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  • 1
    Call number: AWI Bio-22-94840
    Description / Table of Contents: Vegetation change at high latitudes is one of the central issues nowadays with respect to ongoing climate changes and triggered potential feedback. At high latitude ecosystems, the expected changes include boreal treeline advance, compositional, phenological, physiological (plants), biomass (phytomass) and productivity changes. However, the rate and the extent of the changes under climate change are yet poorly understood and projections are necessary for effective adaptive strategies and forehanded minimisation of the possible negative feedbacks. The vegetation itself and environmental conditions, which are playing a great role in its development and distribution are diverse throughout the Subarctic to the Arctic. Among the least investigated areas is central Chukotka in North-Eastern Siberia, Russia. Chukotka has mountainous terrain and a wide variety of vegetation types on the gradient from treeless tundra to northern taiga forests. The treeline there in contrast to subarctic North America and north-western and central Siberia is represented by a deciduous conifer, Larix cajanderi Mayr. The vegetation varies from prostrate lichen Dryas octopetala L. tundra to open graminoid (hummock and non-hummock) tundra to tall Pinus pumila (Pall.) Regel shrublands to sparse and dense larch forests. Hence, this thesis presents investigations on recent compositional and above-ground biomass (AGB) changes, as well as potential future changes in AGB in central Chukotka. The aim is to assess how tundra-taiga vegetation develops under changing climate conditions particularly in Fareast Russia, central Chukotka. Therefore, three main research questions were considered: 1) What changes in vegetation composition have recently occurred in central Chukotka? 2) How have the above-ground biomass AGB rates and distribution changed in central Chukotka? 3) What are the spatial dynamics and rates of tree AGB change in the upcoming millennia in the northern tundra-taiga of central Chukotka? Remote sensing provides information on the spatial and temporal variability of vegetation. I used Landsat satellite data together with field data (foliage projective cover and AGB) from two expeditions in 2016 and 2018 to Chukotka to upscale vegetation types and AGB for the study area. More specifically, I used Landsat spectral indices (Normalised Difference Vegetation Index (NDVI), Normalised Difference Water Index (NDWI) and Normalised Difference Snow Index (NDSI)) and constrained ordination (Redundancy analysis, RDA) for further k-means-based land-cover classification and general additive model (GAM)-based AGB maps for 2000/2001/2002 and 2016/2017. I also used Tandem-X DEM data for a topographical correction of the Landsat satellite data and to derive slope, aspect, and Topographical Wetness Index (TWI) data for forecasting AGB. Firstly, in 2016, taxa-specific projective cover data were collected during a Russian-German expedition. I processed the field data and coupled them with Landsat spectral Indices in the RDA model that was used for k-means classification. I could establish four meaningful land-cover classes: (1) larch closed-canopy forest, (2) forest tundra and shrub tundra, (3) graminoid tundra and (4) prostrate herb tundra and barren areas, and accordingly, I produced the land cover maps for 2000/2001/2002 and 2016/20017. Changes in land-cover classes between the beginning of the century (2000/2001/2002) and the present time (2016/2017) were estimated and interpreted as recent compositional changes in central Chukotka. The transition from graminoid tundra to forest tundra and shrub tundra was interpreted as shrubification and amounts to a 20% area increase in the tundra-taiga zone and 40% area increase in the northern taiga. Major contributors of shrubification are alder, dwarf birch and some species of the heather family. Land-cover change from the forest tundra and shrub tundra class to the larch closed-canopy forest class is interpreted as tree infilling and is notable in the northern taiga. We