<!DOCTYPE article PUBLIC "-//NLM//DTD JATS (Z39.96) Journal Archiving and Interchange DTD v1.0 20120330//EN" "JATS-archivearticle1.dtd">
<article xmlns:xlink="http://www.w3.org/1999/xlink">
  <front>
    <journal-meta>
      <issn pub-type="ppub">1613-0073</issn>
    </journal-meta>
    <article-meta>
      <title-group>
        <article-title>How to improve the estimation of red deer (Cervus elaphus) population density in Serbia</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Miroslav</string-name>
          <email>miroslav.urosevic@stocarstvo.edu.rs</email>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Urošević</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
          <xref ref-type="aff" rid="aff4">4</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Jovan</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Mirceta</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Bojan Tubic</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Dejan Beukovic</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
          <xref ref-type="aff" rid="aff4">4</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Samantha Wisely</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Workshop</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>4th International Workshop on Camera Traps</institution>
          ,
          <addr-line>AI, and Ecology, 2024</addr-line>
        </aff>
        <aff id="aff1">
          <label>1</label>
          <institution>Game animals</institution>
          ,
          <addr-line>Counting, Drones, South East Europe</addr-line>
        </aff>
        <aff id="aff2">
          <label>2</label>
          <institution>Public Enterprise Vojvodinasume</institution>
          ,
          <addr-line>Preradovićeva 2, Petrovaradin-Novi Sad</addr-line>
          ,
          <country country="RS">Serbia</country>
        </aff>
        <aff id="aff3">
          <label>3</label>
          <institution>University of Florida - Cervidae Health Research Initiative</institution>
          ,
          <addr-line>110 Newins-Ziegler Hall, Gainesville, FL</addr-line>
          ,
          <country country="US">USA</country>
        </aff>
        <aff id="aff4">
          <label>4</label>
          <institution>University of Novi Sad, Faculty of Agriculture</institution>
          ,
          <addr-line>Dep. of Animal Science Novi Sad, Trg Dositeja Obradovica 8; Novi Sad</addr-line>
          ,
          <country country="RS">Serbia</country>
        </aff>
      </contrib-group>
      <abstract>
        <p>Spatial and temporal estimates of population abundance or density are essential to evaluate whether conservation eforts are having the desired efects on endangered species and to determine the impact of extrinsic efects such as climate change or land use change, or the intrinsic threats such as disease outbreaks. Precise estimates are challenging because red deer have a relatively large radius of movement between the place where they stay during the day and where they take food at night which can lead to counting errors of 10, 20 and even 50%.</p>
      </abstract>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>1. Introduction</title>
      <p>
        Accurate, consistent, and efective estimation of the population abundance of wildlife species is crucial
for adaptive management and conservation of natural ecosystems. Spatial and temporal estimates of
population abundance or density are essential to evaluate whether conservation eforts are having the
desired efects on endangered species and to determine the impact of extrinsic efects such as climate
change or land use change, or the intrinsic threats such as disease outbreaks. Population and species
monitoring are important elements in the management and conservation of species [
        <xref ref-type="bibr" rid="ref1">1</xref>
        ], and many
methods are used to make realtvie or absolute estimtes of population size Hunter harvest statistics are
often used as an estimate of the minimum number live which is an indirect measurement of population
size; however, this approach only concerns game species that are not protected, and game bags may
reflect hunters behaviour and tradition rather than changes in population size [
        <xref ref-type="bibr" rid="ref2 ref3 ref4">2, 3, 4</xref>
        ].
      </p>
      <p>
        Direct counting methods include ground-based transect surveys, faecal density counts, and images
from camera traps [
        <xref ref-type="bibr" rid="ref5">5, 6, 7, 8</xref>
        ]. These ground-based methods are time-consuming and can be subject
to biases, especially for game species. In person transects in daylight limit the detection of nocturnal
species and species with visual camouflage [ 9, 10], and thus to monitor nocturnal game species, e.g., red
deer (Cervus elaphus), nightly spotlight surveys are widely used [11, 12]. More recently, genotyping
faecal samples in a genetic mark-recapture framework has provided population size estimates that are
more accurate than hunter-harvest statistics [13] but are costly [14].
      </p>
      <p>In recent years, the use of drones in search and rescue operations has increased and have the promise
of being efective in wildlife monitoring. Drone technology combined with deep learning and image
processing techniques have made processing the large amount of data more eficient and efective.
