Climate Change, Northern Birds of Conservation Concern and Matching the Hotspots of Habitat Suitability with the Reserve Network
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{"title"=>"Climate Change, Northern Birds of Conservation Concern and Matching the Hotspots of Habitat Suitability with the Reserve Network", "type"=>"journal", "authors"=>[{"first_name"=>"Raimo", "last_name"=>"Virkkala", "scopus_author_id"=>"6602857342"}, {"first_name"=>"Risto K.", "last_name"=>"Heikkinen", "scopus_author_id"=>"7003406236"}, {"first_name"=>"Stefan", "last_name"=>"Fronzek", "scopus_author_id"=>"7801628833"}, {"first_name"=>"Niko", "last_name"=>"Leikola", "scopus_author_id"=>"24076472000"}], "year"=>2013, "source"=>"PLoS ONE", "identifiers"=>{"sgr"=>"84877879472", "doi"=>"10.1371/journal.pone.0063376", "pui"=>"368942621", "pmid"=>"23700420", "scopus"=>"2-s2.0-84877879472", "issn"=>"19326203", "isbn"=>"1932-6203 (Electronic)\\n1932-6203 (Linking)"}, "id"=>"34b0e526-43e9-34fb-aa7e-4a80e49cb10e", "abstract"=>"National reserve networks are one of the most important means of species conservation, but their efficiency may be diminished due to the projected climatic changes. Using bioclimatic envelope models and spatial data on habitats and conservation areas, we studied how efficient the reserve network will be in preserving 100 forest, mire, marshland, and alpine bird species of conservation concern in Finland in 2051-2080 under three different climate scenarios. The occurrences of the studied bird species were related to the amount of habitat preferred by each species in the different boreal zones. We employed a novel integrated habitat suitability index that takes into account both the species' probability of occurrence from the bioclimatic models and the availability of suitable habitat. Using this suitability index, the distribution of the topmost 5% suitability squares (\"hotspots\") in the four bird species groups in the period 1971-2000 and under the three scenarios were compared with the location of reserves with the highest amounts of the four habitats to study the efficiency of the network. In species of mires, marshlands, and Arctic mountains, a high proportion of protected habitat was included in the 5% hotspots in the scenarios in 2051-2080, showing that protected areas cover a high proportion of occurrences of bird species. In contrast, in forests in the southern and middle boreal zones, only a small proportion of the protected habitat was included in the 5% hotspots, indicating that the efficiency of the protected area network will be insufficient for forest birds in the future. In the northern boreal zone, the efficiency of the reserve network in forests was highly dependent on the strength of climate change varying between the scenarios. Overall, there is no single solution to preserving biodiversity in a changing climate, but several future pathways should be considered.", "link"=>"http://www.mendeley.com/research/climate-change-northern-birds-conservation-concern-matching-hotspots-habitat-suitability-reserve-net", "reader_count"=>54, "reader_count_by_academic_status"=>{"Unspecified"=>2, "Professor > Associate Professor"=>2, "Researcher"=>12, "Student > Doctoral Student"=>3, "Student > Ph. D. Student"=>15, "Student > Postgraduate"=>1, "Student > Master"=>12, "Other"=>2, "Student > Bachelor"=>4, "Professor"=>1}, "reader_count_by_user_role"=>{"Unspecified"=>2, "Professor > Associate Professor"=>2, "Researcher"=>12, "Student > Doctoral Student"=>3, "Student > Ph. D. Student"=>15, "Student > Postgraduate"=>1, "Student > Master"=>12, "Other"=>2, "Student > Bachelor"=>4, "Professor"=>1}, "reader_count_by_subject_area"=>{"Engineering"=>1, "Unspecified"=>3, "Environmental Science"=>22, "Agricultural and Biological Sciences"=>26, "Veterinary Science and Veterinary Medicine"=>1, "Earth and Planetary Sciences"=>1}, "reader_count_by_subdiscipline"=>{"Engineering"=>{"Engineering"=>1}, "Earth and Planetary Sciences"=>{"Earth and Planetary Sciences"=>1}, "Agricultural and Biological Sciences"=>{"Agricultural and Biological Sciences"=>26}, "Unspecified"=>{"Unspecified"=>3}, "Environmental Science"=>{"Environmental Science"=>22}, "Veterinary Science and Veterinary Medicine"=>{"Veterinary Science and Veterinary Medicine"=>1}}, "reader_count_by_country"=>{"Korea (South)"=>1, "United States"=>1, "Finland"=>2, "Brazil"=>1, "France"=>2, "Portugal"=>1}, "group_count"=>4}

