Bertille Mohring, François Brischoux, Frédéric Angelier. 2021: Vineyards, but not cities, are associated with lower presence of a generalist bird, the Common Blackbird (Turdus merula), in Western France. Avian Research, 12(1): 3. DOI: 10.1186/s40657-020-00239-0
Citation: Bertille Mohring, François Brischoux, Frédéric Angelier. 2021: Vineyards, but not cities, are associated with lower presence of a generalist bird, the Common Blackbird (Turdus merula), in Western France. Avian Research, 12(1): 3. DOI: 10.1186/s40657-020-00239-0

Vineyards, but not cities, are associated with lower presence of a generalist bird, the Common Blackbird (Turdus merula), in Western France

More Information
  • Corresponding author:

    Bertille Mohring, bertille.mohring@abo.fi

  • Received Date: 22 Jul 2020
  • Accepted Date: 13 Dec 2020
  • Available Online: 24 Apr 2022
  • Publish Date: 04 Jan 2021
  • Background 

    Land-use change is one of the main drivers of the global erosion of biodiversity. In that context, it is crucial to understand how landscape characteristics drive the presence of rare endangered species. Nevertheless, it is also important to study common species in multiple habitats, because they represent a large proportion of biodiversity and are essential to maintain ecological functions. Interestingly, some habitats, as farmlands with permanent crops (e.g. vineyards), have been overlooked in the literature.

    Methods 

    In this study, we investigated the distribution of a widespread and common bird species, the Common Blackbird (Turdus merula), within and between the three main habitats of our study area (rural Western France). We specifically focused on (1) woodlands, (2) farmlands with a high vineyard coverage, and (3) moderately urbanized areas. Specifically, we aimed to assess the beneficial and detrimental effects of these habitats and their fine-scale composition on the presence of a common bird species, relying on a survey by point counts (nearly 100 locations). We studied the effects of habitats and gradients of fine-scale habitat composition on blackbird presence using logistic regression analyses.

    Results 

    Blackbirds were present in all studied habitats. However, their presence varied between habitats, being lower in vineyards than in woodlands and cities. In woodlands and cities, fine-scale analyses did not reveal any component driving the species' presence. However, we found that shrub and tree vegetation cover had a significant positive effect on blackbird presence in vineyards.

    Conclusions 

    Our results are in agreement with the definition of a generalist species. Interestingly, species distribution varied between habitats. The high presence of blackbirds in urban areas suggests that medium-sized cities, despite their artificialization, do not constrain the settlement of this former forest specialist and that green spaces may allow blackbirds to thrive in medium-sized cities. On the contrary, we found an impoverished presence of blackbirds in vineyards and a positive effect of vegetation on their presence in these landscapes. This suggests that permanent crops, and more generally farmlands, may impose important constraints to common species. Future studies should examine how to enhance biodiversity through agricultural management policies, especially in vineyards.

  • The Grey Partridge (Perdix perdix Linnaeus, 1758) is a polytypic Galliform species included in the Least Concern (LC) category of the IUCN Red List of Threatened Species at both global (Staneva and Burfield 2017) and national scale (Peronace et al. 2012). Considering that, to date, Grey Partridge's population genetics is based on mtDNA (Andersen and Kahlert 2012), and that heteroplasmy has been previously described specifically in hybrids and other Galliform species (Barr et al. 2005; Gandolfi et al. 2017), we decided to investigate the presence of this phenomenon in P. perdix.

    During this research, both wild and farm animals were analyzed (102 samples, Additional file 1); as concerns wild animals, both present and historical (see Gandolfi et al. 2017 for "historical" definition), P. perdix samples were characterized, whereas as to contemporary live samples, non-invasive specimens belonged both to husbandries or were sampled in nature (feather or faeces).