However, there are also challenges such as legal restrictions and weather conditions. Continuous</p>
      <p>CEUR</p>
      <p>ceur-ws.org
development of these technologies enable drones to be used more efectively in search and rescue
operations [15] and in wildlife monitoring.</p>
    </sec>
    <sec id="sec-2">
      <title>2. Status of deer populations in Serbia and potential knowledge gaps</title>
      <p>Currently, data necessary to estimate red deer population abundance are either not recorded or are
not made available in a timely manner [16]. Data collected on hunting grounds in Serbia, as well as
other data collected and processed by the Statistical Ofice of the Republic of Serbia [ 17], are published
in two-year periodicals in the field of forestry, which does not meet the needs of modern hunting
management and sustainable use of wildlife populations. Improvements could be implemented to make
better use of this valuable data that has already been collected or could be collected with minimal
additional efort. For example, the current information system of the Statistical Ofice of the Republic of
Serbia [17] should enable all hunting ground users to directly enter data into a single database of the
statistical ofice. In addition, these data should be harmonized with other databases and data sources
in the field of hunting, such as the information system of the Hunting Association of Serbia and the
Ministry of agriculture. According to the oficial statistical data, the estimated number of red deer
populations in the spring of 2011 was about 4,200 individuals, and in the spring of 2019 about 6,300
individuals. However, the majority of assessment sheets do not contain information on the estimated
age of individuals, nor is it requested on datasheets (Form T-11, Evaluation Sheet, Figure 1). Adding
data on age class would allow better demographic estimations of populations to be made. Moreover,
trophy value (Form E-4, Figure 2) is not recorded (The International Council for Game and Wildlife
Conservation, “CIC” points) Changes to these forms would improve the amount of information about
harvested animals which in turn would lead to better estimates of population size. Game laws should
be adjusted to reflect this additional information for harvested animals.</p>
    </sec>
    <sec id="sec-3">
      <title>3. The current procedure of estimation of red deer population in</title>
    </sec>
    <sec id="sec-4">
      <title>Serbia</title>
      <p>Red deer are easier to count using visual surveys than roe deer because they have a diferent biological
rhythm and way of behaving in nature. Red deer spend most of the year in herds, and they separate
(individual movement) only during mating, while females are separated from the herd during calving.
Thus, during certain times of the year, animals congregate in readily visible herds. However, there
are numerous challenges when counting big game animals (red deer; fallow deer – Dama dama; roe
deer – Capreouls capreolus; european mouflon - Ovis aries musimon and wild boar – Sus scrofa) that
can lead to errors of 10, 20 and even 50% compared to the actual situation [18]. Precise estimates are
challenging because red deer have a relatively large radius of movement between the place where they
stay during the day and where they take food at night.</p>
      <p>To mitigate biases in population estimation, the counting procedure itself should be carefully planned,
considering that it is a complex process and requires teamwork with the coordination of a large number
of participants, i.e.”countersit is necessary to harmonize the methodologies for counting animals across
all hunting grounds. Surveys should also be randomly stratified among suitable red deer habitats and
given equal survey efort.</p>
      <p>ОЦЕЊИВАЧКИ ЛИСТ</p>
      <p>Јелен / Cervus elaphus L./
_____________________________________________________________
(Име и презиме ловца, место боравка, држава, регистарски број ловне карте)
Елементи оцењивања и лепоте роговља
/ Beaty Points /
Могући
бр. поена
Утврђени бр.</p>
      <p>поена
Ловиште:
Место звано:
Датум лова:
Елементи мерења и оцењивања</p>
      <p>/ Measurements /
Дужина роговља
/ Length of main beam /
Дужина надочњака
/ Length of brow tine /
Дужина средњака
/ Length of tray tine /
Обим венца (руже)
/ Circumference of coronet /
Обим између надочњака и средњака
/ Circumference of lower beam /
Обим између средњака и круне
/ Circumference of upper beam /
Тежина свежег роговља умањена за 10 % односно ______ кг. /
Weight
Распон роговља / Inside span
Број парожака на гранама роговља
/ Number of tine ends /
Збир поена од редног броја 1. до 9. / Score 1-9
Боја роговља
Искричавост роговља
Врхови (шиљци) парожака
Ледењаци
Круне
1.
2.
3.
4.
5.
6.
7.
8.
9.
Ред.
број
10.
11.
12.
13.
14.</p>
      <p>15.
