Abstract:A lthough islands cover only ~5% of the global land area, they support ~20% of terrestrial plant and vertebrate species (Courchamp et al. 2014). Insular species are particularly vulnerable to extinction; one-third of critically endangered species and nearly two-thirds of recent extinctions consisted of species endemic to islands (Tershy et al. 2015), and these declines may have impacts on Indigenous peoples (Lyver et al. 2019). Several interacting factors contribute to this vulnerability, including invasions b… Show more
“…Extreme flooding may also alter river morphology which may change habitat quality and availability (Death et al 2015). Measured impacts are summarised in Table 2, but substantial knowledge gaps remain, particularly when impacts are indirect and have complicated mechanisms (Macinnis-Ng et al 2021). New Zealand's freshwater biota is often described as depauperate with a high degree of habitat and trophic generalism owing to life-history evolution in geographic isolation and unpredictable, variable climatic conditions (Winterbourn et al 1981).…”
Section: Freshwater Environmentsmentioning
confidence: 99%
“…Similarly, the ability to migrate and disperse will largely affect how species can adapt to changing conditions, and this varies widely between species and systems in New Zealand (McDowall 2006). Meanwhile, many freshwater ecosystems are highly impacted by existing land-use change and water abstraction which will exacerbate future climate changes due to global warming (Robertson et al 2016;Macinnis-Ng et al 2021).…”
Section: Freshwater Environmentsmentioning
confidence: 99%
“…Details of changes in temperature, precipitation patterns, wind, storms, and other climate factors are expanded in regional modelling produced by Ministry for the Environment (2016) and Ministry for the Environment and Stats NZ (2020) with some additional context provided by Hopkins et al (2015). While considering past climates is important for understanding potential impacts of future climate change (McGlone et al 2010;McGlone & Walker 2011), we confine the scope of this review to current and future climate because interacting factors such as invasive species and habitat fragmentation were not a feature of past climates (Macinnis-Ng et al 2021).…”
While global climate change is impacting biota across the world, New Zealand's maritime climate is highly variable and relatively mild, so climate change is sometimes seen as a minimal threat to species and ecosystems especially in comparison to the more immediate threat of invasive species. However, climate change will alter rainfall patterns, increase the incidence and severity of extreme events, and gradually increase temperatures which will all modify terrestrial, freshwater, and marine systems. Our comprehensive review of reported climate change impacts in New Zealand indicates that most measured impacts to date are due to indirect impacts (such as exacerbation of invasive species impacts) and most are in the marine realm. Ocean acidification and marine heatwaves are particularly problematic for calcareous organisms and algae respectively. Other notable impacts include thermal squeeze in the alpine zone and impacts of drought on freshwater fish. Very small populations of rare and threatened species can be very vulnerable to extreme events (e.g. fire, floods). While the evidence for climate change impacts is sparse in some regions and for some ecosystems, we encourage ongoing monitoring to identify processes of decline that may need to be mitigated. We identify five key research needs to improve our understanding of the threat of climate change to the biodiversity of Aotearoa New Zealand.
“…Extreme flooding may also alter river morphology which may change habitat quality and availability (Death et al 2015). Measured impacts are summarised in Table 2, but substantial knowledge gaps remain, particularly when impacts are indirect and have complicated mechanisms (Macinnis-Ng et al 2021). New Zealand's freshwater biota is often described as depauperate with a high degree of habitat and trophic generalism owing to life-history evolution in geographic isolation and unpredictable, variable climatic conditions (Winterbourn et al 1981).…”
Section: Freshwater Environmentsmentioning
confidence: 99%
“…Similarly, the ability to migrate and disperse will largely affect how species can adapt to changing conditions, and this varies widely between species and systems in New Zealand (McDowall 2006). Meanwhile, many freshwater ecosystems are highly impacted by existing land-use change and water abstraction which will exacerbate future climate changes due to global warming (Robertson et al 2016;Macinnis-Ng et al 2021).…”
Section: Freshwater Environmentsmentioning
confidence: 99%
“…Details of changes in temperature, precipitation patterns, wind, storms, and other climate factors are expanded in regional modelling produced by Ministry for the Environment (2016) and Ministry for the Environment and Stats NZ (2020) with some additional context provided by Hopkins et al (2015). While considering past climates is important for understanding potential impacts of future climate change (McGlone et al 2010;McGlone & Walker 2011), we confine the scope of this review to current and future climate because interacting factors such as invasive species and habitat fragmentation were not a feature of past climates (Macinnis-Ng et al 2021).…”
While global climate change is impacting biota across the world, New Zealand's maritime climate is highly variable and relatively mild, so climate change is sometimes seen as a minimal threat to species and ecosystems especially in comparison to the more immediate threat of invasive species. However, climate change will alter rainfall patterns, increase the incidence and severity of extreme events, and gradually increase temperatures which will all modify terrestrial, freshwater, and marine systems. Our comprehensive review of reported climate change impacts in New Zealand indicates that most measured impacts to date are due to indirect impacts (such as exacerbation of invasive species impacts) and most are in the marine realm. Ocean acidification and marine heatwaves are particularly problematic for calcareous organisms and algae respectively. Other notable impacts include thermal squeeze in the alpine zone and impacts of drought on freshwater fish. Very small populations of rare and threatened species can be very vulnerable to extreme events (e.g. fire, floods). While the evidence for climate change impacts is sparse in some regions and for some ecosystems, we encourage ongoing monitoring to identify processes of decline that may need to be mitigated. We identify five key research needs to improve our understanding of the threat of climate change to the biodiversity of Aotearoa New Zealand.