    DNA was extracted through a specifically modified protocol (Lucentini et al. 2010), and two mitochondrial genes, Cytochrome Oxidase Subunit I (COI) and Control Region (CR/D-loop), were amplified (Kerr et al. 2007; Barbanera et al. 2009) and Sanger sequencing was outsourced for both ends of amplicons to Eurofins Genomics.

    All sequences of 561 bp for D-loop and of 334 bp for COI were screened manually looking for double peaks in order to evaluate the presence and to validate point heteroplasmy (Ramos et al. 2013). We found out that, out of 102 individuals, nine showed point heteroplasmy in the D-loop fragment (Fig. 1A), and two in COI gene. Both mutations are missense, causing in the first case the substitution of an Isoleucine (AUU) by a Serine (AGU) while in the other case a Glycine (CAA) was substituted by an Arginine (CGA).

    Figure  1.  A Example of D-loop heteroplasmy in Perdix samples. Example of polymorphic site (b) (GenBank MN413492), clearly showing mtDNA heteroplasmy compared with homoplasmic samples for this site (a) (GenBank MN413497) (c) (GenBank MN413494). B Electropherogram of one of the cloned samples and of two related clones (MN413488–MN413489)

    Different haplotypes were retrieved and deposited in GenBank (Accession Numbers MN413488–MN413500, MT649222–MT649228 for D-loop and MN480303–MN480304, MT649229–MT649247 for COI).

    Specimens presenting clear heteroplasmic D-loop single mutation sites and others showing electropherograms suggesting D-loop heteroplasmy insertion/deletion, were cloned using pGEM-T Easy vector (Promega) following the manufacturer's instructions. The analysis of clones strongly confirms the presence of heteroplasmy and the absence of any contamination. In fact, obtained clones, when sequenced, showed two different haplotypes, confirming the presence of more than one mtDNA in each cloned sample (Fig. 1B).

    Furthermore, to rule out possible contaminations, 39 individuals, including the nine heteroplasmic ones, were genotyped with a nuclear gene, the Oocyte maturation factor (c-mos) using both primers appropriately designed for this purpose (CMOS2F; F5′-3′GCTGTGAAGCAAGTGAAGAA; CMOS2 R; R5′-3′AGCCGAAGTCTCCAATCTT) and those described by Shen et al. (2014). The analysis of this nuclear locus never showed any double peaks and/or signal superimposition, thus excluding the presence of sample contamination. Obtained related sequences were registered in GenBank (MN442418–MN442421).

    In conclusion, this study provides the first evidence of mitochondrial heteroplasmy in Perdix perdix, a phenomenon that can create some ambiguities in phylogenetic and evolutionary interpretations. In fact, paternal mtDNA could lead to inaccurate estimates of divergence times if the molecular clock is used, and could confuse the putative haplogroup assignment. Furthermore, the data obtained, suggesting the occurrence of hybridization in Perdix perdix, strongly underlined the importance of the rapid adoption of control measures aimed to prevent the introduction of genomes from different geographical areas and to avoid the concrete risk of an extinction vortex to which the residual, small and isolated populations are segregated.

    Further researches should focus to advance the knowledge on the hybridization scheme of Perdix species and on the possible interfertile species, to better understand the evolutionary history of the species and its management.

    Supplementary information accompanies this paper at https://doi.org/10.1186/s40657-020-00213-w.

    Authors would like to thank the Natural History Museum of the University of Pisa, the Civic Museum of Zoology of Rome, the Casalina's Gallery of Natural History and the Natural History Museum of Fisiocritici of Siena.

    AA, PV and LL conceived and designed the research. PV, PS and AA acquired samples. CP, FG and LL performed the sample analysis. LL, AF and AA analyzed the data. PV, LL, CP, FS, IDR and AA conducted manuscript preparation, revising and analysis of intellectual contents. LL and AA contributed equally to the extent of this research. All authors read and approved the final manuscript.