Primedba :</p>
      <p>At the end, the organizer of the entire counting process at one hunting ground invites all the counters
or observers to jointly analyze the collected data and perform a recapitulation of the obtained figures or
aggregated data.</p>
      <p>From the described counting process, it is clear how demanding this activity is in every sense,
as regards the number of people, time consumption and ultimately costs. Counting is best or most
successfully done in the morning or early evening because that’s when the deer are most active, i.e. they
are looking for food, so they can be seen or observed more easily. Also, it is more successful to observe
deer in winter or early spring when there is less vegetative cover and animals are congregated in herds.
Days when meteorological conditions (temperature, pressure and air humidity) change suddenly are
not suitable for game counting, as deer consequently change their day/night rhythm with an uncertain
outcome in the future [18].</p>
      <p>After taking all the mentioned factors into account, the counting organizer should determine the
counting time and the direction of movement of the members of the counting team (usually 2 to 3
people in a group). As mentioned, observers should be placed at crossings (hunting towers, valleys,
embankments, watercourses, roads) that record the direction of movement, the number of animals and
the exact time (hour, minute) when it happened. In any case, they enter the data with all the details
(place of capture, all categories of deer) in the appropriate forms as well as possible remarks, such as
the joining of two groups from two directions.</p>
    </sec>
    <sec id="sec-5">
      <title>4. Red deer estimation in the Public Enterprise “Vojvodinasume”,</title>
    </sec>
    <sec id="sec-6">
      <title>Serbia</title>
      <p>Hunting grounds in Public Enterprise (PE) ‘Vojvodinasume’ have been established and set up on an
area of 108,988.00 ha. In this area, 17 hunting grounds have been established, set up and entrusted to
PE “Vojvodinasume” (Figure 3). Total area of enclosed hunting grounds is 25,552.00 ha or 23.50% of the
total area under hunting grounds established in PE “Vojvodinasume”. The red deer habitats in the area
managed by the PE Vojvodinasume are mainly the flat forest land, along the Sava and Danube rivers.</p>
      <p>PE “Vojvodinasume” is a business entity conducting activities in the sector of hunting. It owns
hunting grounds and game breeding farms with professional staf working on them. This makes it one
of the key actors in planning the development of the hunting sector both in the Province of Vojvodina
and the whole Republic of Serbia.</p>
      <p>Enclosed hunting grounds are used for intensive, modern methods of breeding two autochthonous
species (red deer and wild boar) and two allochthonous species (fallow deer and mouflon), generally
kept and bred together on the same enclosed site. Intensive production and breeding of large game is
intended mainly for foreign hunters-tourists (foreign market). However, over the past couple of years,
local hunters-tourists have also been taken into consideration (domestic market).</p>
      <p>Counting of red deer is done in the second half of March. To determine the estimated number of
individuals, a combination of several methods is used: the number of harvested animals, observation of
animals by game wardens from the tower, the presence of game footprints, camera traps, and counting
of animals by simultaneously passing several people through the hunting ground. The breeding stock
of red deer is evaluated by synthesis of all parameters. The final population size estimate refers to the
population post-hunting season but before calves are born. The use of camera traps in game counting
at PE Vojvodinasume is still relatively new and has not been validated.</p>
      <p>Red deer abundance I estimated on the 17 hunting grounds (divided into 5 organizational units),
(Figure 4). The majority of red deer habitat belongs to flat areas (105.805 ha) with only one in hilly or
mountainous habitats (4.118 ha). According to the map on Figure 3 and statistical data (Figure 4), the
largest number of red deer are located near the Danube river in the hunting grounds “Apatinski rit” (No
2) and “Kozara” (No 3) with total number of 1.734 animals, as well as “Deliblatska Peščara” (No 11) with
790 animals. The sum of these three hunting ground is 2.524 animals, which is more than two-thirds of
the red deer population on PE Vojvodinasume properties. If the fourth most productive hunting ground
in terms of the number of red deer (450 animals), which is the Bosutske Sume (No 13), is added , the
number of deer on those four hunting grounds on the banks of the Danube and Sava rivers, it follows
that this number (3974 animals) is more than four fiths of the red deer fund in PE Vojvodinasume.</p>
    </sec>
    <sec id="sec-7">
      <title>5. The experiences of other researchers</title>
      <p>Although there is not much research on the use of drones in deer population estimation, it appears that
there are numerous challenges and technical details that need to be solved.</p>
      <p>In their study in Germany, Zabel et al. [19] evaluated the accuracy of Unmanned Aerial Vehicles
(UAVs) and thermal infrared cameras in counting red deer populations. The study revealed that factors