Scopus | Further Information

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Figshare

  • {"files"=>["https://ndownloader.figshare.com/files/1063797"], "description"=>"<p>The overall habitat suitability index was based on the mean of species-specific habitat suitability indices, which is the probability of species occurrence in 2051–2080 multiplied by the amount of habitat preferred by species in each square. The amount of habitat in this calculation was scaled in each square by dividing it by the largest amount of the given habitat in each zone. The probability of species occurrence was based on three different climate scenarios: B1 (CSIRO), ensemble mean of 19 GCM based on A1B (19GCM) and A2 (MIROC3). Squares in which the given habitat was absent were excluded from the correlation analyses. The number of squares included in each species group, in southern, middle and northern boreal zones, respectively: in species of forests 1539, 1164, and 1071, in species of mires 1509, 1159, and 1069, and in species of marshlands 1313, 989, and 636. The number of squares included in Arctic mountain heaths was 686 and in Arctic mountain birch woods 452. The number of species in each species group in parentheses.</p>", "links"=>[], "tags"=>["ecology", "Ecological environments", "Terrestrial environments", "biodiversity", "biogeography", "Conservation science", "Global change ecology", "Species extinction", "Atmospheric science", "Climatology", "climate change", "protected", "suitability", "groups"], "article_id"=>704905, "categories"=>["Biological Sciences", "Earth and Environmental Sciences"], "users"=>["Raimo Virkkala", "Risto K. Heikkinen", "Stefan Fronzek", "Niko Leikola"], "doi"=>"https://dx.doi.org/10.1371/journal.pone.0063376.t001", "stats"=>{"downloads"=>0, "page_views"=>6, "likes"=>0}, "figshare_url"=>"https://figshare.com/articles/_Correlation_Spearman_rank_r_s_between_the_amount_of_protected_habitat_and_overall_habitat_suitability_index_of_species_groups_in_a_given_square_/704905", "title"=>"Correlation (Spearman rank, r<sub>s</sub>) between the amount of protected habitat and overall habitat suitability index of species groups in a given square.", "pos_in_sequence"=>0, "defined_type"=>3, "published_date"=>"2013-05-20 01:21:45"}
  • {"files"=>["https://ndownloader.figshare.com/files/1063795"], "description"=>"<p>Hotspots are based on the overall habitat suitability index of species in 1971–2000 (A) and in 2051–2080 according to the three scenarios: B = CSIRO, B1; C = 19GCM ensemble mean, A1B; D = MIROC, A2. The southern boreal zone = olive, the middle boreal zone = yellow, the northern boreal zone = light yellow.</p>", "links"=>[], "tags"=>["ecology", "Ecological environments", "Terrestrial environments", "biodiversity", "biogeography", "Conservation science", "Global change ecology", "Species extinction", "Atmospheric science", "Climatology", "climate change", "hotspots"], "article_id"=>704903, "categories"=>["Biological Sciences", "Earth and Environmental Sciences"], "users"=>["Raimo Virkkala", "Risto K. Heikkinen", "Stefan Fronzek", "Niko Leikola"], "doi"=>"https://dx.doi.org/10.1371/journal.pone.0063376.g004", "stats"=>{"downloads"=>0, "page_views"=>6, "likes"=>0}, "figshare_url"=>"https://figshare.com/articles/_The_location_of_the_5_hotspots_of_forest_species_/704903", "title"=>"The location of the 5% hotspots of forest species.", "pos_in_sequence"=>0, "defined_type"=>1, "published_date"=>"2013-05-20 01:21:43"}
  • {"files"=>["https://ndownloader.figshare.com/files/1063793"], "description"=>"<p>Variation in species-specific habitat suitability index of species (A, C, E) and the amount of protected forest, mire and marshland habitat (in km<sup>2</sup>; B, D, F; respectively) in 2051–2080 according to the 19GCM ensemble mean in a forest species (the red-breasted flycatcher <i>Ficedula parva</i>; A, B), in a mire species (the wood sandpiper <i>Tringa glareola</i>: C, D) and in a marshland species (the marsh harrier <i>Circus aeruginosus</i>: E, F).