    Sample number and origin of each sample was reported. In particular a geographical origin or a museum/collection collocation was specified, if applicable. Furthermore, details about GenBank code on D-Loop, COI and c-mos fragment were provided. Different haplotypes were retrieved and deposited in GenBank (Accession Numbers MN413488–MN413500, MT649222–MT649228 for Dloop, MN480303–MN480304, MT649229–MT649247 for COI and MN442418–MN442421 for c-mos).

    The performed sampling procedures and analyses are consistent with the Directive 2010/63/EU, the Italian national regulations and the indications of the Ethics Committee of the Universities of Perugia and Viterbo (Italy). The approval by the Ethics Committee was not necessary because of the nature of the samples (museal individuals) and of the non-invasive in vivo sampling method. In fact, just two feathers were collected from live animals excluding those having a functional role. Birds were immediately released at the same sampling site. The sampling campaign was authorized by local authorities with the scientific ISPRA authorization number 12184.

    Not applicable.

    The authors declare that they have no competing interests.

  • Abs M, Bergen F. A long term survey of the avifauna in an urban park. In: Marzluff JM, Shulenberger E, Endlicher W, Alberti M, Bradley G, Ryan C, et al., editors. Urban ecology: an international perspective on the interaction between humans and nature. Boston: Springer; 2008. p. 373–6.
    Assandri G, Bogliani G, Pedrini P, Brambilla M. Insectivorous birds as 'non-traditional' flagship species in vineyards: applying a neglected conservation paradigm to agricultural systems. Ecol Indic. 2017a;80: 275–85.
    Assandri G, Giacomazzo M, Brambilla M, Griggio M, Pedrini P. Nest density, nest-site selection, and breeding success of birds in vineyards: management implications for conservation in a highly intensive farming system. Biol Conserv. 2017b;205: 23–33.
    Baillie J, Hilton-Taylor C, Stuart SN. IUCN red list of threatened species: a global species assessment. Gland: IUCN–The World Conservation Union; 2004.
    Barton K. MuMIn: Multi-model inference. R package version 1.43.17. 2020. .
    Beaugeard E, Brischoux F, Angelier F. Green infrastructures and ecological corridors shape avian biodiversity in a small French city. Urban Ecosyst. 2020. .
    Betts MG, Diamond AW, Forbes GJ, Villard M-A, Gunn JS. The importance of spatial autocorrelation, extent and resolution in predicting forest bird occurrence. Ecol Model. 2006;191: 197–224.
    Bivand RS, Wong DWS. Comparing implementations of global and local indicators of spatial association. TEST. 2018;27: 716–48.
    Brédif H, Simon L. Ordinary biodiversity, local stakeholders and forest management as a driver for regional sustainable development. J Forest. 2014;04: 249–58.
    Brouat C, Chevallier H, Meusnier S, Noblecourt T, Rasplus J-Y. Specialization and habitat: spatial and environmental effects on abundance and genetic diversity of forest generalist and specialist Carabus species. Mol Ecol. 2004;13: 1815–26.
    Buckley NJ. The new atlas of breeding birds in Britain and Ireland: 1988–1991. In: Gibbons DW, Reid JB, Chapman RA, editors. The Auk. London: T & AD Poyser; 1995. p. 812–3.
    Burnham KP, Anderson DR. Model selection and multi-model inference: a practical information-theoretic approach. 2nd ed. New York: Springer; 2002.
    Butler RW. Population regulation of wading Ciconiiform birds. Colon Waterbird. 1994;17: 189–99.
    Carrara E, Arroyo-Rodríguez V, Vega-Rivera JH, Schondube JE, de Freitas SM, Fahrig L. Impact of landscape composition and configuration on forest specialist and generalist bird species in the fragmented Lacandona rainforest, Mexico. Biol Conserv. 2015;184: 117–26.
