic subsidy on a large Australian lizard (Varanus
varius): meal cket or last supper? PLoS One 7: e34069.
Jones, A.R., Jessop, T.S., Arieandy, A., Brook, B.W., Brown,
S.C., Cio, C., Benu, Y.J., Purwandana, D., et al. (2020).
Idenfying island safe havens to prevent the exncon of
the World’s largest lizard from global warming. Ecology
and Evoluon 10: 10492–10507.
Karunarathna, D.M.S.S., Surasinghe, T.D., Dissanayake, D.,
Botejue, M., Gabadage, D. & Madawale, M.B. (2017).
Dietary habits and the predators of the Bengal monitor
Varanus bengalensis in Sri Lanka. Biawak 11: 28–39.
Koch, A., Ziegler, T., Bohme, W., Arida, E. & Auliya, M.
(2013). Distribuon, threats, and conservaon status of
the monitor lizard (Varanidae: Varanus ssp.) of Southern
Asia and the Indo-Australian achipelago. Herpetological
Conservaon and Biology 8: 1–62.
Kolenda, K., Pawlik, M., Kuśmierek, N., Smolis, A. & Kadej,
M. (2021). Online media reveals a global problem of
discarded containers as deadly traps for animals. Scienc
Reports 11: 267.
Kulabtong, S. & Mahaprom, R. (2015). Observaon on food
items of Asian water monitor, Varanus salvator (Lauren,
1768) (Squamata Varanidae), in urban ecosystem, Central
Thailand. Biodiversity Journal 6: 695–698.
Nijman, V. (2015). Water monitor lizards for sale as novelty
food in Java, Indonesia. Biawak 9: 28–32.
Rahman, K.M.M., Rakhimov, I.I. & Khan, M.M.H. (2017).
Public atudes toward monitor lizards (Replia:
Varanidae): A conservaon challenge in the human-
dominated ecosystems of Bangladesh. Annual Research
& Review in Biology 13: 1–10.
Roman, L., Hardesty, B.D., Leonard, G.H., Pragnell-Raasch,
H., Mallos, N., Campbell, I. & Wilcox, C. (2020). A global
assessment of the relaonship between anthropogenic
debris on land and the seaoor. Environmental Polluon
264: 114663.
Strine, C.T., Silva, I., Crane, M., Nadolski, B., Artchawakom,
T., Goode, M. & Suwanwaree P. (2014). Mortality of a
Wild King Cobra, Ophiophagus hannah Cantor, 1836
(Serpentes: Elapidae) from Northeast Thailand aer
Ingesng a Plasc Bag. Asian Herpetological Research 5:
284–286.
Stanner, M. & Mendelssohn, H. (1987). Sex rao, populaon
density and home range of the desert monitor (Varanus
griseus) in the southern coastal plain of Israel. Amphibia-
Replia 8: 153–163.
Trembath, D. & Freier, D. (2005). Accidental ingeson
of barbecue scraps leads to death of a varanid in the
Northern Territory. Herpetofauna 35: 48–49.
Uyeda, L.T. (2009). Garbage appeal: relave abundance
of water monitor lizards (Varanus salvator) correlates
with presence of human food leovers on Tinjil Island,
Indonesia. Biawak 3: 9–17.
Uyeda, L.T., Iskandar, E., Purbatrapsila, A., Pamungkas,
J., Wirsing, A. & Kyes, R. (2014). Water monitor lizard
(Varanus salvator) satay: A treatment for skin ailments
in Muarabinuangeun and Cisiih, Indonesia. Biawak 8:
35–38.
Uyeda, L.T., Iskandar, E., Kyes, R.C. & Wirsing, A.J. (2015).
Encounter rates, agonisc interacons, and social
hierarchy among garbage-feeding water monitor lizards
(Varanus salvator biviatus) on Tinjil Island, Indonesia.
Herpetological Conservaon and Biology 10: 753–764.
Walde, A.D., Harless, M.L., Delaney, D.K. & Pater, L.L. (2007).
Anthropogenic threat to the desert tortoise (Gopherus
agassizii): lier in the Mojave Desert. Western North
American Naturalist 67: 147–149.
Zdunek, P. (2019). W krainie ostatnich żyjących smoków.
Salamandra 47: 44–47.
Please note that the Supplementary Material for this arcle is available online via the Herpetological Bullen website:
hps://thebhs.org/publicaons/the-herpetological-bullen/issue-number-161-autumn-2022
Accepted: 19 May 2022
The threat of discarded food and drinks containers to monitor
lizards
PRZEMYSŁAW ZDUNEK & KRZYSZTOF KOLENDA
Table1S. A list of monitor lizards that were found in discarded containers, AD - adult, SUB sub-adult, JUV - juvenile, D -
dead, L - live
Species
Life
stage
Dead
/Live
Country
Type
of container
Source/Observer
Varanus acanthurus
A
D
Australia
Drink can
Kolenda et al. 2021
Varanus acanthurus
A
L
Australia
Drink can
Kolenda et al. 2021
Varanus acanthurus
A
L
Australia
Drink can
Brian Bush;
https://youtu.be/2cDWddRjhB0;
access date 02.03.2021
Varanus acanthurus
A
L
Australia
Drink can
Ben Campbell
Varanus acanthurus
A
D
Australia
Drink can
Owen Gale
Varanus acanthurus
A
L
Australia
Drink can
Zig Madycki
Varanus acanthurus
A
D
Australia
Drink can
https://www.exploroz.com/Onthe
Road/Environment/Care.aspx;
access date 02.03.2021
Varanus acanthurus
A
D
Australia
Drink can
Eidenmüller 2021
Varanus acanthurus
A
L
Australia
Drink can
Nicole Haigh
Varanus bengalensis
JUV
L
India
Drink can
https://www.youtube.com/watch?
