Grouse and game dynamics. Pekka Helle Natural Resources Institute Finland Oulu

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Grouse and game dynamics Pekka Helle Natural Resources Institute Finland Oulu pekka.helle@luke.fi

- MTT Agrifood Research Finland - Finnish Forest Research Institute Metla - Finnish Game and Fisheries Research Institute RKTL - Information Centre of the Ministry of Agriculture and Forestry Tike From 1 January 2015: Natural Resources Institute Finland Luonnonvarakeskus Luke Turnover 140 EUR milj. Person-years approx.1700 Locations 38 The 2nd largest research institute in Finland 17.2.2015 2

Hares 2 species Fur-bearing animals 11 Moose and other artiodactylus 7 Large predators and seals 4 Waterfowl 16 Grouse (tetraonid birds) 5 Farmland game birds 3 Coots and waders 2

Hares 254 000 Fur-bearing animals 290 000 Number of bagged in 2013 Moose and other artiodactylus 83 000 Large predators and seals 1 400 Waterfowl 450 000 Grouse 495 000 Farmland game birds 240 000 Coots and waders 5 500

Value of bagged animals, 1000 (2013) Moose 47 140 (53%) Other mammals 22 660 Birds 18 400 Total 88 200 (reindeer husbandry 52 500) Recreational value?

No. of hunters in Finland Female percentage 5.8 (2011)

Ministry of agriculture & forestry EU Luke Hunters Finnish Wildlife Agency

Monitoring methods include: line transect counts (ground, aerial), territory mapping, study plot method, voice counts, pellet counts, nest counts, colony counts, DNA-sampling (non-invasive method for some species), capture-recapture method, radio/satellite telemetry, etc. Statistical principles/tools - total counts seldom possible - random sampling if possible - stratified sampling (random/systematic e.g. program DISTANCE for line transect data), TRIM (Trends and indices in monitoring data) etc. - Bayes-based methods coming The very problem: - Voluntary people do the dirty work! - They cannot be forced too much!

Game sustainable hunting Monitoring of: Moose Wild forest reindeer Baltic seals Large predators Field game Waterfowl Some individual species (e.g. beaver) Forest mammals WILDLIFE TRIANGLE Grouse SCHEME ca 35 species

Moose hunting clubs (6000) reports No. of moose observations per day

Two sub-populations Aerial counts with helicopter

Baltic seals Aerial counts Two species: ringed seal and grey seal (international effort)

Hylkeiden lukumäärä 16000 Grey seal 14000 12000 10000 Suomi Finland 8000 Ruotsi Sweden 6000 muut Other Balti 4000 2000 0 1980 1985 1990 1995 2000 2005 2010

Lynx MMain method for large predators: Network of trained local (1700) About 60 000 observations yearly (Tassu)

GAME IN AGRICULTURAL AREAS (line transects) (South and Western coastal areas)!!!!!

FOREST GAME WILDLIFE TRIANGLE SCHEME 4 + 4 + 4 = 12 km As randomly as possible in forested areas

1700 wildlife triangles 770 760 750 Good coverage nationwide Most of them established in Lapland Highest density in Kainuu province 740 730 720 710 700 690 680 670 20 30 40 50 60 70

Late-summer census 3-man line transect: main belt 60 m in breadth August prime time for counting grouse, broods still together Census efficiency high, 80% on average

Winter count in January-March Usually by skiing Main target: mammal tracks crossing the line Standardization: pre-check of the line or count done after a good snow-fall

Species covered in winter: Mountain hare European hare Red squirrel Thank Flying you squirrel Beaver Muskrat Wolf Red fox Arctic fox Raccoon dog Brown bear Stoat Weasel American mink Polecat Pine marten Wolverine Badger Otter Lynx Wild boar White-tailed deer Moose Wild forest reindeer Roe deer Capercaillie Black grouse Hazel grouse Willow grouse Partridge Pheasant Goshawk Raven

Parameters August count: Grouse, density of individuals density of adults density of juveniles brood size hen with or without brood (capercaillie, black grouse) Winter count: Track density number of crossings per 24 h per 10 km

Pine marten in 2014

Capercaillie

Capercaillie Black grouse Hazel grouse

Wildlife triangles: playing with large numbers During 1988 2014, about 45 000 counts performed (24 000 in late-summer, 21 000 in winter) Total length covered more than 500 000 km 850 000 working hours done, roughly 420 person years About 330 000 grouse individuals observed Snow tracks of mountain hare, moose and red fox most abundant. Their total numbers are 640 000, 190 000 and 170 000, respectively.