find almost no land-cover changes in the present treeless tundra. Secondly, total AGB state and change were investigated for the same areas. In addition to the total vegetation AGB, I provided estimations for the different taxa present at the field sites. As an outcome, AGB in the study region of central Chukotka ranged from 0 kg m-2 at barren areas to 16 kg m-2 in closed-canopy forests with the larch trees contributing the highest. A comparison of changes in AGB within the investigated period from 2000 to 2016 shows that the greatest changes (up to 1.25 kg m 2 yr 1) occurred in the northern taiga and in areas where land cover changed to larch closed-canopy forest. Our estimations indicate a general increase in total AGB throughout the investigated tundra-taiga and northern taiga, whereas the tundra showed no evidence of change in AGB within the 15 years from 2002 to 2017. In the third manuscript, potential future AGB changes were estimated based on the results of simulations of the individual-based spatially explicit vegetation model LAVESI using different climate scenarios, depending on Representative Concentration Pathways (RCPs) RCP 2.6, RCP 4.5 and RCP 8.5 with or without cooling after 2300 CE. LAVESI-based AGB was simulated for the current state until 3000 CE for the northern tundra-taiga study area for larch species because we expect the most notable changes to occur will be associated with forest expansion in the treeline ecotone. The spatial distribution and current state of tree AGB was validated against AGB field data, AGB extracted from Landsat satellite data and a high spatial resolution image with distinctive trees visible. The simulation results are indicating differences in tree AGB dynamics plot wise, depending on the distance to the current treeline. The simulated tree AGB dynamics are in concordance with fundamental ecological (emigrational and successional) processes: tree stand formation in simulated results starts with seed dispersion, tree stand establishment, tree stand densification and episodic thinning. Our results suggest mostly densification of existing tree stands in the study region within the current century in the study region and a lagged forest expansion (up to 39% of total area in the RCP 8.5) under all considered climate scenarios without cooling in different local areas depending on the closeness to the current treeline. In scenarios with cooling air temperature after 2300 CE, forests stopped expanding at 2300 CE (up to 10%, RCP 8.5) and then gradually retreated to their pre-21st century position. The average tree AGB rates of increase are the strongest in the first 300 years of the 21st century. The rates depend on the RCP scenario, where the highest are as expected under RCP 8.5. Overall, this interdisciplinary thesis shows a successful integration of field data, satellite data and modelling for tracking recent and predicting future vegetation changes in mountainous subarctic regions. The obtained results are unique for the focus area in central Chukotka and overall, for mountainous high latitude ecosystems.
    Type of Medium: Dissertations
    Pages: 149 Seiten , Illustrationen, Diagramme
    Language: English
    Note: Dissertation, Potsdam, Universität Potsdam, 2022 , Contents Abstract Zusammenfassung Contents Abbreviations Motivation 1 Introduction 1.1 Scientific background 1.2 Study region 1.3 Aims and objectives 2 Materials and methods 3.1 Section 4 - Strong shrub expansion in tundra-taiga, tree infilling in taiga and stable tundra in central Chukotka (north-eastern Siberia) between 2000 and 2017 3.2 Section 5 - Recent above-ground biomass changes in central Chukotka (NE Siberia) combining field-sampling and remote sensing 3.3 Section 6 - Future spatially explicit tree above-ground biomass trajectories revealed for a mountainous treeline ecotone using the individual-based model LAVESI 4 Strong shrub expansion in tundra-taiga, tree infilling in taiga and stable tundra in central Chukotka (north-eastern Siberia) between 2000 and 2017 Abstract 1 Introduction 2 Materials and methods 2.1 Field data collection and processing 2.2 Landsat data, pre-processing