    Clavel J, Julliard R, Devictor V. Worldwide decline of specialist species: toward a global functional homogenization? Front Ecol Environ. 2011;9: 222–8.
    Clergeau P, Croci S, Jokimäki J, Kaisanlahti-Jokimäki M-L, Dinetti M. Avifauna homogenisation by urbanisation: analysis at different European latitudes. Biol Conserv. 2006;127: 336–44.
    Cockle KL, Martin K, Drever MC. Supply of tree-holes limits nest density of cavity-nesting birds in primary and logged subtropical Atlantic forest. Biol Conserv. 2010;143: 2851–7.
    Dabelsteen T. Variation in the response of freeliving Blackbirds Turdus merula to playback of song: I. Effect of continuous stimulation and predictability of the response. Z Tierpsychol. 1982;58: 311–28.
    Dabelsteen T. Variation in the response of freeliving Blackbirds Turdus merula to playback of song: II. Effect of time of day, reproductive status and number of experiments. Z Tierpsychol. 1984;65: 215–27.
    Dabelsteen T. Interactive playback: a finely tuned response. In: McGregor PK, editor. Playback and studies of animal communication. Boston: Springer; 1992. p. 97–109.
    Dabelsteen T, Pedersen SB. Song and information about aggressive responses of blackbirds, Turdus merula: evidence from interactive playback experiments with territory owners. Anim Behav. 1990;40: 1158–68.
    Davis BNK. Soil animals as vectors of organochlorine insecticides for ground-feeding birds. J Appl Ecol. 1966;3: 133–9.
    Devictor V, Julliard R, Jiguet F. Distribution of specialist and generalist species along spatial gradients of habitat disturbance and fragmentation. Oikos. 2008;117: 507–14.
    Diehl P, Helb H-W. Radiotelemetric monitoring of heart-rate responses to song playback in blackbirds (Turdus merula). Behav Ecol Sociobiol. 1986;18: 213–9.
    Donald PF, Green RE, Heath MF. Agricultural intensification and the collapse of Europe's farmland bird populations. Proc Biol Sci. 2001;268: 25–9.
    Ellis EC, Ramankutty N. Putting people in the map: anthropogenic biomes of the world. Front Ecol Environ. 2008;6: 439–47.
    Eötvös CB, Magura T, Lövei GL. A meta-analysis indicates reduced predation pressure with increasing urbanization. Landsc Urban Plan. 2018;180: 54–9.
    Evans KL, Hatchwell BJ, Parnell M, Gaston KJ. A conceptual framework for the colonisation of urban areas: the blackbird Turdus merula as a case study. Biol Rev. 2010;85: 643–67.
    Fernández-Juricic E, Jimenez MD, Lucas E. Bird tolerance to human disturbance in urban parks of Madrid (Spain): management implications. In: Marzluff JM, Bowman R, Donnelly R, editors. Avian ecology and conservation in an urbanizing world. Boston: Springer; 2001. p. 259–73.
    Foley JA, Defries R, Asner GP, Barford C, Bonan G, Carpenter SR, et al. Global consequences of land use. Science. 2005;309: 570–4.
    Fritsch C, Coeurdassier M, Faivre B, Baurand P-E, Giraudoux P, van den Brink NW, et al. Influence of landscape composition and diversity on contaminant flux in terrestrial food webs: a case study of trace metal transfer to European blackbirds Turdus merula. Sci Total Environ. 2012;432: 275–87.
    Futuyma DJ, Moreno G. The evolution of ecological specialization. Annu Rev Ecol Syst. 1988;19: 207–33.
    Gaston KJ, Fuller RA. Commonness, population depletion and conservation biology. Trends Ecol Evol. 2008;23: 14–9.
    Guittet M, Sibe V, Gaudin J-C. Les vignobles: de nouveaux réservoirs de biodiversité. Faune sauvage. 2011: 9.
    Godet L. La « nature ordinaire » dans le monde occidental. L'Espace géographique. 2010;39: 295–308.