such as season, flight altitude and temperature afect the accuracy of the UAV. These results suggest
that UAVs have the potential to provide accurate population counts, but it is important to consider
various factors.</p>
      <p>Larsen et al. [20] in their study in Denmark, investigated the use of a drone equipped with a thermal
camera for recognizing wild mammal species in open areas and determining the sex and age of red deer
(Cervus elaphus) and roe deer (Capreolus capreoulus), and these species could be distinguished from
one another and from cattle They described many details about characteristics used for recognising
species e.g. cattle and deer could be distinguished by their body shape. The width of the waist of
cattle was more than twice their hip and shoulder width, whereas deer had an almost identical waist,
shoulder, and hip width. Hence, deer looked more rectangular in shape than cattle in the thermal
videos. Red deer and roe deer were also visually diferent and could be distinguished by head and
antler shape. The snout of a red deer is relatively long compared to that of a roe deer. Furthermore,
the movements of red deer were perceptibly slower compared to those of roe deer. Another important
parameter for measuring the length of the mammals was the positioning of the individual. The standard
measurements of mammals include tail length and total length [21]. For accurate measurements hereof,
the individual should be standing and not lying curled up. More time spent recording individuals
increases the possibility of obtaining exact measures. One of the challenges in monitoring red and roe
deer is that they forage in the same areas, and therefore it is important to find ways to distinguish
between species of deer from thermal drone images. The group structure of roe deer difers throughout
the year. In the summer months, roe deer tend to live alone or in family groups, while in autumn and
winter, they gather in groups of up to 60–70 individuals [22]. In this study, however, red deer and
roe deer could be distinguished from each other by their very diferent body sizes, head forms and
movement speeds. With suficient data, the shapes of the heads could be measured and analyzed to show
if there is a significant diference in the head shape between red deer and roe deer. In autumn, when
the study was conducted, roe deer still moved around in small groups on the moor (13 km2), Lyngby
Hede, managed by The Danish Nature Agency and the antlers of the stags were easily recognized by
the thermal camera.</p>
      <p>At other times of the year, when antlers are not present, it is not possible to diferentiate between
male and female red deer [23]. Jarnemo et al. [24] found that female and male red deer are normally
sexually segregated outside of the rut. When the rutting season begins in early September, the male red
deer form large harems and the elder stags can be recognized by their roaring, fights, and urination,
while the hinds can be determined by whether or not they nurse a calf. However, a young male deer
without antlers or with smaller antlers may be confused with a hind due to its size, and because young
males sometimes stay with the herd [25].</p>
    </sec>
    <sec id="sec-8">
      <title>6. Conclusion and future challenges to be addressed in Serbia</title>
      <p>According to previous reports, it has been demonstrated that UAV-based thermal imaging surveys can
ofer a non-invasive but potentially very accurate and precise surveying approach to estimate red deer
population numbers, sex ratios and possibly breeding success in northern Europe. Unfortunately, there
are no reports about the use of UAVs for red deer in South East Europe. Therefore, future research
activities for the most accurate counts of stags should include flights in early summer, corresponding to
when vegetation growth is still reduced and antler growth is developed. Additionally, camera traps
and other methodsshould be used to validate the data obtained on the number of game species by UAV.
The application of this method to large, free-ranging populations of red deer in West Balkan countries
needs to be validated , and hunting managers would need to consider aspects such as sampling design,
species identification, counting biases and also cost implications. UAVs technology should be tested in
the West Balkans and a first stept would be drafting a guide for the estimation of red deer population
density with detailed instructions. All these activities require time, persistence and of course the unity
of all stakeholders, which currently is not easy to manage.</p>
      <p>The diverse geographical areas of red deer habitats in PE Vojvodinasume should be kept in mind
[19, 20]. Generally, the average elevation in Province Vojvodina is 110 m, with minimum elevation of 66
m and where the Gudurica peak on the Vršac Mountains, is the highest peak in Vojvodina, at an altitude
of 641 m above sea level. But the main challenge for use of UAV is how to see, recognise and record red
deer animals through the dense tree tops (mainly penduculate oak forests as well as black poplar and
willow varieties) on the banks of Danube and Sava rivers. In order to solve these problem, we would
plan to count game during the vegetation period when the leaves fall from the trees, that is, during the
period of the first frosts (from beginning of November) until the end of March of the following year.