and spectral indices processing 2.3 Redundancy analysis (RDA) and classification approaches 3 Results 3.1 General characteristics of the vegetation field data 3.2 Relating field data to Landsat spectral indices in the RDA model 3.3 Land-cover classification 3.4 Land-cover change between 2000 and 2017 4 Discussion 4.1 Dataset limitations and optimisation 4.2 Vegetation changes from 2000/2001/2002 to 2016/2017 Conclusions Acknowledgements Data availability statement References Appendix A. Detailed description of Landsat acquisitions Appendix B. MODIS NDVI time series from 2000 to 2018 Appendix C. Landsat Indices values for each analysed vegetation site Appendix D. Fuzzy c-means classification for interpretation of uncertainties for land-cover mapping Appendix E. Validation of land-cover maps Appendix F. K-means classification results Appendix G. Heterogeneity of natural landscapes and mixed pixels of satellite data Appendix H. Distribution of land-cover classes and their changes by study area 5 Recent above-ground biomass changes in central Chukotka (NE Siberia) combining field-sampling and remote sensing Abstract 1 Introduction 2 Materials and methods 2.1 Study region and field surveys 2.2 Above-ground biomass upscaling and change derivation 3 Results 3.1 Vegetation composition and above-ground biomass 3.2 Upscaling above-ground biomass using GAM 3.3 Change of above-ground biomass between 2000 and 2017 in the four focus areas 4 Discussion 4.1 Recent state of above-ground biomass at the field sites 4.2 Recent state of above-ground biomass upscaled for central Chukotka 4.3 Change in above-ground biomass within the investigated 15–16 years in central Chukotka 5 Conclusions Data availability statement Author contributions Competing interests Acknowledgements References Appendix A. Sampling and above-ground biomass (AGB) calculation protocol for field data 6 Future spatially explicit tree above-ground biomass trajectories revealed for a mountainous treeline ecotone using the individual-based model LAVESI Abstract 1 Introduction 2 Materials and methods 2.1 Study region 2.2 LAVESI model setup, parameterisation, and validation 2.2.4 LAVESI simulation setup for this study 2.2.5 Validation of the model’s performance 3 Results 3.1 Dynamics and spatial distribution changes of tree above-ground-biomass 3.2 Spatial and temporal validation of the contemporary larch AGB 4 Discussion 4.1 Future dynamics of tree AGB at a plot level 4.2 What are the future dynamics of tree AGB at the landscape level? 5 Conclusions Data availability Acknowledgements References Appendix B. Permutation tests for tree presence versus topographical parameters Appendix C. Landsat-based, field, and simulated estimations of larch above-ground biomass (AGB). 7 Synthesis 7.1 What changes in vegetation composition have happened from 2000 to 2017 in central Chukotka? 7.2 How have the above-ground biomass (AGB) distribution and rates changed from 2000 to 2017 in central Chukotka? 7.3 What are the spatial dynamics and rates of tree AGB change in the upcoming centuries in the northern tundra-taiga from 2020 to 3000 CE on the plot level and landscape level? References Acknowledgements
    Location: AWI Reading room
    Branch Library: AWI Library
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  • 2
    Publication Date: 2023-01-13
    Keywords: Alaska, USA; Deadhorse; ENV; Environmental investigation; Event label; Franklin_Bluffs; Green_Cabin; Happy_Valley; Howe_Island; Isachsen2; Latitude of event; Longitude of event; Mould_Bay2; Queen Elizabeth Islands, Canada NWT; Sagwon; Sample code/label; Vegetation biomass; West_Dock
    Type: Dataset
    Format: text/tab-separated-values, 3555 data points
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  • 3
    Publication Date: 2023-05-12
    Keywords: Area; Change; Country; Difference; Standard deviation; Vegetation biomass; Vegetation biomass, rate of change; Vegetation biomass, total
    Type: Dataset
    Format: text/tab-separated-values, 78 data points
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  • 4
    Publication Date: 2023-05-12