    Gregory RD, Noble DG, Custance J. The state of play of farmland birds: population trends and conservation status of lowland farmland birds in the United Kingdom. Ibis. 2004;146: 1–13.
    Hanowski JM, Niemi GJ, Blake JG. Statistical perspectives and experimental design when counting birds on line transects. Condor. 1990;92: 326–35.
    Hatchwell BJ, Chamberlain DE, Perrins CM. The demography of Blackbirds Turdus merula in rural habitats: is farmland a sub-optimal habitat? J Appl Ecol. 1996;33: 1114.
    Hinsley SA, Bellamy PE, Newton I, Sparks TH. Habitat and landscape factors influencing the presence of individual breeding bird species in woodland fragments. J Avian Biol. 1995;26: 94–104.
    Hiron M, Berg Å, Eggers S, Josefsson J, Pärt T. Bird diversity relates to agri-environment schemes at local and landscape level in intensive farmland. Agr Ecosyst Environ. 2013;176: 9–16.
    Hobday AJ, Chambers LE, Arnould JPY. Prioritizing climate change adaptation options for iconic marine species. Biodivers Conserv. 2015;24: 3449–68.
    Hole DG, Whittingham MJ, Bradbury RB, Anderson GQA, Lee PLM, Wilson JD, et al. Widespread local house-sparrow extinctions — Agricultural intensification is blamed for the plummeting populations of these birds. Nature. 2002;418: 931–2.
    Jankowiak Ł, Pietruszewska H, Wysocki D. Weather conditions and breeding season length in blackbird (Turdus merula). Folia Zool. 2014;63: 245–50.
    Jokimäki J, Suhonen J. Distribution and habitat selection of wintering birds in urban environments. Landsc Urban Plan. 1998;39: 253–63.
    Julliard R, Jiguet F. Un suivi intégré des populations d'oiseaux communs en France. Alauda. 2002;70: 137–47.
    Julliard R, Clavel J, Devictor V, Jiguet F, Couvet D. Spatial segregation of specialists and generalists in bird communities. Ecol Lett. 2006;9: 1237–44.
    Kassen R. The experimental evolution of specialists, generalists, and the maintenance of diversity: experimental evolution in variable environments. J Evol Biol. 2002;15: 173–90.
    Kubel JE, Yahner RH. Detection probability of Golden-winged Warblers during point counts with and without playback recordings. J Field Ornithol. 2007;78: 195–205.
    Larsen AE, Noack F. Identifying the landscape drivers of agricultural insecticide use leveraging evidence from 100, 000 fields. Proc Natl Acad Sci USA. 2017;114: 5473–8.
    Lê S, Josse J, Husson F. FactoMineR: an R package for multivariate analysis. J Stat Softw. 2008;25: 1–18.
    Lee DC, Marsden SJ. Adjusting count period strategies to improve the accuracy of forest bird abundance estimates from point transect distance sampling surveys: count period strategies for distance sampling surveys. Ibis. 2008;150: 315–25.
    Lennon JJ, Beale CM, Reid CL, Kent M, Pakeman RJ. Are richness patterns of common and rare species equally well explained by environmental variables? Ecography. 2011;34: 529–39.
    Luck GW, Smallbone LT. Species diversity and urbanisation: patterns, drivers and implications. In: Gaston KJ, editor. Urban Ecology. Cambridge: Cambridge University Press; 2010. p. 88–119.
    Luniak M. Synurbization — adaptation of animal wildlife to urban development. In: Shaw WW, Harris LK, Vandruff L, editors. Proceedings 4th international urban wildlife symposium. Tucson, Arizona: University of Arizona; 2004. p. 50–5.
    Luniak M, Kozlowki P, Nowicki W. Magpie Pica pica in Warsaw — abundance, distribution and changes in its population. Acta Orn. 1997;32: 77–86.
    Mac Nally RC. The relationship between habitat breadth, habitat position, and abundance in forest and woodland birds along a continental gradient. Oikos. 1989;54: 44–54.
