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Changes of Martes species numbers in the Middle Urals over 20 years

Authors:
  • Institute of Plant and Animal Ecology

Abstract

In our opinion, the relationship between hunting pressure and the abundance of marten and sables is undeniable. However, such a strong and sharp increase in marten and sable numbers may be explained by global warming too. This may explain the continuing growth of the marten population in the southern region
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CONTENTS'
FROM'THE'CHAIR'...................................................................................................................................................................'2!
FROM'THE'TREASURER'AND'MEMBERSHIP'DIRECTOR'............................................................................................'4!
FROM'THE'WEBMASTER'......................................................................................................................................................'5!
PUBLICATION'OF'THE'5TH'MARTES'SYMPOSIUM'BOOK'............................................................................................'7!
WESTERN'NORTH'AMERICA'...............................................................................................................................................'9!
LIMITING!FACTORS!AND!LANDSCAPE!CONNECTIVITY:!THE!AMERICAN!MARTEN!IN!THE!ROCKY!MOUNTAINS!................................!9!
SECONDYEAR!TRANSLOCATION!OF!FISHERS!INTO!THE!NORTHERN!SIERRA!NEVADA!AND!SOUTHERN!CASCADES!OF!
CALIFORNIA!.................................................................................................................................................................................................!10!
DECLINE!IN!AMERICAN!MARTEN!OCCUPANCY!RATES!AT!SAGEHEN!EXPERIMENTAL!FOREST,!CALIFORNIA!.................................!13!
USE!OF!NONINVASIVE!GENETIC!DATA!TO!ESTIMATE!FISHER!POPULATION!PARAMETERS!IN!THE!EASTERN!KLAMATH!
MOUNTAINS!OF!CALIFORNIA!.....................................................................................................................................................................!16!
SIMULATING!THE!EFFECTS!OF!CLIMATE!CHANGE!ON!POPULATION!CONNECTIVITY!OF!AMERICAN!MARTEN!IN!THE!NORTHERN!
ROCKY!MOUNTAINS,!USA!.........................................................................................................................................................................!21!
EASTERN'NORTH'AMERICA'..............................................................................................................................................'22!
MODELING!HABITAT!QUALITY!FOR!AMERICAN!MARTENS!IN!WESTERN!NEWFOUNDLAND,!CANADA!............................................!22!
MULTISCALAR!EFFECTS!OF!FOREST!FRAGMENTATION!BY!TIMBER!HARVESTING!ON!AMERICAN!MARTEN!IN!THE!BOREAL!FOREST!
OF!EASTERN!CANADA!.................................................................................................................................................................................!23!
DISTRIBUTION!AND!DETECTION!RATES!OF!A!REINTRODUCED!FISHER!POPULATION!IN!WESTERN!MARYLAND!............................!25!
POPULATION!ECOLOGY!OF!AMERICAN!MARTEN:!IMPACT!OF!WIND!FARM!DEVELOPMENT!IN!HIGHELEVATION!SPRUCEFIR!
HABITAT!IN!NEW!HAMPSHIRE!..................................................................................................................................................................!28!
EUROPE'...................................................................................................................................................................................'33!
TEETH!VARIATIONS!AND!PATHOLOGIES!IN!STONE!MARTENS!FROM!CROATIA!...................................................................................!33!
PINE!MARTEN!ABUNDANCE!AND!POTENTIAL!IMPACTS!OF!HABITAT!FRAGMENTATION!IN!NORTHERN!IRELAND‐A!CASE!STUDY!
IN!THE!MOURNE!MOUNTAINS!...................................................................................................................................................................!34!
RESEARCH!OF!GENETIC!VARIABILITY!OF!BEECH!MARTEN!FROM!CROATIA!.........................................................................................!35!
RUSSIA'.....................................................................................................................................................................................'37!
CHANGES!OF!MARTES!SPECIES!NUMBERS!IN!THE!MIDDLE!URALS!OVER!20!YEARS!..........................................................................!37!
SABLE!AND!MARTEN!POPULATION!INCREASE:!IS!IT!POSSIBLE!TO!RAISE!GAME!QUOTAS?!................................................................!41!
ASIA'..........................................................................................................................................................................................'42!
DIET!OF!AN!OPPORTUNISTICALLY!FRUGIVOROUS!CARNIVORE,!MARTES'FLAVIGULA,!IN!SUBTROPICAL!FOREST!............................!42!