    Keywords: Area; Change; Difference; Province; Standard deviation; Vegetation biomass; Vegetation biomass, rate of change; Vegetation biomass, total
    Type: Dataset
    Format: text/tab-separated-values, 365 data points
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  • 5
    Publication Date: 2023-05-12
    Keywords: Area; Change; Difference; Standard deviation; Vegetation biomass; Vegetation biomass, rate of change; Vegetation biomass, total; Vegetation type
    Type: Dataset
    Format: text/tab-separated-values, 259 data points
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  • 6
    Publication Date: 2023-05-12
    Keywords: Area; Change; Difference; Standard deviation; Vegetation biomass; Vegetation biomass, rate of change; Vegetation biomass, total; Zone, biogeographic
    Type: Dataset
    Format: text/tab-separated-values, 84 data points
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  • 7
    Publication Date: 2023-11-01
    Keywords: Abietinella abietina; Agonimia gelatinosa; Alaska, USA; Alectoria nigricans; Alectoria ochroleuca; Allocetraria madreporiformis; Aloina brevirostris; Alopecurus alpinus; Amblystegium longicuspus; Amblystegium serpens; Anaptychia bryorum; Anastrophyllum minutum; Andromeda polifolia; Androsace chamaejasme; Aneura pinguis; Antennaria friesiana; Antennaria sp.; Anthelia juratzkana; Arctagrostis latifolia; Arctoa anderssonii; Arctocetraria nigricascens; Arctomia delicatula; Arctostaphylos alpina; Arctous rubra; Arnellia fennica; Artemisia borealis; Arthrorhaphis vacillans; Asahinea chrysantha; Astragalus alpinus; Astragalus richardsonii; Astragalus umbellatus; Aulacomnium acuminatum; Aulacomnium palustre; Aulacomnium turgidum; Baeomyces carneus; Baeomyces rufus; Barbilophozia barbata; Barbilophozia binsteadii; Barbilophozia hyperborea; Barbilophozia kunzeana; Barbula unguiculata; Bare ground; Bartramia ithyphylla; Betula nana; Biatora subduplex; Biatora vernalis; Biatorella conspersa; Bistorta vivipara; Blepharostoma trichophyllum; Brachythecium mildeanum; Brachythecium turgidum; Braya glabella var. glabella; Braya glabella var. purpurascens; Braya humilis; Bryocaulon divergens; Bryodina rhypariza; Bryoerythrophyllum recurvirostre; Bryonora castanea; Bryum arcticum; Bryum argenteum; Bryum caespiticium; Bryum pseudotriquetrum; Bryum rutilans; Bryum sp.; Bryum subneodamense; Bryum teres; Bryum wrightii; Bucegia romanica; Calamagrostis canadensis; Calamagrostis sp.; Callialaria curvicaule; Calliergon giganteum; Calliergon sp.; Caloplaca ammiospila; Caloplaca cerina; Caloplaca phaeocarpella; Caloplaca sp.; Caloplaca tetraspora; Caloplaca tiroliensis; Caloplaca tornoensis; Caloplaca xanthostigmoidea; Calypogeja muelleriana; Calypogeja sphagnicola; Campylium arcticum; Campylium chrysophyllum; Campylium longicuspus; Campylium polygamum; Campylium stellatum; Candelariella placodizans; Candelariella sp.; Candelariella terrigena; Cardamine bellidifolia; Cardamine digitata; Carex aquatilis; Carex atrofusca; Carex bigelowii; Carex capillaris; Carex fuliginosa var. misandra; Carex heleonastes; Carex membranacea; Carex microchaeta; Carex rariflora; Carex rotundata; Carex rupestris; Carex scirpoidea; Carex sp.; Carex vaginata var. quasivaginata; Cassiope tetragona; Catapyrenium cinereum; Catapyrenium sp.; Catoscopium nigritum; Cephalozia bicuspidata; Cephalozia pleniceps; Cephaloziella arctogena; Cephaloziella grimsulana; Cephaloziella varians; Cerastium arcticum; Cerastium beeringianum; Ceratodon heterophyllus; Ceratodon purpureus; Cetraria aculeata; Cetraria inermis; Cetraria islandica; Cetraria laevigata; Cinclidium arcticum; Cinclidium latifolium; Cirriphyllum cirrosum; Cladina arbuscula; Cladina mitis; Cladina rangiferina; Cladina stygia; Cladonia alaskana; Cladonia amaurocraea; Cladonia cenotea; Cladonia chlorophaea; Cladonia coccifera; Cladonia cornuta; Cladonia cyanipes; Cladonia deformis; Cladonia fimbriata; Cladonia gracilis; Cladonia gracilis var. elongata; Cladonia macroceras; Cladonia pleurota; Cladonia pocillum; Cladonia pyxidata; Cladonia scabriuscula; Cladonia sp.; Cladonia squamosa; Cladonia subfurcata; Cladonia sulphurina; Cladonia trassii; Cladonia uncialis; Cochlearia