Abstract:Natural disturbance regimes-cycles of fire, flood, drought or other events-range from highly predictable (disturbances occur regularly in time or in concert with a proximate cue) to highly unpredictable. While theory predicts how populations should evolve under different degrees of disturbance predictability, there is little empirical evidence of how this occurs in nature. Here, we demonstrate local adaptation in populations of an aquatic insect occupying sites along a natural gradient of disturbance predictab… Show more
“…Organisms might not be able to adapt and respond by their resilience and resistance abilities to the new disturbance regimes resulting from climate change that surpass the intensity, frequency, or duration thresholds of natural disturbances (Lytle, 2007;Lytle et al, 2008). The ability of biota to cope with these disturbances is very poorly understood, which weakens the predictive accuracy of the ecological responses.…”
Section: Ecological Response To Disturbancementioning
Freshwater species worldwide are experiencing dramatic declines partly attributable to ongoing climate change. It is expected that the future effects of climate change could be particularly severe in mediterranean-climate regions (med-regions), which host many endemic species already under great stress from the high level of human development. In this article, we review the climate and climate-induced changes in streams of med-regions and the responses of stream biota, focusing on both observed and anticipated biological responses.We also discuss current knowledge gaps and conservation challenges. Expected climate alterations have already been observed in the last decades, and include: increased annual average air temperatures; decreased annual average precipitation; hydrologic alterations; and an increase in frequency, intensity, and duration of extreme events, such as floods, droughts, and fires. Recent observations, which are concordant with forecasts built, show stream biota of med-regions when facing climate changes tend to be displaced towards higher elevations and upper latitudes, communities tend to change their composition and homogenize, while some life-history traits seem to provide biota with resilience and resistance to adapt to the new conditions (as being short -lived, small, and resistant to low streamflow and desiccation). Nevertheless, such organism's responses may be insufficient to cope with current and future environmental changes. Accurate forecasts of biotic changes and possible adaptations are difficult to obtain in med-regions mainly because of the difficulty of distinguishing disturbances due to natural variability from the effects of climate change, particularly regarding hydrology. Long-term studies are needed to disentangle such variability and improve knowledge regarding the ecological responses and detection of earlywarning signals to climate change. Investments should focus on taxa beyond fish and macroinvertebrates, and in covering the less studied regions of Chile and South Africa.
3Scientists, policy makers, and water managers must be involved in the climate change dialogue because the freshwater conservation concerns are huge.
“…Organisms might not be able to adapt and respond by their resilience and resistance abilities to the new disturbance regimes resulting from climate change that surpass the intensity, frequency, or duration thresholds of natural disturbances (Lytle, 2007;Lytle et al, 2008). The ability of biota to cope with these disturbances is very poorly understood, which weakens the predictive accuracy of the ecological responses.…”
Section: Ecological Response To Disturbancementioning
Freshwater species worldwide are experiencing dramatic declines partly attributable to ongoing climate change. It is expected that the future effects of climate change could be particularly severe in mediterranean-climate regions (med-regions), which host many endemic species already under great stress from the high level of human development. In this article, we review the climate and climate-induced changes in streams of med-regions and the responses of stream biota, focusing on both observed and anticipated biological responses.We also discuss current knowledge gaps and conservation challenges. Expected climate alterations have already been observed in the last decades, and include: increased annual average air temperatures; decreased annual average precipitation; hydrologic alterations; and an increase in frequency, intensity, and duration of extreme events, such as floods, droughts, and fires. Recent observations, which are concordant with forecasts built, show stream biota of med-regions when facing climate changes tend to be displaced towards higher elevations and upper latitudes, communities tend to change their composition and homogenize, while some life-history traits seem to provide biota with resilience and resistance to adapt to the new conditions (as being short -lived, small, and resistant to low streamflow and desiccation). Nevertheless, such organism's responses may be insufficient to cope with current and future environmental changes. Accurate forecasts of biotic changes and possible adaptations are difficult to obtain in med-regions mainly because of the difficulty of distinguishing disturbances due to natural variability from the effects of climate change, particularly regarding hydrology. Long-term studies are needed to disentangle such variability and improve knowledge regarding the ecological responses and detection of earlywarning signals to climate change. Investments should focus on taxa beyond fish and macroinvertebrates, and in covering the less studied regions of Chile and South Africa.
3Scientists, policy makers, and water managers must be involved in the climate change dialogue because the freshwater conservation concerns are huge.
“…Flow fluctuations and extreme conditions such as floods are primary sources of variability and disturbance (Cowell et al 2004). High discharge events can cause severe population losses and changes in the community composition and structure (Hart and Finelli 1999;Lytle et al 2008). Streams in monsoonal environments are subject to extreme seasonal variation in flow (Jacobsen and Encalada 1998;Brewin et al 2000).…”
“…Extirpation of populations, possibly due to climate change and water withdrawals by humans, is ongoing and leads to significant ecosystem-level changes (Bogan and Lytle 2011). Its naturally fragmented distribution and conservation status have made A. herberti the subject of recent studies on phylogeography (Finn et al 2007), population stability (Finn et al 2009), and behavioral adaptations (Lytle et al 2008). Belostomatids are also interesting because males provide exclusive parental care, and A. herberti has become a model system for studying sperm competition (Smith 1979) and mating systems evolution (Smith 1997).…”
The giant water bug (Abedus herberti) is a large flightless insect that is a keystone predator in aridland aquatic habitats. Extended droughts, possibly due to climate change and groundwater pumping, are causing once-perennial aquatic habitats to dry, resulting in serious conservation concern for some populations. A. herberti also exhibits exclusive male parental care, which has made it a model organism for studying mating systems evolution. Here we describe 17 novel polymorphic microsatellite loci developed for A. herberti. Number of alleles per locus ranged from 2 to 15, and average observed and expected heterozygosities were 0.579 and 0.697, respectively. These loci can successfully resolve both population genetic structure among sites separated by 3–100 km (FST = 0.08–0.21, P < 0.0001), and divergent mating strategies within local populations, making them highly useful for conservation genetics studies of this vulnerable species.
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