FRUGIVORY!AND!SEED!DISPERSAL!BY!THE!YELLOWTHROATED!MARTEN,!MARTES'FLAVIGULA,!IN!A!SUBTROPICAL!FOREST!OF!
CHINA!............................................................................................................................................................................................................!43!
HELP'WANTED'.....................................................................................................................................................................'44!
REQUEST!FOR!COLLABORATION:!CRANIAL!MORPHOLOGY!IN!AMERICAN!AND!EURASIAN!MARTES!...............................................!44!
EASTERN!NORTH!AMERICA!REGIONAL!REPRESENTATIVE!NEEDED!..................................................................................................!45!
NEW'BOOK'ANNOUNCEMENT'..........................................................................................................................................'45!
NORTHERN'FURBEARER'CONFERENCE'PROCEEDINGS'AVAILABLE'..................................................................'46!
RECENT'MARTES'LITERATURE'.......................................................................................................................................'47!
!
NEWSLETTER'
Volume!18(1)!·!2011!
'
Martes!Working!Group!Newsletter!18(1)!
37!
Sindičić,!M.,!T.!Gomerčić,!D.!Kos,!D.!Dežđek,!D.!Konjević,!T.!Keros,!and!A.!Slavica.!2011.!
Variability!of!mitochondrial!DNA!in!beech!marten!(Martes'foina)!from!central!Croatia.!
Abstract!Volume!VIth!European!Congress!of!Mammalogy,!Pariz,!Francuska.!P.!71.!
!
!
RUSSIA'
!
Changes'of'Martes'species'numbers'in'the'Middle'Urals'over'20'years'
!
Vladimir'Monakhov'
Institute!of!Plant!and!Animal!Ecology,!!
Ural!Division!of!Russian!Academy!of!Sciences!
8!Marta!St.,!202,!Ekaterinburg,!Russia,!620144!
Email:!mon@ipae.uran.ru!
!
Pine!martens!(Martes'martes)!occur!throughout!the!Ural! Mountains!region,!but!sables!(M.'
zibellina)! occur! only! in! the! northeast! (Monakhov! 2005).! Winter! transect! counts,! held!
regularly! in! February! and! March,! are! used! to! estimate! the! number! of! pine! martens! and!
sables! living! in! the! Ural! Mountains! jointly.! The! Department! of! the! Sverdlovsk! region!
gathers!these!data!to!facilitate!the! protection,!control!and!regulation!of!wildlife!use.! From!
the!annual! estimates,!multi‐year! averages!of! abundance!for! the!periods! 1987!–!1991!and!
2005!–!2011!were!calculated!for!all!47!municipal!areas.!
!
The!territory!of!the!Sverdlovsk!region!is! intersected!by!the! Ural!Mountains!from!north! to!
south.! For! this! reason,! habitats! of! commercial! (harvested)! species! are! very! diverse.!
According!to! our!research! (Monakhov!et'al.! 1997),!the! region!supports! 3!natural‐hunting!
Zones,!which!include!6!game‐economy!counties!(Figure!1A):!
The!To‐Urals!Zone!(prior!to!Urals,!PU)!includes!a!county!with!the!same!title.!
The! Urals! Zone! (Ural! Mountains,! U)! is! divided! into! 3! counties:! North‐Urals! (U1),!
middle‐taiga‐mountainous!(U2),!and!Middle!Urals!(U3).!
The!Trans‐Ural!range!of!the!region!is!called!the!Western!Siberian!Zone!(WS).!It!also!
encompasses! 3! counties:! plain! middle‐taiga! (WS1),! southern! taiga! (WS2),! and!
forest‐steppe!(WS3).!
!
Analysis!of!data!on!the!number!of!Martes,!in!combination!with!the!natural‐hunting!zoning,!
reveals!regular!features!in!the!dynamics!of!species!resources.!In!addition,!this!information!
allows!us!to!evaluate!the!priority!causes!and!factors!of!these!changes.!
!
The!number!of!sables!has!increased!significantly!in!the!past!20!years!throughout!the!region!
(Table! 1,! Figure! 1).! The! increase! in! the! different! counties! ranges! from! 1.6! to! 3.02! times!
(average!2.7)!(Table!1).!