</p>", "links"=>[], "tags"=>["ecology", "Ecological environments", "Terrestrial environments", "biodiversity", "biogeography", "Conservation science", "Global change ecology", "Species extinction", "Atmospheric science", "Climatology", "climate change", "suitability", "protected", "boreal", "zones"], "article_id"=>704902, "categories"=>["Biological Sciences", "Earth and Environmental Sciences"], "users"=>["Raimo Virkkala", "Risto K. Heikkinen", "Stefan Fronzek", "Niko Leikola"], "doi"=>"https://dx.doi.org/10.1371/journal.pone.0063376.g003", "stats"=>{"downloads"=>2, "page_views"=>11, "likes"=>0}, "figshare_url"=>"https://figshare.com/articles/_Species_specific_habitat_suitability_index_and_the_amount_of_protected_habitat_in_the_southern_boreal_middle_boreal_and_northern_boreal_zones_in_Finland_/704902", "title"=>"Species-specific habitat suitability index and the amount of protected habitat in the southern boreal, middle boreal and northern boreal zones in Finland.", "pos_in_sequence"=>0, "defined_type"=>1, "published_date"=>"2013-05-20 01:21:42"}
  • {"files"=>["https://ndownloader.figshare.com/files/1063789"], "description"=>"<p>Protected area network in Finland.</p>", "links"=>[], "tags"=>["ecology", "Ecological environments", "Terrestrial environments", "biodiversity", "biogeography", "Conservation science", "Global change ecology", "Species extinction", "Atmospheric science", "Climatology", "climate change"], "article_id"=>704899, "categories"=>["Biological Sciences", "Earth and Environmental Sciences"], "users"=>["Raimo Virkkala", "Risto K. Heikkinen", "Stefan Fronzek", "Niko Leikola"], "doi"=>"https://dx.doi.org/10.1371/journal.pone.0063376.g001", "stats"=>{"downloads"=>0, "page_views"=>28, "likes"=>0}, "figshare_url"=>"https://figshare.com/articles/_Protected_area_network_in_Finland_/704899", "title"=>"Protected area network in Finland.", "pos_in_sequence"=>0, "defined_type"=>1, "published_date"=>"2013-05-20 01:21:39"}
  • {"files"=>["https://ndownloader.figshare.com/files/1063798", "https://ndownloader.figshare.com/files/1063799"], "description"=>"<div><p>National reserve networks are one of the most important means of species conservation, but their efficiency may be diminished due to the projected climatic changes. Using bioclimatic envelope models and spatial data on habitats and conservation areas, we studied how efficient the reserve network will be in preserving 100 forest, mire, marshland, and alpine bird species of conservation concern in Finland in 2051–2080 under three different climate scenarios. The occurrences of the studied bird species were related to the amount of habitat preferred by each species in the different boreal zones. We employed a novel integrated habitat suitability index that takes into account both the species’ probability of occurrence from the bioclimatic models and the availability of suitable habitat. Using this suitability index, the distribution of the topmost 5% suitability squares (“hotspots”) in the four bird species groups in the period 1971–2000 and under the three scenarios were compared with the location of reserves with the highest amounts of the four habitats to study the efficiency of the network. In species of mires, marshlands, and Arctic mountains, a high proportion of protected habitat was included in the 5% hotspots in the scenarios in 2051–2080, showing that protected areas cover a high proportion of occurrences of bird species. In contrast, in forests in the southern and middle boreal zones, only a small proportion of the protected habitat was included in the 5% hotspots, indicating that the efficiency of the protected area network will be insufficient for forest birds in the future. In the northern boreal zone, the efficiency of the reserve network in forests was highly dependent on the strength of climate change varying between the scenarios. Overall, there is no single solution to preserving biodiversity in a changing climate, but several future pathways should be considered.