combining long-term plot resurvey and historical management data
Transkript
Towards an integrated research platform of the Czech forest vegetation: combining long-term plot resurvey and historical management data Radim Hédl, Péter Szabó, Martin Kopecký, Markéta Chudomelová, Ondřej Vild, Martin Macek, Petr Petřík, Silvie Suchánková, Tadeáš Štěrba, Václav Zouhar Long-term vegetation change: the black-box we would like to open Drivers of change t0 time ? linearity ? forecasting t1 The four oft-quoted drivers of forest vegetation change in the Anthropocene 1. Management + land-use 2. Atmospheric deposition 3. Ungulates (big herbivores) 4. Climate change http://www.metmuseum.org/toah/works-of-art/19.73.209 Resurvey of forest vegetation plots in the Czech Republic • potentially 60 thousand plots from the 1930s–1980s • first resampling studies in the 1990s • semi-permanent plots approximate location by old map, topography, coordinates, etc. 2015 Re-survey of forest vegetation plots in the Czech Republic Plots established during the forestry typology survey • • • • • • Forest Management Institute (UHUL) 1951-1980 the main sampling wave 91 authors 39,000 plots; 3 per 100 ha 59% in non-natural forests (regularly managed) digitalized (Turboveg, Access) 2015 Resampled forest plots, Czech Rep. 1991-2015, mainly 2012-2015 About 1500 plots (3000 samples); 3-5(-8) a day 2016-2018 number of plots Resampled forest plots, Czech Rep. sampling year original samples repeated samples Koda Sidonie Polom es ies, e tr ec p (s ) e r u t c u str > positioning: original maps ion t a c i f ti n e d i on i plot t p i r sc e d e sit es i t r e p o r p soil , n o i t p i r c s e (profile d is) s y l a n a l chemica c o s o t y ph v é e rel l a c i g o io l An example: Rychlebské hory Rychlebské hory 280 km2 About 400 plots from 1958-1960, partly 1964-1965 Single authorship 165 plots revisited in 2014-2015 129 plots resampled (R. Hédl, M. Chudomelová) elevation (m a.s.l.) Plot size usually 500 m2, circular Elevation 370-985 m 1050 Alluvial to spruce forests 950 850 750 650 550 450 350 0 10 20 30 40 50 60 70 80 plot rank Resampling: only when vegetation not completely altered 2014: 72 plots resampled, 22 cancelled) 2015: 57 plots resampled, 14 cancelled) 129 plots resampled: 72% 36 plots cancelled: 28% 90 100 110 120 Species diversity: obvious authorship bias number of species per plot plot size 500 m2 druhů nr.Počet of species 80 70 80 75 70 65 60 60 50 50 40 40 30 30 20 20 10 10 0 0 60 57 57 staré old nové new nové staré 0 10 20 30 40 50 60 70 80 90 100 plot rank Who cares about averages? They may be under/overestimates. 110 120 Vegetation coverage: another area of strong authorship bias 2 sites, resurveyed forest plots, CZ 60 40 20 coverage (%) zapoj odhadnuty coverage (%) 80 Tree layer coverage 1965 2012 Did the forest canopy become sparser? The opposite is true (analysis of aerial photos, EIV-L) Multiple-site resurvey • 15 sites, 1806 samples • 1953–2014 • 165-950 m asl. species richness Boří les lowland Hodonínská Dúbrava Bzenecká Dúbrava Kapánsko Polabí Milovice Wood Děvín Wood = abandoned coppices Milovický les Krumlovský les Ždánický les upland Děvín Chřiby Středohoří-Lovosice Středohoří-Litoměřice Bílé Karpaty Rychlebské hory highland Velká Javořina -30 -20 -10 0 10 20 30 40 No. species per plot (mean, SD) Multiple-site resurvey • 15 sites, 1806 samples • 1953–2014 • 165-950 m asl. EIV nutrients Boří les lowland Hodonínská Dúbrava Bzenecká Dúbrava Kapánsko Polabí Milovice Wood Děvín Wood = abandoned coppices Milovický les Krumlovský les Ždánický les upland Děvín Chřiby Středohoří-Lovosice Středohoří-Litoměřice Bílé Karpaty Rychlebské hory highland Velká Javořina -3 -2 -1 0 1 2 3 Plot-wise change (mean, SD) Which driver? We do not really know. The case of the Milovice Wood (S Moravia). 1. long-term semi-permanent vegetation plot resurveys 2. estimation of environmental change by Ellenberg I.V. Chytrý & Danihelka, 1993 Folia Geobotanica … it’s deer! Hédl et al., 2010 Diversity and Distributions … no, it’s coppicing abandonment! 1953; 1992; 2006 Forest management • The strongest driver of vegetation changes • Includes land-use change, direct management, ungulates (large herbivores) Much of the interpretation of long-term change is related to management. …but there is little primary data-based evidence Historical forest use database for Moravia 4 historians, 2 GIS-experts MS Access 40,000 entries ERC-LONGWOOD www.longwood.cz 11th-20th century hunting 17th hunting 1940s Coppicing, 19th century Coppicing, 18th>19th century change Forest pasture Litter raking Hay cutting Management effects Legacy Events t0 time t1 Management influences vegetation at any time (past / present…). Management leaves a legacy of its influence. Plot-related management history 8 parameters Both „legacy“ and „event“ (related to sampling date) Archival survey (written documents, maps) Two periods: 1: before 1850 (lower data quality) 2: after 1850 (good data quality) Parameter Type Period Management form categorial 1, 2 Tree species composition species, % 1, 2 Stand age years 2 Last cutting type and intensity categorial 2 Tree density / timber volume nr./ha, m3/ha 1, 2 Non-timber uses categorial 1, 2 Game density nr./ha 2 Game composition categorial, % 1, 2 The effects of historical management • Requires thorough archival research (primary data) • Legacy > long-lasting effects > potential for vegetation databases • Events > actual influence at any time > potential for resurveys
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