Data from: Space-for-time substitution misleads projections of plant community and stand-structure development after disturbance in a slow-growing environment
Data files
Oct 03, 2024 version files 79.97 KB
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Plotdata_including_plant_species_occurrences.xlsx
63.80 KB
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README.md
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Abstract
Understanding and projecting ecosystem dynamics is a key goal for both basic science and applied ecosystem management. In ecosystems dominated by long-lived organisms such as forests, space-for-time substitutions (SFT) inferring temporal development from observations of study objects differing in age across space at a given time, also called chronosequences, are widely used as an alternative approach for long-term monitoring, in particular, to understand forest dynamics after stand-replacing disturbances. Uncertainties and challenges of SFT substitution, however, arise from violations of the underlying assumption that everything but time since disturbance is identical among the spatial sampling sites. Direct comparisons between true time series and SFT substitutions are still surprisingly rare. I resampled a 20-year-old SFT substitution study to check if this method accurately projects vegetation changes after major disturbances in primary subalpine conifer forests and to evaluate its conclusions for forest management. Two decades and a spatial scale of about 600 km² constitute spatial and temporal conditions for which little empirical evidence for the validity of SFT substitution exists. SFT suggested a strong shift away from old-growth plant community compositions after clearcutting with, misleadingly, no trend back over two decades. True temporal development, however, differed significantly from this expectation as it showed a directional trend back towards old-growth plant community compositions after the initial displacement. Compositional recovery is predicted to take 100-200 years in the studied ecosystem. Accordingly, several late seral forest floor herbs and bryophytes were still missing completely even 50 years after clearcutting. Non-constant climate, species pools, and management actions compromise the ability to reliably project temporal dynamics in plant community composition and stand structure by space-for-time substitutions, likely also for other scenarios than the studied subalpine conifer forests after stand-replacing disturbance. Long-term monitoring therefore is indispensable for understanding ecosystem dynamics, in particular in slow-growing and stressful environments. Management needs to consider the slow regeneration in its planning of rotation times and is advised to monitor and retain species indicative of old-growth conditions at the landscape level.
https://doi.org/10.5061/dryad.b5mkkwhp7
Description of the data and file structure
"Plot" runs from 1-48, with each plot occurring twice for being sampled in two different "Sampling Years", i.e., 2003 and 2023. Plot size is 100m².
"Disturbance type" is either "clearcut", "fire", or "windthrow". Disturbance type "no" indicates the absence of stand-replacing disturbances for > 100 years.
"Latitude" and "Longitude" are provided in decimal degrees with negative longitudes indicating west of Greenwich.
"Altitude" is elevation above sea level in meters.
"Tree canopy cover" and "Deadwood cover" are visual estimations from the ground with possible ranges from 0% to 100%.
"Species richness" includes all bryophytes and vascular plants except for epiphytes with aboveground cover in the respective plot.
"Basal area" is the tree stem area at 1.3 m height, calculated from measurements of the circumference of all trees reaching at least this height. Unit is m² per ha.
"Tree count" is the number of individuals irrespective of their size, meaning seedlings to full-grown trees. The number of trees smaller than 1.3 m is missing for the initial sampling of the reference_2003 stands (rows 34-49, plots 33-48 for the sampling year 2003, where the numbers represent only the trees >1.3m tall), but available for all other stands and times.
Columns O to EQ contains the presence/absence information of all species and each plot. Species are abbreviated to the first three letters of their genus names and species epitaphs, see below for full species names and species abbreviations. All specimens were identified at the genus level, but some specimens were not successfully identified at the species level. If, based on leaf and stem shape and morphology, those specimens clearly differed from all other identified species of the same genera, those other species were kept and the unidentified species treated as another species (Brachythecium spec, Carex spec, Cirsium spec, Hieracium spec, Pyrola spec, Salix spec (even twice), Vaccinium spec, Viola spec). If the unidentified species did not clearly differ from other identified species of the same genera or if there were no other species identified in that genera at all, all specimens were treated as one species (Antennaria spec, Arnica spec, Aster spec, Dicranum spec, Eurhynchium spec, Listera spec, Plagiothecium spec). With regards to the trees, abundance by species and diameter at 1.3 m height (DBH) were documented.