v=V9864TtY3ho; access date
02.03.2021
Varanus bengalensis
A
L
India
Plastic jar
https://www.youtube.com/watch?
v=NK0Yxic-8sA; access date
02.03.2021
Varanus gouldii
SUB
L
Australia
Drink can
Kolenda et al. 2021
Varanus gouldii
SUB
D
Australia
Drink can
Kolenda et al. 2021
Varanus gouldii (flavirufus
type)
SUB
L
Australia
Drink can
Kolenda et al. 2021
Varanus gouldii
SUB
L
Australia
Drink can
Owen Gale
Varanus nebulosus
A
L
No data
Food can
Kolenda et al. 2021
Varanus nebulosus*
A
L
Malay
Peninsula
Food can
Kolenda et al. 2021
Varanus nebulosus
A
L
Malaysia
Food can
https://youtu.be/37csnfVDJxA;
access date 02.03.2021
Varanus nebulosus
A
L
Thailand
Food can
https://au.news.yahoo.com/monit
or-lizard-helped-getting-head-
120000925.html; access date
02.03.2021
Varanus nebulosus
A
L
Malaysia
Food can
https://www.youtube.com/watch
?v=k28heE7RBEQ; access date
02.03.2021
Varanus niloticus
A
L
South
Africa
Food can
Kolenda et al. 2021
Varanus salvator
macromaculatus
A
L
Thailand
Food can
Kolenda et al. 2021
Varanus salvator
macromaculatus
A
L
Thailand
Food can
Kolenda et al. 2021
Varanus salvator
macromaculatus
A
D
Thailand
undetermine
d type
Ulysse Boiteau-Montéville
Varanus salvator
macromaculatus
A
L
Thailand
Food can
https://www.facebook.com/watch
/?v=822815378270890; access
date 02.03.2021
Varanus salvator
macromaculatus
A
L
Thailand
Food can
https://www.youtube.com/watch?
v=RnlXy7rJ84c; access date
02.03.2021
Varanus salvator
macromaculatus
A
L
Thailand
Food can
https://www.facebook.com/watch
/?v=1204178096408768; access
date 02.03.2021
Varanus similis**
A
L
Australia
Food can
Kolenda et al. 2021
Varanus similis
A
L
Australia
Drink can
Paul Vandersar
Varanus tristis
A
L
Australia
Drink can
Kolenda et al. 2021
Varanus tristis
A
L
Australia
Drink can
Kolenda et al. 2021
Varanus tristis
A
L
Australia
Drink can
https://www.sciencesource.com/a
rchive/Lizard-with-Head-Stuck-in-
Beer-Can-SS2422609.html; access
date 02.03.2021
*initially determined as V. komodoensis, but after detailed inspection and consultation with an expert, we suggest it is V. nebulosus
**initially determined as V. scalaris, however, correct name is still under debate, but according to Auliya and Koch, 2020,
Eidenmüller, 2021 and www.reptile-database.org/[accessed 02-03-2021], it should probably be V. similis
REFERENCES
Auliya, M. & Koch, A. (2020). Visual Identification Guide for the Monitor Lizard Species of the World
(Genus Varanus): Guidance for the Identification of Monitor Lizards with Current Distribution
Data as well as Short Explanations on Reproductive Characteristics and Captive Breeding to
Support CITES Authorities. Bonn, Germany: Federal Agency for Nature Conservation, 202 pp.
Eidenmüller, B. (2021). The book of monitor lizards. Edition Chimaira, Frankfurt am Main, 320 pp.
Kolenda, K., Pawlik, M., Kuśmierek, N., Smolis, A. & Kadej, M. (2021). Online media reveals a global
problem of discarded containers as deadly traps for animals. Scientific Reports 11: 267.
The Reptile Database. (2021). Varanus similis MERTENS, 1958. https://reptile-
database.reptarium.cz/species?genus=Varanus&species=similis [accessed 02-03-2021]
... Varanids are a relatively small but diverse group of lizards, currently comprising 88 recognized species (Uetz et al., 2024). These lizards are facing significant main and potential threats within their natural habitats, including habitat destruction, road mortality, human consumption, uncontrolled pet trade, and even from items discarded by humans (Koch et al., 2013;Ayob et al., 2020;Zdunek and Kolenda, 2022;Böhme et al., 2023;Zdunek and Stenger, 2023). Additionally, progressive global warming could potentially lead to a decrease in habitat patch occupancy (Jones et al., 2020;Shadloo et al., 2021). ...