</p></div>", "links"=>[], "tags"=>["ecology", "Ecological environments", "Terrestrial environments", "biodiversity", "biogeography", "Conservation science", "Global change ecology", "Species extinction", "Atmospheric science", "Climatology", "climate change", "birds", "matching", "hotspots", "suitability"], "article_id"=>704906, "categories"=>["Biological Sciences", "Earth and Environmental Sciences"], "users"=>["Raimo Virkkala", "Risto K. Heikkinen", "Stefan Fronzek", "Niko Leikola"], "doi"=>["https://dx.doi.org/10.1371/journal.pone.0063376.s001", "https://dx.doi.org/10.1371/journal.pone.0063376.s002"], "stats"=>{"downloads"=>4, "page_views"=>10, "likes"=>0}, "figshare_url"=>"https://figshare.com/articles/_Climate_Change_Northern_Birds_of_Conservation_Concern_and_Matching_the_Hotspots_of_Habitat_Suitability_with_the_Reserve_Network_/704906", "title"=>"Climate Change, Northern Birds of Conservation Concern and Matching the Hotspots of Habitat Suitability with the Reserve Network", "pos_in_sequence"=>0, "defined_type"=>4, "published_date"=>"2013-05-20 01:21:46"}
  • {"files"=>["https://ndownloader.figshare.com/files/1063790"], "description"=>"<p>Overall proportion (%) of protected habitat (All protected areas; i.e. the amount of protected habitat vs. the total amount of the habitat) and the proportion (%) protected in the 5% hotspots (1971–2000; CSIRO, B1; 19GCM; MIROC, A2) in three of the studied habitats, forests (A), mires (B) and marshlands (C), and in the three vegetation zones: blue column = the southern boreal zone, red column = the middle boreal zone, green column = the northern boreal zone. The 5% hotpots are separately determined for the three species groups based on the overall habitat suitability index of species and model projections for the observed climate in 1971–2000 and the three scenarios for 2051–2080 (B1, 19GCM ensemble mean A1B, A2).</p>", "links"=>[], "tags"=>["ecology", "Ecological environments", "Terrestrial environments", "biodiversity", "biogeography", "Conservation science", "Global change ecology", "Species extinction", "Atmospheric science", "Climatology", "climate change", "protected"], "article_id"=>704900, "categories"=>["Biological Sciences", "Earth and Environmental Sciences"], "users"=>["Raimo Virkkala", "Risto K. Heikkinen", "Stefan Fronzek", "Niko Leikola"], "doi"=>"https://dx.doi.org/10.1371/journal.pone.0063376.g002", "stats"=>{"downloads"=>0, "page_views"=>2, "likes"=>0}, "figshare_url"=>"https://figshare.com/articles/_The_proportion_of_protected_habitat_in_1971_8211_2000_and_in_2051_8211_2080_/704900", "title"=>"The proportion of protected habitat in 1971–2000 and in 2051–2080.", "pos_in_sequence"=>0, "defined_type"=>1, "published_date"=>"2013-05-20 01:21:40"}

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  • {"unique-ip"=>"5", "full-text"=>"6", "pdf"=>"1", "scanned-summary"=>"0", "scanned-page-browse"=>"0", "figure"=>"0", "supp-data"=>"0", "cited-by"=>"0", "year"=>"2019", "month"=>"2"}
  • {"unique-ip"=>"4", "full-text"=>"3", "pdf"=>"3", "scanned-summary"=>"0", "scanned-page-browse"=>"0", "figure"=>"0", "supp-data"=>"0", "cited-by"=>"0", "year"=>"2019", "month"=>"3"}
  • {"unique-ip"=>"4", "full-text"=>"6", "pdf"=>"0", "scanned-summary"=>"0", "scanned-page-browse"=>"0", "figure"=>"0", "supp-data"=>"0", "cited-by"=>"0", "year"=>"2019", "month"=>"4"}
  • {"unique-ip"=>"5", "full-text"=>"3", "pdf"=>"5", "scanned-summary"=>"0", "scanned-page-browse"=>"0", "figure"=>"0", "supp-data"=>"0", "cited-by"=>"0", "year"=>"2019", "month"=>"5"}

Relative Metric

{"start_date"=>"2013-01-01T00:00:00Z", "end_date"=>"2013-12-31T00:00:00Z", "subject_areas"=>[{"subject_area"=>"/Biology and life sciences", "average_usage"=>[269, 466, 588, 697, 800, 896, 988, 1076, 1165, 1254, 1340, 1417]}, {"subject_area"=>"/Biology and life sciences/Ecology", "average_usage"=>[290, 478, 601, 716, 816, 914, 1016, 1112, 1203, 1285, 1373, 1451, 1516]}, {"subject_area"=>"/Biology and life sciences/Organisms", "average_usage"=>[281, 484, 611, 728, 835, 934, 1030, 1123, 1214, 1299, 1383, 1464]}, {"subject_area"=>"/Earth sciences/Atmospheric science", "average_usage"=>[287, 443, 560, 684, 777, 894, 989, 1065, 1143, 1235, 1335, 1423, 1477]}, {"subject_area"=>"/Ecology and environmental sciences/Aquatic environments", "average_usage"=>[276, 480, 624, 713, 810, 927, 1024, 1130, 1221, 1318, 1422, 1506, 1587]}, {"subject_area"=>"/Ecology and environmental sciences/Conservation science", "average_usage"=>[390, 618, 766, 904, 1030, 1153, 1268, 1391, 1487, 1591, 1685, 1767, 1865]}, {"subject_area"=>"/Ecology and environmental sciences/Ecological environments", "average_usage"=>[261, 401]}]}
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