Species names (nomenclature according to Schoch et al., 2020):
| Species | Growth form | Abbreviation |
|---|---|---|
| Abies lasiocarpa Nutt. | tree | Abilas |
| Actaea rubra (Aiton) Willd. | herb | Actrub |
| Agrostis scabra Willd. | graminoid | Agrsca |
| Alnus alnobetula (Ehrh.) K.Koch | shrub | Alnaln |
| Alnus incana Moench | shrub | Alninc |
| Anaphalis margaritacea (L.) Benth. & Hook. f. | herb | Anamar |
| Antennaria Gaertn. | herb | Antspec |
| Arnica L. | herb | Arnspe |
| Aster L. | herb | Astspe |
| Athyrium filix-femina (L.) Roth | fern | Athfil |
| Aulacomnium palustre (Hedw.) Schwaegr. | bryophyte | Aulpal |
| Barbilophozia lycopodioides (Wallr.) Loeske | bryophyte | Barlyc |
| Brachythecium albicans (Hedw.) Schimp. | bryophyte | Braalb |
| Brachythecium erythrorrhizon Schimp. | bryophyte | Braery |
| Brachythecium hylotapetum B.L.Higinb. & N.L.Higinb. | bryophyte | Brahyl |
| Brachythecium salebrosum (Hoffm. ex F.Weber & D.Mohr) Schimp. | bryophyte | Brasal |
| Brachythecium Schimp. | bryophyte | Braspe |
| Brewerimitella breweri (A.Gray) R.A.Folk & Y.Okuyama | herb | Mitbre |
| Bromus vulgaris Shear | graminoid | Brovul |
| Calamagrostis canadensis (Michx.) P.Beauv. | graminoid | Calcan |
| Carex bebbii Olney ex Fernald | graminoid | Carbeb |
| Carex canescens L. | graminoid | Carcan |
| Carex L | graminoid | Carspe |
| Carex magellanica Lam. | graminoid | Carmag |
| Carex rossii Boott | graminoid | Carros |
| Cassiope mertensiana (Bong.) G.Don | shrub | Casmer |
| Ceratodon purpureus (Hedw.) Brid. | bryophyte | Cerpur |
| Chamaenerion angustifolium (L.) Scop. | herb | Chaang |
| Chimaphila umbellata W.P.C.Barton | shrub | Chiumb |
| Cirsium Mill. | herb | Cirspe |
| Cirsium vulgare (Savi) Ten. | herb | Cirvul |
| Clintonia uniflora (Menzies ex Schult. & Schult.f.) Kunth | herb | Cliuni |
| Cornus canadensis L. | herb | Corcan |
| Dicranum Hedw. | bryophyte | Dicspe |
| Diphasiastrum complanatum (L.) Holub | herb | Dipcom |
| Dryopteris expansa (C.Presl) Fraser-Jenk. & Jermy | fern | Dryexp |
| Elymus glaucus Buckley | graminoid | Elygla |
| Epilobium ciliatum Raf. | herb | Epilcil |
| Equisetum arvense L. | herb | Equarv |
| Eurhynchium Bruch & Schimp. | bryophyte | Eurspe |
| Festuca occidentalis Hook. | graminoid | Fesocc |
| Fragaria virginiana Mill. | herb | Fravir |
| Funaria hygrometrica Hedw. | bryophyte | Funhyg |
| Galium triflorum Michx. | herb | Galtri |
| Goodyera oblongifolia Raf. | herb | Gooobl |
| Gymnocarpium dryopteris (L.) Newman | fern | Gymdry |
| Hieracium albiflorum Hook. | herb | Hiealb |
| Hieracium L. | herb | Hiespe |
| Hylocomiadelphus triquetrus (Hedw.) Ochyra & Stebel | bryophyte | Hyltri |
| Lactuca canadensis L. | herb | Laccan |
| Larix occidentalis Nutt. | tree | Larocc |
| Leucanthemum vulgare Lam. | herb | Leuvul |
| Lilium columbianum Leichtlin | herb | Lilcol |
| Linnaea borealis L. | shrub | Linbor |
| Listera R.Br. | herb | Lisspe |
| Lonicera involucrata (Richardson) Banks ex Spreng. | shrub | Loninv |
| Lonicera utahensis S. Watson | shrub | Lonuta |
| Lupinus arcticus S.Watson | herb | Luparc |
| Luzula parviflora Desv. | graminoid | Luzpar |
| Maianthemum racemosum Link | herb | Mairac |
| Marchantia polymorpha L. | bryophyte | Marpol |
| Mnium spinulosum Bruch & Schimp. | bryophyte | Mnispi |
| Neottia cordata Rich. | herb | Neocor |
| Orthilia secunda (L.) House | herb/shrub | Ortsec |
| Osmorhiza berteroi DC. | herb | Osmber |
| Packera pseudaurea (Rydb.) W.A.Weber & Á.Löve | herb | Pacpse |
| Parnassia fimbriata K.D.Koenig | herb | Parfim |
| Paxistima myrsinites (Pursh) Raf. | shrub | Paxmyr |
| Pedicularis bracteosa Benth. | herb | Pedbra |
| Pedicularis racemosa Douglas ex Benth. | herb | Pedrac |
| Philonotis fontana (Hedw.) Brid. | bryophyte | Phifon |
| Picea glauca (Moench) Voss x engelmannii Engelm. | tree | Picgla |
