Nélida R. Villaseñor

Dr. Nélida R. Villaseñor

orcid

Research Focus & Metrics

Academic Career Length

14Years (2013-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

View All Publications
17 April 2014 in PLOS ONE
Verified
Journal Article
Open access
PDF file
DDDon A Driscoll
Don A Driscoll
SBSam C Banks
Sam C Banks
PBPhilip S Barton
Philip S Barton
KIKaren Ikin
Karen Ikin
PLPia Lentini
Pia Lentini
MWMartin J Westgate
Martin J Westgate
Dispersal knowledge is essential for conservation management, and demand is growing. But are we accumulating dispersal knowledge at a pace that can meet the demand? To answer this question we tested for changes in dispersal data collection and use over time. Our systematic review of 655 conservation-related publications compared five topics: climate change, habitat restoration, population viability analysis, land planning (systematic conservation planning) and invasive species. We analysed temporal changes in the: (i) questions asked by dispersal-related research; (ii) methods used to study dispersal; (iii) the quality of dispersal data; (iv) extent that dispersal knowledge is lacking, and; (v) likely consequences of limited dispersal knowledge. Research questions have changed little over time; the same problems examined in the 1990s are still being addressed. The most common methods used to study dispersal were occupancy data, expert opinion and modelling, which often provided indirect, low quality information about dispersal. Although use of genetics for estimating dispersal has increased, new ecological and genetic methods for measuring dispersal are not yet widely adopted. Almost half of the papers identified knowledge gaps related to dispersal. Limited dispersal knowledge often made it impossible to discover ecological processes or compromised conservation outcomes. The quality of dispersal data used in climate change research has increased since the 1990s. In comparison, restoration ecology inadequately addresses large-scale process, whilst the gap between knowledge accumulation and growth in applications may be increasing in land planning. To overcome apparent stagnation in collection and use of dispersal knowledge, researchers need to: (i) improve the quality of available data using new approaches; (ii) understand the complementarities of different methods and; (iii) define the value of different kinds of dispersal information for supporting management decisions. Ambitious, multi-disciplinary research programs studying many species are critical for advancing dispersal research.

15 September 2015 in Ecological Management & Restoration
Verified
Journal Article
Closed access
PDF file
KIKaren Ikin
Karen Ikin
DRDarren S. Le Roux
Darren S. Le Roux
LRLaura Rayner
Laura Rayner
NVNélida R. Villaseñor
Nélida R. Villaseñor
KEKathy Eyles
Kathy Eyles
DLDavid B Lindenmayer
David B Lindenmayer

1 March 2020 in Urban Forestry & Urban Greening
Verified
Journal Article
Closed access
NVNélida R. Villaseñor
Nélida R. Villaseñor
LCLuna A. Chiang
Luna A. Chiang
HHH. Jaime Hernández
H. Jaime Hernández
MEMartín A.H. Escobar
Martín A.H. Escobar

8 May 2014 in PLOS ONE
Verified
Journal Article
Open access
PDF file
NVNélida R. Villaseñor
Nélida R. Villaseñor
DDDon A. Driscoll
Don A. Driscoll
MEMartín A. H. Escobar
Martín A. H. Escobar
PGPhilip Gibbons
Philip Gibbons
DLDavid B. Lindenmayer
David B. Lindenmayer
With accelerating rates of urbanization worldwide, a better understanding of ecological processes at the wildland-urban interface is critical to conserve biodiversity. We explored the effects of high and low-density housing developments on forest-dwelling mammals. Based on habitat characteristics, we expected a gradual decline in species abundance across forest-urban edges and an increased decline rate in higher contrast edges. We surveyed arboreal mammals in sites of high and low housing density along 600 m transects that spanned urban areas and areas turn on adjacent native forest. We also surveyed forest controls to test whether edge effects extended beyond our edge transects. We fitted models describing richness, total abundance and individual species abundance. Low-density housing developments provided suitable habitat for most arboreal mammals. In contrast, high-density housing developments had lower species richness, total abundance and individual species abundance, but supported the highest abundances of an urban adapter (Trichosurus vulpecula). We did not find the predicted gradual decline in species abundance. Of four species analysed, three exhibited no response to the proximity of urban boundaries, but spilled over into adjacent urban habitat to differing extents. One species (Petaurus australis) had an extended negative response to urban boundaries, suggesting that urban development has impacts beyond 300 m into adjacent forest. Our empirical work demonstrates that high-density housing developments have negative effects on both community and species level responses, except for one urban adapter. We developed a new predictive model of edge effects based on our results and the literature. To predict animal responses across edges, our framework integrates for first time: (1) habitat quality/preference, (2) species response with the proximity to the adjacent habitat, and (3) spillover extent/sensitivity to adjacent habitat boundaries. This framework will allow scientists, managers and planners better understand and predict both species responses across edges and impacts of development in mosaic landscapes.

1 January 2018 in Urban Forestry & Urban Greening
Verified
Journal Article
Closed access
HHH. Jaime Hernández
H. Jaime Hernández
NVNélida R. Villaseñor
Nélida R. Villaseñor

4 July 2019 in Urban Ecosystems
Verified
Journal Article
Closed access
PDF file
NVNélida R. Villaseñor
Nélida R. Villaseñor
MEMartín A. H. Escobar
Martín A. H. Escobar