Article
Full-text available
Zdunek, P. Bouazza, A., Martínez del Mármol, G. 2024. Dragons in desert trouble: anthropogenic wells as a potential threat to the Desert Monitor, Varanus griseus (Daudin, 1803), in Morocco. Herpetology Notes 17: 821-826.
... Location 2, which is the estuary of the Kelumpang River, is often used as a garbage dump by villagers. Trash can be a threat to herpetofauna, for example varanid lizard can be stuck in discarded drinks cans (Zdunek & Kolenda 2022) and microhabitat pollution by garbage (Lubis et al. 2008;Botejue & Wattavidanage 2012). If no waste management is implemented on Karimata Island, not only the local herpetofauna is affected, but also large-scale habitat destruction can occur. ...
Article
Full-text available
Karimata Island is an island about 100 km west of Borneo, causes geographical isolation and generally always shows an impact on the diversity of animal communities that are less, one of the communities affected is herpetofauna. Herpetofauna is very important in an ecosystem so it is necessary to conduct a survey. The survey was conducted from April 1 to April 7, 2023 in Betok Jaya Village, Karimata Island which was divided in 3 observation areas based on habitat type using the Visual Encounter Survey method. Herpetofauna found consisted in 22 species divided into 5 species of amphibians and 17 species of reptiles with a total of 43 individuals. Herpetofauna located adjacent to human areas is vulnerable to various disturbances such as maritime transportation activities, household waste pollution and land clearing, which can be a threat to the herpetofauna community of Karimata Island.
... The unintentional entrapment of reptiles does not apply solely to fishing nets. These have also been documented in fishing traps (Crane et al., 2016), oliveharvesting nets (Zevgolis and Christopoulos, 2023), or other similar human-discarded items (Miranda et al., 2013;Udyawer et al., 2013;Blettler and Mitchell, 2021;Zdunek and Kolenda, 2022). Furthermore, due to weathering, abrasion, and biofouling, abandoned fishing nets and other man-made plastic objects deteriorate over time, releasing smaller fragments into the environment, which potentially may increase the risk of ingestion and the release of microplastics (Gajanur and Jaarar, 2023). ...
Article
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Zdunek, P., Kłodawska, M. 2023. First predation of a Nile Monitor Varanus niloticus (Linnaeus, 1758) by a Central African Rock Python Python sebae (Gmelin, 1789) in Cameroon, with emphasis on local abandoned fishing nets and their potential threats. Herpetology Notes 16: 477-481
... However, to the extent of our knowledge, this is the first reported case of a terrestrial serpent caught in discarded fishing nets. On the other hand, the fortuitous trapping of reptiles by sundry humanthrown materials (Miranda et al., 2013;Blettler & Mitchell, 2021;Zdunek & Kolenda, 2022), or their Not only an aquatic threat: A Caspian whipsnake Dolichophis caspius (Gmelin, 1789) entangled in discarded fishing net onshore on Lesvos Island, Greece 195 unintended capture as bycatch in traps meant for other fauna species (Crane et al., 2016;Christopoulos et al., 2021), and within artificial structures (Woinarski et al., 2000;Doody et al., 2003;Manning, 2007;García-Cardenete et al., 2014), have been well-documented in many cases. In particular, trapping by farming and gardening materials and equipment has also been witnessed (Stuart et al., 2001;Brown & Sleeman, 2002;Kapfer & Paloski, 2011;Šmíd, 2012;Christopoulos & Pafilis, 2021;. ...
Article
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The use of fishing nets has a widespread impact on marine, saline-brackish, and freshwater environments, as well as the species occurring in them. While the nets are intended to capture fish and other target species, they often result in high mortality rates of many other fauna species through bycatch and entanglement. Fishing nets that are lost, destroyed, or reach the end of their lifespan are often referred to as "ghost nets", posing a major threat to fauna as hundreds of species become fatally entangled. Here, we report for the first time an incident of a terrestrial snake, a Caspian whipsnake (Dolichophis caspius), which we found entangled onshore in a ghost net on Lesvos Island, Greece. The snake was released into its natural habitat after being carefully disentangled. This incident highlights the need for proper disposal of fishing nets to prevent future entanglements and mortality of non-target species.
... However, the unintentional entrapment of reptiles by various human-discarded items [27][28][29] or as bycatch in traps that are intended for other faunal species [30,31], and within anthropogenic structures [32][33][34][35], has been well documented on numerous occasions. In particular, trapping by agricultural and gardening items and equipment has also been observed [36][37][38][39], with one such case being reported in the context of olive cultivation [40]. ...
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Several awareness workshops were jointly organized by the Environment, Agriculture and Education Society (EAES) along with the International Union for Conservation of Nature and Natural Resources (IUCN) Species Survival Commission's (SSC) Monitor Lizard Specialist Group (MLSG) in five districts of West Bengal, India from 29 July to 2 August 2019. The main objective of the workshops was to create widespread awareness among the local youth regarding the conservation, utilization and illegal trade of wildlife, with a special focus on monitor lizards in India. In total, more than 1,000 students aged 12 to 24 participated in the workshops.
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