!
The!data!on!pine!marten!are!even!more!impressive!(Table!1,!Figure!2).!In!1987!–!1991,!the!
number!of!pine!martens!exceeded!1,000!only!in!1!county!(WS2),!but!did!not!exceed!500!in!
4!counties! (PU,!U1,! U3,! and!WS3).! After!20! years,! WS2!county! supports!more! than!3,000!
Martes!Working!Group!Newsletter!18(1)!
38!
pine!martens,!and!an!additional!4!counties!(U2,!U3,!WS1,!and!WS3)!now!support!more!than!
1,000! martens.! For! the! remaining! 2! counties! (PU! and! U1),! the! minimum! number! is! now!
500! martens.! The! average! increase! in! the! number! of! martens! in! the! region! is! about! 2.9!
times!(Table!1).!The!minimum!increase!among!the!individual!counties!was!2.3!times!(PU1),!
and!the!maximum!increase!was!8.4!times!(WS3).!!In!2!other!southern!counties!(U2!and!U3),!
the!number!increased!by!3.3!and!4.4!times,!respectively.!
!
N.S.! Korytin! (2011)! documented! similar! changes! in! the! number! of! Uralian! Martes.! He!
attributed!these!changes!to!anthropogenic!causes.!Hunting!pressure!limited!the!number!of!
martens! and! sables! in! the! 1980! –! 1990! period.! When! this! pressure! was! removed! in! the!
2000s,!marten!and!sable!abundances!increased.!
!
In!our! opinion,! the! relationship! between! hunting! pressure!and! the! abundance! of! marten!
and!sables!is! undeniable.!However,!such! a!strong!and!sharp!increase!in!marten! and!sable!
numbers!may!be!explained!by!global!warming!too.!This!may!explain!the!continuing!growth!
of!the!marten!population!in!the!southern!region!of!3.3!–!8.4!times!(Table!1,!Figure!2).!
!
Data!indicate!that!warming!is!occurring!in!the!Urals!(an!increase!over!the!past!30!years!of!
1.5!–!2°C)!and!in!Russia!in!general!(1!–!1.5°C).!Also,!forests!have!expanded!northward.!This!
forest!expansion!is! enhanced!by! the!overgrowth! of!unused!agricultural! lands.!As! a!result,!
some!migratory!birds!are! wintering!in!the! Urals.!In!addition,!the! migration!paths!of!birds!
are!changing:!
http://www.gazeta.ru/news/science/2008/12/15/n_1308432.shtml!
http://www.svgimet.ru/index.php?page=about&pid=100101!
http://ural.ria.ru/science/20061215/81526135.html!
!
In! the! Urals,! the! greatest! sable! population! growth! occurred! in! commonly! used! habitats!
(district! SW1,! by! 3! times).! However,! there! is! evidence! that! sable! population! growth! is!
occurring! in! other! western! parts! of! its! range! (Korytin! 2011).! In! addition,! the! sable! has!
begun! appearing! in! areas! where! it! has! previously! been! rare! (e.g.,! in! the! U2! and! SW3!
counties,!Monakhov!2010).!
!!
If!we!look!at!the!abundance!of!Mustela!species,!we!obtain!a!very!different!picture!(Table!1).!
On! average,! in! all! districts,! Siberian! weasels! (Mustela' sibirica)! and! ermines! (Mustela'
erminea)! have! decreased! by! 53%! (range! 34! –! 128%),! and! 41%! (range! 16! –! 80%),!
respectively.!We! believe!that! these!declines! are!due! to!habitat! reduction!(overgrowing! of!
fields,!meadows!and!edges! by!deciduous!and!coniferous! young!forest),!and! an!increase!in!
other!predator!populations,! including! pine! marten! and! sable.! With!the! increase! in! forest!
cover!due!to!uncultivated!agricultural!land!more!habitat!may!be!created!for!sable!and!pine!
marten!in!the!near!future.!
!
This!work!was!supported!by!RFBR,!project!10‐04‐96063.!
!
' '
Martes!Working!Group!Newsletter!18(1)!
39!
References'
Korytin,!N.S.!2011.!Changes!in!the!numbers!of!predatory!mammals!in!the!Middle!Urals!
caused!by!anthropogenic!factors.!Russian!Journal!of!Ecology!42(3):!231–235.!