    Melles S, Glenn SM, Martin K. Urban bird diversity and landscape complexity: species-environment associations along a multiscale habitat gradient. Conserv Ecol. 2003;7: 5.
    Mennechez G, Clergeau P. Effect of urbanisation on habitat generalists: starlings not so flexible? Acta Oecol. 2006;30: 182–91.
    Najmanová L, Adamík P. Effect of climatic change on the duration of the breeding season in three European thrushes. Bird Study. 2009;56: 349–56.
    Newbold T, Hudson LN, Arnell AP, Contu S, De Palma A, Ferrier S, et al. Has land use pushed terrestrial biodiversity beyond the planetary boundary? A global assessment. Science. 2016;353: 288–91.
    Newton I. Population limitation in birds: the last 100 years. Br Birds. 2007;100: 518–39.
    Olden JD. Biotic homogenization: a new research agenda for conservation biogeography. J Biogeogr. 2006;33: 2027–39.
    Paquet M, Arlt D, Knape J, Low M, Forslund P, Pärt T. Quantifying the links between land use and population growth rate in a declining farmland bird. Ecol Evol. 2019;9: 868–79.
    Pithon JA, Beaujouan V, Daniel H, Pain G, Vallet J. Are vineyards important habitats for birds at local or landscape scales? Basic Appl Ecol. 2016;17: 240–51.
    R Core Team. R: A language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing; 2019.
    Ralph CJ, Droege S, Sauer JR. Managing and monitoring birds using point counts: standards and applications. In: Ralph CJ, Droege S, Sauer JR, editors. Monitoring bird populations by point counts. Albany: U.S. Department of Agriculture, Forest Service, Pacific Southwest Research Station; 1995. p. 161–8.
    Reif J, Voříšek P, Šťastnyˇ K, Bejček V, Petr J. Population increase of forest birds in the Czech Republic between 1982 and 2003. Bird Study. 2007;54: 248–55.
    Rotenberry JT, Wiens JA. A synthetic approach to principal component analysis of bird/habitat relationships. In: Capen DE, editor. The use of multivariate statistics in studies of wildlife habitat. Fort-Collins: Rocky Mountain Forest and Range Experiment Station; 1981. p. 197–208.
    Sandström UG, Angelstam P, Mikusiński G. Ecological diversity of birds in relation to the structure of urban green space. Landsc Urban Plan. 2006;77: 39–53.
    Shultz SB, Bradbury RL, Evans KD, Gregory RM, Blackburn T. Brain size and resource specialization predict long-term population trends in British birds. P Roy Soc B-Biol Sci. 2005;272: 2305–11.
    Sierro A, Arlettaz R. L'avifaune du vignoble en Valais central: évaluation de la diversité à l'aide de transects. Nos Oiseaux. 2003;50: 89–100.
    Siriwardena GM, Baillie SR, Buckland ST, Fewster RM, Marchant JH, Wilson JD. Trends in the abundance of farmland birds: a quantitative comparison of smoothed Common Birds Census indices. J Appl Ecol. 1998;35: 24–43.
    Snow DW. Territory in the Blackbird Turdus Merula. Ibis. 1956;98: 438–47.
    Sol D, González-Lagos C, Moreira D, Maspons J, Lapiedra O. Urbanisation tolerance and the loss of avian diversity. Ecol Lett. 2014;17: 942–50.
    Stanton RL, Morrissey CA, Clark RG. Analysis of trends and agricultural drivers of farmland bird declines in North America: a review. Agr Ecosyst Environ. 2018;254: 244–54.
    Steel ZL, Steel AE, Williams JN, Viers JH, Marquet PA, Barbosa O. Patterns of bird diversity and habitat use in mixed vineyard-matorral landscapes of Central Chile. Ecol Indic. 2017;73: 345–57.
    Wretenberg J, Lindström Å, Svensson S, Thierfelder T, Pärt T. Population trends of farmland birds in Sweden and England: similar trends but different patterns of agricultural intensification. J Appl Ecol. 2006;43: 1110–20.
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