UAV pilot studies should coincide with the prescribed terms for counting game in March.</p>
    </sec>
    <sec id="sec-9">
      <title>Acknowledgments References</title>
      <p>This research was funded by the Ministry of Education, Science and Technological development of
Serbia on the basis of the contracts for the realization and financing of scientific research work in 2024
(The Contract No. 451-03-65/2024-03/ 200117).
[6] P. Aubry, D. Pontier, J. Aubineau, F. Berger, Y. Léonard, B. Mauvy, S. Marchandeau, Monitoring
population size of mammals using a spotlight-count-based abundance index: How to relate the
number of counts to the precision?, Ecological indicators 18 (2012) 599–607.
[7] F. P. Princee, Exploring studbooks for wildlife management and conservation, volume 17, Springer,
2016.
[8] Z. J. Delisle, E. A. Flaherty, M. R. Nobbe, C. M. Wzientek, R. K. Swihart, Next-generation camera
trapping: systematic review of historic trends suggests keys to expanded research applications in
ecology and conservation, Frontiers in Ecology and Evolution 9 (2021) 617996.
[9] B. Ingberman, R. Fusco-Costa, E. L. de Araujo Monteiro-Filho, Population survey and demographic
features of a coastal island population of alouatta clamitans in atlantic forest, southeastern brazil,
International journal of primatology 30 (2009) 1–14.
[10] R. Kays, J. Sheppard, K. Mclean, C. Welch, C. Paunescu, V. Wang, G. Kravit, M. Crofoot, Hot monkey,
cold reality: surveying rainforest canopy mammals using drone-mounted thermal infrared sensors,
International journal of remote sensing 40 (2019) 407–419.
[11] M. Garel, C. Bonenfant, J.-L. Hamann, F. Klein, J.-M. Gaillard, Are abundance indices derived from
spotlight counts reliable to monitor red deer cervus elaphus populations?, Wildlife Biology 16
(2010) 77–84.
[12] L. Corlatti, A. Gugiatti, L. Pedrotti, Spring spotlight counts provide reliable indices to track
changes in population size of mountain-dwelling red deer cervus elaphus, Wildlife Biology 22
(2016) 268–276.
[13] C. Ebert, J. Sandrini, B. Welter, B. Thiele, U. Hohmann, Estimating red deer (cervus elaphus)
population size based on non-invasive genetic sampling, European Journal of Wildlife Research
67 (2021) 27.
[14] S. P. Davis, Evaluating the use of drones to estimate deer density and count wildlife trails in bath
nature preserve, Ohio, Master’s thesis, University of Akron, 2021.
[15] S. M. S. M. Daud, M. Y. P. M. Yusof, C. C. Heo, L. S. Khoo, M. K. C. Singh, M. S. Mahmood,
H. Nawawi, Applications of drone in disaster management: A scoping review, Science &amp; Justice
62 (2022) 30–42.
[16] S. Mladenović, Sistem monitoringa populacija jelenske divljači u Srbiji, Ph.D. thesis, University of</p>
      <p>Belgrad, 2022.
[17] Statistical Ofice of the Republic of Serbia, Bulletin forestry in the republic of serbia, belgrade, no.</p>
      <p>660 (2024).
[18] R. Z., Hunting for 3rd and 4th grade forestry school (in Serbian), Institute for textbook publishing
and teaching aids, 2006.
[19] F. Zabel, M. A. Findlay, P. J. White, Assessment of the accuracy of counting large ungulate species
(red deer cervus elaphus) with uav-mounted thermal infrared cameras during night flights, Wildlife
Biology 2023 (2023) e01071.
[20] H. L. Larsen, K. Møller-Lassesen, E. M. E. Enevoldsen, S. B. Madsen, M. T. Obsen, P. Povlsen,
D. Bruhn, C. Pertoldi, S. Pagh, Drone with mounted thermal infrared cameras for monitoring
terrestrial mammals, Drones 7 (2023) 680.
[21] W. Ansell, Standardisation of field data on mammals, African Zoology 1 (1965) 97–113.
[22] W. Bresiński, Grouping tendencies in roe deer under agrocenosis conditions, Acta theriologica 27
(1982) 427–447.
[23] T. Y. Ito, A. Miyazaki, L. A. Koyama, K. Kamada, D. Nagamatsu, Antler detection from the sky:
deer sex ratio monitoring using drone-mounted thermal infrared sensors, Wildlife Biology 2022
(2022) e01034.
