HISTORICAL LANDSCAPE CONNECTIVITY AFFECTS PRESENT PLANT SPECIES DIVERSITY

By R. Lindborg, O. Eriksson. 2004

648 citations recorded by the source corpus.

Subfields: Ecological Modeling, Ecology, Evolution, Behavior and Systematics, Nature and Landscape Conservation

View Paper: https://www.semanticscholar.org/paper/393bc8e0d2932597d31dc48eb55dc8c98bab4ab0

How researchers see this paper

The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.

In Ecological Modeling

1. J. Pöyry
2. A. Helm
3. Risto Heikkinen
4. Z. Münzbergová
5. M. Pärtel
6. J. Ehrlén
7. M. Kuussaari
8. J. Buse

In Ecology, Evolution, Behavior and Systematics

1. A. Helm
2. Z. Münzbergová
3. R. Bommarco
4. Eelke Jongejans
5. Martin Hermy
6. M. Pärtel
7. M. Kuussaari
8. K. Piessens

In Nature and Landscape Conservation

1. A. Helm
2. Z. Münzbergová
3. M. Pärtel
4. R. Bommarco
5. M. Kuussaari
6. Risto Heikkinen
7. J. Pöyry
8. Eelke Jongejans

Citations in the corpus

• Habitat degradation impacts black howler monkey (Alouatta pigra) gastrointestinal microbiomes (2013, background): “Specifically, because habitat degradation leads to differences in available plant species and reductions in plant diversity (Benitez-Malvido and Martinez-Ramos, 2003; Vellend, 2003; Lindborg and Eriksson, 2004), we predict that howlers inhabiting disturbed habitats will exhibit signs of dysbiosis, s”
• Slow response of plant species richness to habitat loss and fragmentation. (2005, background): “Thus Lindborg & Eriksson (2004) found that the current species richness of Swedish seminatural grasslands is related to the connectivity of the sites 50–100 years ago, although species richness was not related to the historical areas of their study sites.”
• Dispersal, demography and spatial population models for conservation and control management (2008, background): “When the dispersal capacity of these plant species is included, these studies alarmingly show that the surviving plant populations have become isolated in an increasingly fragmented landscape, and that present patch occupancy levels are better explained by historical species distributions than by cu”
• Does the heathland flora in north-western Belgium show an extinction debt? (2006, background): “the number of heathland and forest species present in the recent period (1972‐2003), and the area of heathland and forest present on the different historic maps (cf. Lindborg and Eriksson, 2004 ).”
• Ecological theory provides strong support for habitat restoration (2017, background): “Similarly to extinction debt, that is often related to habitat spatial configuration and habitat fragmentation (Helm et al., 2006, Lindborg and Eriksson, 2004), colonisation credit can be attributed to factors acting at a landscape-scale.”
• Factors and scales potentially important for saproxylic beetles in temperate mixed oak forest (2007, background): “The predictive power of WKHOD1 suggests that earlier distribution of habitats may be important for species richness today, supporting theories regarding continuity of substrates (Nilsson and Baranowski, 1997) and connectivity of habitat patches (Lindborg and Eriksson, 2004).”
• Habitat fragmentation reduces grassland connectivity for both short‐distance and long‐distance wind‐dispersed forbs (2005, background): “The current small populations, especially at sites that were classified as non-habitat and on road verges in the AH area, probably reflect the past habitat distribution rather than the current one (as also found in Swedish semi-natural grasslands, Lindborg & Eriksson 2004).”
• Human influence lowers plant genetic diversity in communities with extinction debt (2009, background): “Extinction debt has been observed in European semi-natural grasslands (Lindborg & Eriksson 2004; Helm, Hanski & Pärtel 2006; Piessens & Hermy 2006; Gustavsson, Lennartsson & Emanuelsson 2007; Cousins 2009), ecosystems *Correspondence author.”
• Land Sparing Versus Land Sharing: Moving Forward (2014, background): “Current biodiversity partly reflects historic land uses (Dullinger et al. 2013)—for example, grassland communities in Sweden have been found to reflect past patterns of landscape connectivity, rather than current patterns (Lindborg & Eriksson 2004).”
• Long‐term spatial dynamics of Succisa pratensis in a changing rural landscape: linking dynamical modelling with historical maps (2006, background): “Current habitat occupancy or species richness unrelated to present-day connectivity has been demonstrated in other systems: for example, the site connectivity 50 and 100 years ago explained c. 50% of the among-site variation in species richness in semi-natural grasslands in Sweden (Lindborg & Erikss”
• Research, part of a Special Feature on Traditional Ecological Knowledge and Global Environmental Change Biocultural Refugia: Combating the Erosion of Diversity in Landscapes of Food Production (2013, background): “Our discussion employs the discourse of social memory and focuses on the carriers by which knowledge, experience, and practice of managing a local ecosystem and its services are captured, stored, revived, and transmitted through time (Barthel et al. 2010).”