TY - JOUR
T1 - Predicting diversity changes in subalpine moorland ecosystems based on geometry of species distributions and realistic area loss
AU - Makishima, Daichi
AU - Ishii, Naohiro
AU - Sutoh, Rui
AU - Goto, Akihito
AU - Kawai, Yutaka
AU - Taniguchi, Hayami
AU - Uchida, Kei
AU - Shimazaki, Masaya
AU - Nakashizuka, Toru
AU - Suyama, Yoshihisa
AU - Hikosaka, Kouki
AU - Sasaki, Takehiro
N1 - Funding Information:
This work was financially supported by a Fostering Joint International Research A (No. 19KK0393) and a Grant‐in‐Aid for Scientific Research B (No. 18H02221 and No. 20H04380) to Takehiro Sasaki from the Ministry of Education, Culture, Sports, Science and Technology of Japan.
Publisher Copyright:
© 2022 International Association for Vegetation Science.
PY - 2022/9/1
Y1 - 2022/9/1
N2 - Question: How does plant species richness respond to simulated area loss based on the realistic geometry of area loss in subalpine moorland ecosystems?. Location: Hakkoda mountain range, Aomori, Japan. Methods: We constructed species distribution models based on relationships between species distributions and environmental conditions in subalpine moorland ecosystems. We then simulated moorland area loss based on the realistic geometry of area loss from the past (1967) to the present (2019) to predict future changes in plant diversity. Here, we defined the realistic geometry of area loss as the plausible spatial pattern of future habitat loss. Finally, we analyzed how the rate of species loss in response to the realistic area loss can be explained by a range of factors including spatial patterns in species distributions, total number of species present, and environmental variables for the focal moorland. Results: Within each moorland site, areas prone or those less prone to be lost were distributed non-randomly at a local scale. In general, the patterns of species loss caused by the realistic area loss differed from those caused by random area loss. At most sites, realistic area loss caused a relatively small decline in species richness up to a certain threshold of area loss, and accelerating decline thereafter. None of the factors can explain the rate of decrease in species richness caused by the realistic area loss. At the species level, however, species with lower occurrence rates at a given site can be lost earlier than those with higher occurrence rates by the realistic area loss. Conclusions: Patterns of habitat loss and species distributions are not spatially random, and the classical approach based on the species–area relationship assuming random area loss can thus either under- or overestimate the risk of species loss.
AB - Question: How does plant species richness respond to simulated area loss based on the realistic geometry of area loss in subalpine moorland ecosystems?. Location: Hakkoda mountain range, Aomori, Japan. Methods: We constructed species distribution models based on relationships between species distributions and environmental conditions in subalpine moorland ecosystems. We then simulated moorland area loss based on the realistic geometry of area loss from the past (1967) to the present (2019) to predict future changes in plant diversity. Here, we defined the realistic geometry of area loss as the plausible spatial pattern of future habitat loss. Finally, we analyzed how the rate of species loss in response to the realistic area loss can be explained by a range of factors including spatial patterns in species distributions, total number of species present, and environmental variables for the focal moorland. Results: Within each moorland site, areas prone or those less prone to be lost were distributed non-randomly at a local scale. In general, the patterns of species loss caused by the realistic area loss differed from those caused by random area loss. At most sites, realistic area loss caused a relatively small decline in species richness up to a certain threshold of area loss, and accelerating decline thereafter. None of the factors can explain the rate of decrease in species richness caused by the realistic area loss. At the species level, however, species with lower occurrence rates at a given site can be lost earlier than those with higher occurrence rates by the realistic area loss. Conclusions: Patterns of habitat loss and species distributions are not spatially random, and the classical approach based on the species–area relationship assuming random area loss can thus either under- or overestimate the risk of species loss.
KW - climate change
KW - generalized additive model
KW - global warming
KW - historical landscape
KW - kriging
KW - random forest
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U2 - 10.1111/jvs.13150
DO - 10.1111/jvs.13150
M3 - Article
AN - SCOPUS:85141209104
SN - 1100-9233
VL - 33
JO - Journal of Vegetation Science
JF - Journal of Vegetation Science
IS - 5
M1 - e13150
ER -