groenlandica; Collema ceraniscum; Collema sp.; Collema tenax; Collema undulatum; Conostomum tetragonum; Cratoneuron sp.; Ctenidium molluscum; Ctenidium procerrimum; Cyrtomnium hymenophylloides; Dactylina arctica; Dactylina beringica; Dactylina ramulosa; Deadhorse; Dicranum acutifolium; Dicranum angustum; Dicranum bonjeanii; Dicranum elongatum; Dicranum fragilifolium; Dicranum groenlandicum; Dicranum sp.; Dicranum spadiceum; Dicranum undulatum; Didymodon asperifolius; Didymodon rigidulus; Didymodon rigidulus var. icmadophilus; Didymodon sp.; Didymodon spadiceus; Distichium capillaceum; Distichium inclinatum; Ditrichum flexicaule; Draba alpina; Draba cinerea; Draba nivalis; Draba oblongata; Draba sp.; Draba subcapitata; Drepanocladus aduncus; Drepanocladus brevifolius; Drepanocladus sendtneri; Drepanocladus sp.; Dryas integrifolia; Elymus alaskanus var. alaskanus; Elymus alaskanus var. hyperarcticus; Empetrum nigrum; Encalypta alpina; Encalypta longicolla; Encalypta procera; Encalypta rhaptocarpa; Encalypta sp.; Encalypta vulgaris; Endocarpon pusillum; Entodon concinnus; ENV; Environmental investigation; Epilobium sp.; Equisetum arvense; Equisetum variegatum; Eriophorum angustifolium var. triste; Eriophorum vaginatum; Eurhynchium pulchellum; Event label; Evernia perfragilis; Festuca baffinensis; Festuca brachyphylla; Festuca hyperborea; Fissidens arcticus; Fissidens bryoides; Flavocetraria cucullata; Flavocetraria nivalis; Franklin_Bluffs; Fulgensia bracteata; Fuscopannaria praetermissa; Green_Cabin; Grimmia sp.; Gymnomitrion concinnatum; Gymnomitrion corallioides; Happy_Valley; Hedysarum alpinum; Hennediella heimii; Hennediella heimii var. arctica; Howe_Island; Hulteniella integrifolium; Hylocomium splendens; Hymenostylium recurvirostre; Hypnum bambergeri; Hypnum cupressiforme; Hypnum holmenii; Hypnum revolutum; Hypnum sp.; Hypnum subimponens; Hypnum vaucheri; Hypogymnia subobscura; Isachsen2; Isopterygiopsis pulchella; Japewia tornoensis; Juncus biglumis; Juncus castaneus; Juncus triglumis; Jungermannia polaris; Kiaeria cf. blyttii; Kobresia myosuroides; Lagotis glauca; Latitude of event; Lecanora epibryon; Lecanora geophila; Lecanora luteovernalis; Lecidea ramulosa; Lecidella wulfenii; Leiocolea collaris; Lepraria cf. vouauxii; Lepraria neglecta; Lepraria sp.; Leptobryum pyriforme; Leptogium gelatinosum; Leptogium lichenoides; Leptogium sp.; Limprichtia revolvens; Lloydia serotina; Longitude of event; Lopadium pezizoideum; Lophozia badensis; Lophozia collaris; Lophozia excisa; Lophozia jurensis; Lophozia longiflora; Lophozia polaris; Lophozia savicziae; Lophozia silvicola; Lophozia sp.; Lophozia ventricosa; Lophozia wenzelii; Lupinus arcticus; Luzula confusa; Luzula nivalis; Masonhalea richardsonii; Meesia longiseta; Meesia triquetra; Meesia uliginosa; Megalaria jemtlandica; Megaspora verrucosa; Micarea incrassata; Minuartia arctica; Minuartia rossii; Minuartia rubella; Mnium marginatum; Mnium thomsonii; Mould_Bay2; Mycoblastus sanguinarius; Myurella julacea; Myurella tenerrima; Nephroma arcticum; Nephroma expallidum; Nostoc commune; Ochrolechia androgyna; Ochrolechia cf. inaequatula; Ochrolechia frigida; Ochrolechia inaequatula; Ochrolechia sp.; Ochrolechia upsaliensis; Odontoshisma macounii; Orthilia secunda; Orthothecium chryseum; Orthothecium strictum; Orthothecium varia; Orthotrichum speciosum; Oxyria digyna; Oxytropis arctica; Oxytropis arctobia; Oxytropis borealis; Oxytropis maydelliana; Oxytropis sp.; Packera heterophylla; Papaver macounii; Papaver radicatum; Papaver sp.; Parmelia omphalodes var. glacialis; Parrya arctica; Parrya nudicaulis; Pedicularis albolabiata; Pedicularis arctoeuropaea; Pedicularis capitata; Pedicularis labradorica; Pedicularis lanata; Pedicularis langsdorfii; Pedicularis lapponica; Pedicularis oederi; Pedicularis sudetica; Pellia endivifolia; Peltigera aphthosa; Peltigera canina; Peltigera didactyla; Peltigera frippii; Peltigera leucophlebia; Peltigera malacea; Peltigera neopolydactyla; Peltigera polydactylon; Peltigera rufescens; Peltigera scabrosa; Peltigera sp.; Peltigera venosa; Pertusaria atra; Pertusaria bryontha; Pertusaria dactylina; Pertusaria glomerata; Pertusaria octomela; Pertusaria panyrga; Petasites frigidus; Phaeorrhiza nimbosa; Philonotis tomentella; Physconia muscigena; Placopsis gelida; Placynthium nigrum; Plagiochila asplenioides; Pleurozium schreberi; Poa abbreviata; Poa alpigena; Poa arctica var. lanata; Poa sp.; Pogonatum urnigerum; Pohlia beringiensis; Pohlia cruda; Pohlia drummondii; Pohlia nutans; Pohlia sp.; Polyblastia bryophila; Polyblastia sendtneri; Polyblastia terrestris; Polychidium muscicola; Polytrichastrum alpinum; Polytrichastrum alpinum var. alpinum; Polytrichum hyperboreum; Polytrichum piliferum; Polytrichum sp.;