!
Monakhov,!V.G.!2005.!Über!den!gegenwärtigen!Zustand!der!Populationen!von!Arten!der!
Gattung!Martes!in!der!Transgressionszone!der!Areale!im!Mittelural.!Beitraege!zur!Jagd‐!und!
Wildforschung!30:!331‐335.!
!
Monakhov,!V.G.!2010.!Records!of!sable!outside!its!range!in!southern!Sverdlovsk!region!in!
winter!of!2009–2010.!Zoologicheskii!Zhurnal!89:1394–1397!(in!Russian!with!English!
summary).!
!
Monakhov!V.G.,!Yu.A.!Kuzminikh,!and!S.P.!Trushin.!1997.!On!the!game‐natural!area!zoning!
of!Svepdlovsk!province.!Pp.!129‐130!in!G.A.!Selitsky!and!Yu.G.!Yaroshenko,!eds.!Problems!of!
outside!ambient!conservation!in!the!Urals!region.!Ekaterinburg.!!
!
!
Table'1.!Multi‐year!averages!of!Martes!and!Mustela!species!abundances!in!the!Middle!Urals!
over!the!last!20!years.!
!
County
Years
Sable
Siberian
weasel
Ermine
PU
1987-1991
176
310
2005-2011
68
50
Variation (%)
39
16
U1
1987-1991
21
71
1006
2005-2011
34
91
804
Variation (%)
163
128
80
U2
1987-1991
800
2314
2005-2011
528
1053
66
46
U3
1987-1991
505
862
2005-2011
273
369
Variation (%)
54
43
WS1
1987-1991
1718
2342
7862
2005-2011
5181
1672
3244
Variation (%)
302
71
41
WS2
1987-1991
664
4467
6624
2005-2011
1281
1840
2318
Variation (%)
193
41
35
WS3
1987-1991
1091
897
2005-2011
371
276
Variation (%)
34
31
!
!
Martes!Working!Group!Newsletter!18(1)!
40!
!
Figure'1.!Changes!of!sable!numbers!in!the!Sverdlovsk!region!from!1987!–!1991!(A,!left)!to!
2005!–!2011!(B,!right).!Designations!of!zones!and!districts!in!the!text.!
!
!
!
Figure'2.!Changes!of!pine!marten!numbers!in!Sverdlovsk!region!from!1987!–!1991!(A,!left)!
to!2005!–!2011!(B,!right).!Designations!as!in!Figure!1.!
... In China, it is distributed in Northern Xinjiang and Northeast China (Monakhov, 2001b(Monakhov, , 2005Proulx et al., 2005). Due to commercial hunting and deforestation, the sable population has decreased dramatically in Northeast China since the l950s (1950-1959Kashtanov et al., 2015;Monakhov, 2005Monakhov, , 2011a and there is an increasing need for its conservation. ...
... Sables may be affected by human influences (Monakhov, 2001a(Monakhov, , 2001b(Monakhov, , 2011a(Monakhov, , 2011bZhou et al., 2011), but the historical data of human activities (e.g., land cover, vegetation cover from the 1950s) are difficult to be compiled. The change of human population size can reflect the scale of urbanization, the deforestation, and the reclamation of farmland. ...
... It is important to quantify distribution change spatial patterns to gain a better understanding of threatening factors (Luo et al., 2015;Pacifici et al., 2015;Urban, Zarnetske, & Skelly, 2013). The predicted ranges for each period were determined as the total number of respective re- Human influence and climate are likely to be important factors affecting sable distribution (Kashtanov et al., 2015;Miyoshi & Higashi, 2004;Monakhov, 2001bMonakhov, , 2005Monakhov, , 2011a ...
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Understanding historical context can help clarify the ecological and biogeographic characteristics of species population changes. The sable (Martes zibellina) population has decreased dramatically in Northeast China since the l950s, and understanding the changes in its distribution over time is necessary to support conservation efforts. To achieve this goal, we integrated ecological niche modeling and historical records of sables to estimate the magnitude of change in their distribution over time. Our results revealed a 51.71% reduction in their distribution in 2000–2016 compared with the potential distribution in the 1950s. This reduction was related to climate change (Pearson's correlation: Bio1, −.962, p < .01; Bio2, −.962, p < .01; Bio5, .817, p < .05; Bio6, .847, p < .05) and human population size (−.956, p < .01). The sable population tended to migrate in different directions and elevations over time in different areas due to climate change: In the Greater Khingan Mountains, they moved northward and to lower elevations; in the Lesser Khingan Mountains, they moved northward; and in the Changbai Mountains, they move southward and to higher elevations. Active conservation strategies should be considered in locations where sable populations have migrated or may migrate to.