Linear trends 1989--2014 Roe deer Wolf Wild forest reindeer Wolverine Lynx European hare White-tailed deer Otter Moose Pine marten Red fox Red squirrel Least weasel Mountain hare!!! Stoat 1989 2014

Value of voluntary work done by hunters and bird-watchers in game monitoring programs estimated in 2008 based on an questionnaire - Large predator observer network 40 person work years - moose (observation cards) 28 pwy - wildlife triangle counts 20 pwy - counts of waterfowl and species of agricultural land less work intensive Value of work about 1 200 000 annually Voluntary helpers also drive about 900 000 km per year without compensation!

Black grouse Hazel grouse Rock ptarmigan Willow grouse Capercaillie

Hudson Bay Company s records (redrawn from Butler 1953)

Population growth model (in its simplest form) New population size = old size + births - deaths + immigrated emigrated N(t+1) = N(t)e r [1 - N(t)/K] N = population size t = time r = growth rate K = carrying capacity There are three kinds of mathematicians: Those who can count and those who cant. Anon.

During 1960s-80s: 6-7 years cycles prevailed Lindström, Jan 1994: Modelling grouse population dynamics. PhD thesis, Univ. Helsinki. 18 16 14 12 10 8 6 Caper Black Hazel 4 2 0 1960 1970 1980 1990 2000 2010

N t = a + b 1 (t) + b 2 cos(t) + b 3 sin(t), where a constant, b 1 captures the trend, b 2 and b 3 together with the trigonometric functions allow for the part of population fluctuation

Cycles can be modelled nicely in 1960s-1980s by a combination of sin and cosine functions What is the population ecological explanation of sin and cosine functions? Of course, none!

Annual bag of black grouse in SW Finland during 1897 1930

Elements needed in Finnish grouse cycles: - delayed density dependence - dampening dynamics: random hits are needed - spatial synchrony of populations Reasons: - intrinsic factors; age structure of population - weather effects (did) - predation (dd) - parasites, diseases (dd) - etc. - most probably a combination of several factors

During increasing phase: - females older than average, producing more offspring - females lay more eggs - females (also/especially old) probably in better physical condition (why is that? spring food, weather, history (year of birth?), better incubators, better in guarding a brood, selecting habitats with less predators), other behavioural responses to predation? During decreasing phase: - factors opposite

What could a random hit be? Weather conditions during egg-laying period and (especially) during early brood season Predation especially during vole population low Diseases Parasites A combination of these (and unknown) factors (In addition, population age structure is playing at least some role in cyclic fluctuations)

18 16 Nation-wide averages - problem of spatial synchrony 14 12 10 8 Caper Black Hazel Willow 6 4 2 0 1960 1970 1980 1990 2000 2010 2020

BLACK Lag Number 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 ACF 1,0,5 0,0 -,5-1,0 Confidence Limits Coefficient 1963 1985 1986 2008 BLACK Lag Number 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 ACF 1,0,5 0,0 -,5-1,0 Confidence Limits Coefficient

Why did the cycles disappear (hypotheses only): - Species densities decreased below a critical threshold due to various reasons (increased predation, lowered habitat quality etc.) - Decreased densities: fewer observations produce more noise to the data - Simulations suggest that minor changes in parameters may alter dynamics: either shortening or lengthening cycles; they may easily disappear and come back as well - If dispersal is needed to maintain spatial synchrony, it may have become weaker due to e.g. habitat fragmentation

SPATIAL ASPECTS

One example: Spatial synchrony in grouse populations1964-2008 15 game management districts All pair-wise correlations calculated (105) Mean value is used to describe average regional synchronism Sliding time window technique Synchrony in 20 years periods 1. 1964-1983 2. 1965-1984.... 26. 1989-2008

Ranta et al. 1995, updated 0.8 0.7 0.6 0.5 0.4 0.3 Caper Black Hazel 0.2 0.1 0 1972 1977 1982 1987 1992 1997 2002

Thank You for your attention!