    Type: Dataset
    Format: text/tab-separated-values, 70093 data points
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  • 8
    Publication Date: 2023-07-10
    Keywords: -; Active layer depth; Alaska, USA; Bare ground; Blue-green algae; Carbon/Nitrogen ratio; Deadhorse; Density; ENV; Environmental investigation; Equisetum; Event label; Forbs; Franklin_Bluffs; Grass, cover; Green_Cabin; Happy_Valley; HEIGHT above ground; Horizon; Howe_Island; Index; Isachsen2; Latitude 2; Lichen; Marchantiophyta; Moss; Mould_Bay2; Normalized Difference Vegetation Index; pH; Plant community; Queen Elizabeth Islands, Canada NWT; Sagwon; Sample code/label; Sand; Shrubs; Silt; Size fraction 〈 0.002 mm, clay; Snow thickness; Soil moisture; Vegetation, cover; Vegetation biomass; Zone, biogeographic
    Type: Dataset
    Format: text/tab-separated-values, 9758 data points
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  • 9
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    PANGAEA
    In:  Supplement to: Epstein, Howard E; Raynolds, Martha K; Walker, Donald A; Bhatt, Uma S; Tucker, Compton J; Pinzon, Jorge E (2012): Dynamics of aboveground phytomass of the circumpolar Arctic tundra during the past three decades. Environmental Research Letters, 7(1), 12 pp, https://doi.org/10.1088/1748-9326/7/1/015506
    Publication Date: 2023-12-13
    Description: Numerous studies have evaluated the dynamics of Arctic tundra vegetation throughout the past few decades, using remotely sensed proxies of vegetation, such as the normalized difference vegetation index (NDVI). While extremely useful, these coarse-scale satellite-derived measurements give us minimal information with regard to how these changes are being expressed on the ground, in terms of tundra structure and function. In this analysis, we used a strong regression model between NDVI and aboveground tundra phytomass, developed from extensive field-harvested measurements of vegetation biomass, to estimate the biomass dynamics of the circumpolar Arctic tundra over the period of continuous satellite records (1982-2010). We found that the southernmost tundra subzones (C-E) dominate the increases in biomass, ranging from 20 to 26%, although there was a high degree of heterogeneity across regions, floristic provinces, and vegetation types. The estimated increase in carbon of the aboveground live vegetation of 0.40 Pg C over the past three decades is substantial, although quite small relative to anthropogenic C emissions. However, a 19.8% average increase in aboveground biomass has major implications for nearly all aspects of tundra ecosystems including hydrology, active layer depths, permafrost regimes, wildlife and human use of Arctic landscapes. While spatially extensive on-the-ground measurements of tundra biomass were conducted in the development of this analysis, validation is still impossible without more repeated, long-term monitoring of Arctic tundra biomass in the field.
    Keywords: International Polar Year (2007-2008); IPY
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    Format: application/zip, 4 datasets
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  • 10
    Publication Date: 2024-01-24
    Keywords: Abbreviation; Comment; Counts; Coverage; International Polar Year 2007-2008; IPY-4; KH; Kharasavey2a; Method comment; MULT; Multiple investigations; Sample type; Species; Yamal Peninsula, northwestern Siberia
    Type: Dataset
    Format: text/tab-separated-values, 221 data points
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