[24] A. Jarnemo, G. Jansson, J. Månsson, Temporal variations in activity patterns during rut–
implications for survey techniques of red deer, cervus elaphus, Wildlife Research 44 (2017)
106–113.
[25] E. Bennitt, H. L. Bartlam-Brooks, T. Y. Hubel, A. M. Wilson, Terrestrial mammalian wildlife
responses to unmanned aerial systems approaches, Scientific reports 9 (2019) 2142.</p>
    </sec>
  </body>
  <back>
    <ref-list>
      <ref id="ref1">
        <mixed-citation>
          [1]
          <string-name>
            <given-names>J. P.</given-names>
            <surname>Jones</surname>
          </string-name>
          ,
          <string-name>
            <given-names>G. P.</given-names>
            <surname>Asner</surname>
          </string-name>
          ,
          <string-name>
            <given-names>S. H.</given-names>
            <surname>Butchart</surname>
          </string-name>
          , K. U. Karanth, The 'why',
          <article-title>'what'and 'how'of monitoring for conservation, Key topics in conservation biology 2 (</article-title>
          <year>2013</year>
          )
          <fpage>327</fpage>
          -
          <lpage>343</lpage>
          .
        </mixed-citation>
      </ref>
      <ref id="ref2">
        <mixed-citation>
          [2]
          <string-name>
            <given-names>C.</given-names>
            <surname>Mitchell</surname>
          </string-name>
          ,
          <string-name>
            <given-names>A. D.</given-names>
            <surname>Fox</surname>
          </string-name>
          ,
          <string-name>
            <given-names>J.</given-names>
            <surname>Harradine</surname>
          </string-name>
          ,
          <string-name>
            <surname>I. Clausager</surname>
          </string-name>
          ,
          <article-title>Measures of annual breeding success amongst eurasian wigeon anas penelope</article-title>
          ,
          <source>Bird Study</source>
          <volume>55</volume>
          (
          <year>2008</year>
          )
          <fpage>43</fpage>
          -
          <lpage>51</lpage>
          .
        </mixed-citation>
      </ref>
      <ref id="ref3">
        <mixed-citation>
          [3]
          <string-name>
            <given-names>J.</given-names>
            <surname>Kahlert</surname>
          </string-name>
          ,
          <string-name>
            <given-names>A. D.</given-names>
            <surname>Fox</surname>
          </string-name>
          ,
          <string-name>
            <given-names>H.</given-names>
            <surname>Heldbjerg</surname>
          </string-name>
          ,
          <string-name>
            <given-names>T.</given-names>
            <surname>Asferg</surname>
          </string-name>
          ,
          <string-name>
            <given-names>P.</given-names>
            <surname>Sunde</surname>
          </string-name>
          ,
          <article-title>Functional responses of human hunters to their prey-why harvest statistics may not always reflect changes in prey population abundance</article-title>
          ,
          <source>Wildlife biology 21</source>
          (
          <year>2015</year>
          )
          <fpage>294</fpage>
          -
          <lpage>302</lpage>
          .
        </mixed-citation>
      </ref>
      <ref id="ref4">
        <mixed-citation>
          [4]
          <string-name>
            <given-names>T.</given-names>
            <surname>Christensen</surname>
          </string-name>
          , L. Haugaard,
          <article-title>DÅvildt i danmark - status for bestand og udbytte 2017</article-title>
          , https: //dce.au.dk/fileadmin/dce.au.dk/Udgivelser/Notater_2017/
          <article-title>DAAVILDT_I_DANMARK</article-title>
          .pdf,
          <year>2017</year>
          .
        </mixed-citation>
      </ref>
      <ref id="ref5">
        <mixed-citation>
          [5]
          <string-name>
            <given-names>C. C.</given-names>
            <surname>Webbon</surname>
          </string-name>
          ,
          <string-name>
            <given-names>P. J.</given-names>
            <surname>Baker</surname>
          </string-name>
          ,
          <string-name>
            <given-names>S.</given-names>
            <surname>Harris</surname>
          </string-name>
          ,
          <article-title>Faecal density counts for monitoring changes in red fox numbers in rural britain</article-title>
          ,
          <source>Journal of Applied Ecology</source>
          <volume>41</volume>
          (
          <year>2004</year>
          )
          <fpage>768</fpage>
          -
          <lpage>779</lpage>
          .
        </mixed-citation>
      </ref>
    </ref-list>
  </back>
</article>