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11.12.2018

• Organised by the • 40 – 50 routes Latvian Latvian Ornithological counted annually society breeding • Volunteer based • Started in 2005 • A part of the Biodiversity counts monitoring programme – Funded by the Nature Trends of the common Conservation forest in Latvia Agency

Ainārs Auniņš

Transects Systematic + random position of routes

• Predefined layout of «monitoring squares» • Observer chooses desirable square • Location of the route whithin a square chosen randomly Route length 4 km: 2 transect lines 2km long 1 km apart; 8 sections

N Section Section maps length – 500 m • 8 sections Distance • 500 m Counting • All belts and in 3 • 0 – 25 m from transect observations • 25 – 100 m from transect counting distance • >100 m from transect mapped belts • Field form times filled for each 4 times • 0 20 III – 1 IV section • 1 20 IV – 30 IV per • 2 10 V – 25 V season • 3 5 VI – 20 VI

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Breeding bird monitoring routes (2005 – 2018)

• Annual population indices > 100 bird species

• Annual population trends > 100 Outputs bird species • Annual Farmland Bird Index and Forest bird index

• Population estimates

Trend classification principles

• TRIM (TRends and Trend Indices for Monitoring data) Strong increase analysis – ln countij ~ sitei + yearj – Imputation of Moderate increase missing data – Population indices – Linear trend Stable (multicative slope; S) – Confidence Moderate decline interval CI = S ± 1.96 SE – Trend Steep decline classification

Uncertain

0.85 0.90 0.95 1.00 1.05 1.10 1.15 Confidence interval of the trend

Population trends Trends by ecosysytems

2005 - 2018 2013 - 2018 All birds Forest birds Trend 2005 - 2013 - 2005 - 2013 - 2018 2018 2018 2018 Steep decline 2 8 2 1

Moderate decline 11 19 5 10 Africa Africa S S Asia Stable Europe 28 4 14 2 Resident Resident Moderate 28 7 12 5 increase Strong increase 0 0 0 0 Uncertain 37 68 21 36 Total 106 106 54 54

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Specialists vs non-specialists

• Migration strategy • GLM Forest • Food • Slope ~ … 2005 – 2018 2013 - 2018 • Edge • Weight: 1/SE of birds: preference/avoidance trend slope trends by • Specialist/non- specialist (EBCC) • ALL PREDICTORS traits • Nesting strategy UNINFORMATIVE – Hole/open nesting ΔAIC < 2 – Nest height – Clutch size

• Species used: – gentilis – Accipiter nisus Forest bird index Food – Hazel Grouse Bonasa bonasia – Grey-headed Picus canus – Black Woodpecker martius 2005 – 2018 2013 - 2018 – Lesser-spotted Woodpecker Dryobates minor – White-backed Woodpecker leucotos – Three-toed Woodpecker Picoides tridactylus – Mistle Turdus viscivorus – Warbler Phylloscopus sibilatrix – Regulus regulus – Red-breasted Flycatcher Ficedula parva – Pied Flycatcher Ficedula hypoleucos

Granivores Granivores – Long-tailed Aegithalos caudatus Insectivores Insectivores Raptors Raptors – Marsh Tit Poecile palustris Soil Soil invertebrates – Tit Poecile montanus Water invertebrates Water invertebrates • Geometric mean index Omnivores – Crested Tit Lophophanes cristatus • No species weighting – Periparus ater – Eurasian familiaris – Spotted nutcracker Nucifraga caryocatactes – Common crossbill Loxia curvirostra – Eurasian bullfinch Pyrrhula pyrrhula – Hawfinch Coccothraustes coccothraustes

Great-spotted Woodpecker White-backed Woodpecker Dendrocopos major Dendrocopos leucotos

Crested Tit Lophophanes cristatus Coal Tit Periparus ater Tits

Black Woodpecker Lesser-spotted Woodpecker Middle-spotted Woodpecker Dryocopus martius Dryobates minor Leiopicus medius Poecile montanus Parus major

Grey-headed Woodpecker Three-toed Woodpecker Picus canus Picoides tridactylus Marsh Tit Poecile palustris Cyanistes caeruleus

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Eurasian Hobby Falco subbuteo Hazel Grouse Bonasa bonasia

Common Buzzard Buteo buteo Eurasian Sparrowhawk Accipiter nisus

EBCC 2005 - 2015: 0.966 ± 0.0107

Lesser-spotted Eagle Clanga pomarina Northern Goshawk Accipiter gentilis 2005-2018: steep decline S = 0.8864 ± 0.0238

2013-2018: uncertain S= 0.9939 ± 0.1036

9 Redwing Turdus iliacus Redwing Turdus iliacus

1961 - 1990 2070 - 2099

EBCC 2005 - 2015: 0.968 ± 0.0033

2005-2018: steep decline S = 0.8873 ± 0.0232

2013-2018: steep decline S= 0.7116 ± 0.0742

Redwing Turdus iliacus Summary 1980 - 1984 • The forest species are not performing overall worse than other ecosystem species • The 2 steep declining birds are linked to forests • Species 5-year trends are worse than 13-year trends • Variance in trend slopes is 2000 - 2004 2013 - 2017 larger in forest species occurring all-year round • The tested traits do not explain variance in the trends of forest species • Forest bird index has been overall stable with non- significant declining trend

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Thank you! Special thanks to the many volunteer birdwatchers collecting the data!

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