... Here the western part of the sable's geographic range and the eastern part of the pine marten's geographic range overlap. In recent years, a multiple increase in marten and sable numbers has been observed for all natural hunting areas and districts of the Middle Urals (Korytin 2011, Monakhov 2011). We consider a significant reduction in hunting removal to be the most probable factor, and concomitant is global warming and loading decrease on agricultural lands. ...
... Here we analyze population data for spring 2013 for these 2 species of Martes provided by the Department of Natural Resources of the Sverdlovsk province. To describe the distributions of these species, we use the natural‐hunting zoning scheme based on game‐ economy counties (GEC), as described previously (Monakhov 2011).When we estimate the number of sable dwelling within the region, we observe that the species' geographic range has not changed. As described previously, sables occupy the northeast part of the Sverdlovsk province (Fig. 1). ...
... For comparison, the average density of pine marten within this occupied area is 1.02 per 1000 ha (Fig. 2). The highest pine marten population densities (2.1 – 2.45 per 1000 ha) were observed in these 5 districts of the Sverdlovsk province: the Artinskii, Krasno‐Turinskii, and Kirovgradskii municipal districts (MDs) of Ural Mountain zone U (Monakhov 2011); the Slobodo‐Turinskii MD on the East of southern taiga WS2 GEC; and the Pyshminskii MD in forest‐steppe WS3 GEC (Fig. 2). However, the maximum pine marten density of about 6 per 1000 ha was observed in the Kamyshlov MD of forest‐steppe WS3 GEC in the SE of Sverdlovsk province. ...
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Contemporary status of sable and European pine marten resources in Mid-Urals Region
... Low fur prices also may reduce number of individuals trapped (Abramov et al. 2016). In the Sverdlovsk Oblast, Russia, M. sibirica experienced a 39-71% decline in total population abundance from 1987 to 2011 (Monakhov 2011a). ...
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... (данные предоставлены Департаментом по охране, контролю и регулированию использования животного мира Свердловской обл.). Выявлены многолетние тренды численности за последние три десятилетия, а также оценены основные факторы, определяющие их численность и распространение в регионе (Monakhov, 2011(Monakhov, , 2011a(Monakhov, , 2012. Показано, что численность соболя за последние 20 лет существенно возросла на всей заселенной им территории области. ...
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... По поводу причин случаев добычи соболей в не свойственных виду районах, мы придерживаемся объяснения, данного в нашем сообщении (Монахов, 2010). Мы считаем, что забеги (а речь в данном случае может идти только о них, посколь-ку постоянного очага обитания вида здесь нет) за пределы видового ареала вызваны значительным увеличением численности соболей в последние 10 лет, на что указывалось ранее (Корытин, 2011;Монахов, 2012;Monakhov, 2011). В качестве возможных причин роста ресурсов вида авторами назывались такие, как уменьшение промыслового пресса, глобальное потепление климата, образование новых лесов на неиспользуемых сельскохозяйственных землях. ...
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... Была предложена усовершенствованная по сравнению с описанной В.В. Рожновым с соавторами [2008] [Monakhov, 2011a[Monakhov, , 2011b[Monakhov, , 2012. Проведены экспедиционные работы в районах Свердловской области: Сысертском, Шалинском, Артемовском, Кировградском, Режевском и МО Екатеринбург с обследованием 28 рек и речек для оценки распространения околоводных хищников с предполагаемым обитанием европейской норки Mustela lutreola Linnaeus 1761 (табл. ...
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On the game-natural area zoning of Svepdlovsk province
  • V G Monakhov
  • . A Yu
  • S P Kuzminikh
  • Trushin
Monakhov V.G., Yu.A. Kuzminikh, and S.P. Trushin. 1997. On the game-natural area zoning of Svepdlovsk province. Pp. 129-130 in G.A. Selitsky and Yu.G. Yaroshenko, eds. Problems of outside ambient conservation in the Urals region. Ekaterinburg.