| Pilosella aurantiaca (L.) F.W.Schultz & Sch.Bip. | herb | Hieaur |
| Pinus contorta var. latifolia Engelm. | tree | Pincon |
| Pinus monticola Douglas ex D. Don | tree | Pinmon |
| Plagiomnium affine (Blandow ex Funck) T.J.Kop. | bryophyte | Plaaff |
| Plagiothecium Bruch & Schimp. | bryophyte | Plaspe |
| Platanthera aquilonis Sheviak | herb | Plaaqu |
| Pleurozium schreberi (Brid.) Mitt. | bryophyte | Plesch |
| Polytrichum formosum Hedw. | bryophyte | Polfor |
| Polytrichum juniperinum Hedw. | bryophyte | Poljun |
| Polytrichum piliferum Hedw. | bryophyte | Polpil |
| Populus balsamifera L. | tree | Popbal |
| Populus tremuloides Michx. | tree | Poptre |
| Pseudotsuga menziesii (Mirb.) Franco | tree | Psemen |
| Ptilium crista-castrensis (Hedw.) De Not. | bryophyte | Pticri |
| Ptychostomum capillare (Hedw.) D.T.Holyoak & N.Pedersen | bryophyte | Ptycap |
| Pyrola asarifolia Michx. | herb | Pyrasa |
| Pyrola chlorantha Sw. | herb | Pyrchl |
| Pyrola L. | herb | Pyrspe |
| Racomitrium lanuginosum (Hedw.) Brid. | bryophyte | Raclan |
| Ranunculus uncinatus D. Don ex G. Don | herb | Ranunc |
| Rhizomnium punctatum (Hedw.) T.J.Kop. | bryophyte | Rhipun |
| Rhododendron albiflorum Hook. | shrub | Rhoalb |
| Rhododendron menziesii Craven | shrub | Menfer |
| Rhytidiadelphus squarrosus (Hedw.) Warnst. | bryophyte | Rhysqu |
| Ribes lacustre (Pers.) Poir. | shrub | Riblac |
| Rubus idaeus L. | shrub | Rubida |
| Rubus parviflorus Nutt. | shrub | Rubpar |
| Rubus pedatus Sm. | herb/shrub | Rubped |
| Salix L. | shrub | Salsp1 |
| Salix L. | shrub | Salsp3 |
| Salix scouleriana Barratt ex Hook. | shrub | Salsco |
| Sambucus racemosa L. | shrub | Samrac |
| Senecio triangularis Hook. | herb | Sentri |
| Sorbus scopulina Greene | shrub | Sorsco |
| Sorbus sitchensis M. Roem. | shrub | Sorsit |
| Spinulum annotinum (L.) A.Haines | herb | Spiann |
| Spiraea betulifolia Pall. | shrub | Spibet |
| Stellaria umbellata Turcz. ex Kar. & Kir. | herb | Steumb |
| Streptopus amplexifolius (L.) DC. | herb | Streamp |
| Streptopus lanceolatus Reveal | herb | Strelan |
| Taraxacum officinale G.H. Weber ex Wiggers | herb | Taroff |
| Tellima grandiflora Douglas ex Lindl. | herb | Telgra |
| Thalictrum occidentale A.Gray | herb | Thaocc |
| Thuja plicata Donn ex D. Don | tree | Thupli |
| Tiarella trifoliata var. unifoliata (Hook.) Kurtz | herb | Tiatri |
| Torreyochloa pallida var. pauciflora (J.S.Presl) J.I.Davis | graminoid | Torpau |
| Trifolium hybridum L. | herb | Trihyb |
| Trillium ovatum Pursh | herb | Triova |
| Trisetum cernuum subsp. canescens (Buckley) Calder & Roy L.Taylor | graminoid | Triscan |
| Trollius albiflorus (A.Gray) Rydb. | herb | Troalb |
| Tsuga heterophylla Sarg. | tree | Tsuhet |
| Vaccinium L. | shrub | Vacspe |
| Vaccinium membranaceum Dougl. ex Torr. | shrub | Vacmem |
| Vaccinium ovalifolium Sm. | shrub | Vacova |
| Vaccinium scoparium Leiberg ex Coville | shrub | Vacsco |
| Valeriana sitchensis Bong. | herb | Valsit |
| Veratrum viride Aiton | herb | Vervir |
| Veronica beccabunga L. | herb | Verbec |
| Viola glabella Nutt. | herb | Viogla |
| Viola orbiculata (A.Gray) Geyer ex B.D.Jacks. | herb | Vioorb |
| Viola L. | herb | Viospe |
This dataset contains plot-level information and plant species occurrences from 48 plots from a subalpine, boreal forest region in southern British Columbia, Canada, sampled as a chronosequence of primary forests and development after stand-replacing disturbance (clearcutting, with young and old clear-cuts differing by 20 years in time). Initial sampling took place in 2003, and resampling of all plots took place in 2023. The 20 years of true temporal development can therefore be compared to a 20-year chronosequence (space for time) approach. See the main publication for more details.