“…Islands such as Moutohorā with high conservation and cultural values, that also carry high burn probability relative to their area, even with management of human activity are likely to become under increased threat due to climate change (Towns et al 2012;Sothieson et al 2016;Macinnis-Ng et al 2021). Modelling and research that can produce and improve fire burn probability mapping will have increased value for conservation, resource and cultural site managers.…”
Aotearoa New Zealand's conservation management has had a strong focus on offshore islands, though this investment is at risk from human-influenced factors such as biosecurity incursions and wildfire. During the last century several wildfires have occurred on Moutohorā (Whale Island), Bay of Plenty, which is a location for six threatened plant and three threatened animal species. Conservation and cultural management on Moutohorā over the last several decades has restored the island to become the most densely vegetated it has been since before humans arrived, albeit with a very different composition. The Prometheus fire-growth simulation model was used to produce a series of deterministic fire extent maps, which were compiled into seasonal burn probability maps. The average simulated fire extent was 53.2 ha, with a maximum area of 129.9 ha (or approx. 84% of the entire island), with 23% of fires not growing past 0.01 ha. Fires that start in summer, the western end of the island, and in mānuka and/or kānuka had the highest mean and maximum fire extent. Burn probability maps are a key step in quantifying the spatial fire risk for important conservation locations such as Moutohorā.
“…These are “natural laboratories ” (Warren et al, 2015; Whittaker et al, 2017) and suitable models to examine persistence strategies because plants with limited dispersal on steadily isolated islands tend to exhibit adaptive strategies to successfully survive (Cody & Overton, 1996; Conti et al, 2021; Ottaviani et al, 2020a). At the same time, insular systems are particularly vulnerable to species extinctions linked to environmental changes (Courchamp et al, 2014; Macinnis-Ng et al, 2021; Veron et al, 2019). The study of plant functional traits in insular systems has boosted in recent years, providing important insights into the eco-evolutionary dynamics of these systems (e.g.…”
1. Species extinction risk at local scales can be partially offset by strategies promoting in-situ persistence. We explored how persistence-related traits of clonal and non-clonal plants in temperate dry grasslands respond intra- and interspecifically to variation in environmental conditions (soil, climate) and insularity.
2. We focused on edaphic island specialist species, hypothesizing that plants experiencing harsh soil environments and strong insularity are distinguished by traits supporting enhanced persistence, such as small stature, long lifespan and resource-conservative strategies. We used linear mixed-effect models and bivariate ordinary least squares linear models to explore the response of species triats to environmental and biogeographic predictors.
3. We found general support for this hypothesis. Soil properties and insularity emerged as the most important drivers of trait patterns. However, clonal species showed more consistent responses to variation in environmental conditions and insularity than non-clonal plants, which were characterized by distinct species-specific responses.
4. Soil properties and insularity confirmed their major role in shaping the persistence strategies of edaphic island plant species. These drivers may exert their effect on specific functions (e.g. belowground resource conservation captured by BDMC). Additionally, we unambiguously identified that clonal species had different persistence strategies than non-clonal ones.
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