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Climate change is altering the phenology of species across the world, but what are the consequences of these phenological changes for the demography and population dynamics of species? Time-sensitive relationships, such as migration, breeding and predation, may be disrupted or altered, which may in turn alter the rates of reproduction and survival, leading some populations to decline and others to increase in abundance. However, finding evidence for disrupted relationships, or lack thereof, and their demographic effects, is difficult because the necessary detailed observational data are rare. Moreover, we do not know how sensitive species will generally be to phenological mismatches when they occur. Existing long-term studies provide preliminary data for analysing the phenology and demography of species in several locations. In many instances, though, observational protocols may need to be optimized to characterize timing-based multi-trophic interactions. As a basis for future research, we outline some of the key questions and approaches to improving our understanding of the relationships among phenology, demography and climate in a multi-trophic context. There are many challenges associated with this line of research, not the least of which is the need for detailed, long-term data on many organisms in a single system. However, we identify key questions that can be addressed with data that already exist and propose approaches that could guide future research.
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... In the middle and high latitudes of the Northern Hemisphere, the nestling growth period of passerines must be synchronized with the peak abundance of insect larva prey to maximize nestling growth and survival [1][2][3][4][5]. Climate change-induced spring temperature increases can advance the timing of insect development [6,7], whereas the timing of breeding in birds is regulated more by photoperiod than temperature [8], resulting in a trophic mismatch between nestlings and insect larvae [7][8][9][10][11][12]. Nestlings hatching outside the peak period of insect larvae abundance may suffer malnutrition, posing a significant challenge to nestling survival [9,10]. ...
... Climate change-induced spring temperature increases can advance the timing of insect development [6,7], whereas the timing of breeding in birds is regulated more by photoperiod than temperature [8], resulting in a trophic mismatch between nestlings and insect larvae [7][8][9][10][11][12]. Nestlings hatching outside the peak period of insect larvae abundance may suffer malnutrition, posing a significant challenge to nestling survival [9,10]. Although adults increase their feeding efforts to satisfy nestling nutritional requirements [13], little is known about how nestlings cope with the stress caused by trophic mismatch. ...
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... There are also indications that increased primary productivity increases predation on the nests of ground-breeding birds, in particular, in the upper bioclimatic sub-zones . There is also some evidence for negative impacts of phenological mismatch, which affects migration and access to food supply during nesting (Carey 2009, Crick 2004, Miller-Rushing et al. 2010. Species that are specifically adapted to the habitat structures or trophic conditions in intact alpine ecosystems are expected to decline due to habitat loss in a warming climate (Lehikoinen et al. 2014 and to changes in alpine grazing regimes that affect tree line dynamics (Bryn and Potthof 2018). ...
... Birds expected to be most affected are species that are specialised on nest sites such as cavity-nesters, or species that require habitats or food resources that are now scarce, such as the late successional stages of pristine forest (e.g., White-backed Woodpecker and Siberian Jay, Bradter et al. 2021). Climate change can cause phenological mismatches, which affect migration and access to food resources during nesting and has been identified as generic mechanism that affects many species (Carey 2009, Crick 2004, Miller-Rushing et al. 2010, but lagged or indirect effects of climate change may also be involved (Jenouvrier 2013). Due to the simultaneous action of forestry and climate change during the timeframe when monitoring data on bird communities are available, it may be difficult to distinguish the relative impact of these two drivers. ...
Technical Report
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The panel-based assessment of ecosystem condition (PAEC) is an evidence-based ap-proach to assess the condition of Norwegian ecosystems. The assessment is carried out by an expert panel with broad expertise in the ecosystems to be assessed and is inspired by approaches used in international assessments such as IPCC and IPBES. The assessment follows an earlier developed protocol. In this report, PAEC is piloted for major terrestrial ecosystems in the county of Trøndelag; forest, alpine, open-lowlands, and wetlands. For each ecosystem, a list of indicators of change in ecosystem condition in response to anthropogenic drivers is developed. The indicators fall within seven main ecosystem char-acteristics: primary production, biomass distribution among trophic levels, functional groups within trophic levels, functionally important species, biological diversity, landscape ecologi-cal patterns, and abiotic factors. The expected change in indicators in response to anthro-pogenic drivers are termed phenomena, and their selection is based on published literature, including reference to the confidence of a change being observed in response to anthropo-genic drivers and the mechanism leading to a deterioration in ecosystem state. Datasets to quantify each indicator are identified and collated and the quality of each dataset is assessed in terms of its spatial and temporal appropriateness. In the first assessment step, the validity (VP) of each phenomenon is scored and used to infer confidence in the causal relationship between changes in the indicator and anthropo-genic drivers. The next step is an evaluation of the biological and statistical significance of the evidence for the occurrence of each phenomenon, termed evidence (EP) of the phe-nomenon. The third step is a consolidated assessment of the ecological state based on the associated indicators and phenomena, first for each ecosystem characteristic, and subse-quently for the ecosystem as a whole. The assessment is based on the validity, the quality of the evidence, and the data quality for each phenomenon. This provides a qualitative as-sessment of deviation from the reference condition of “no deviation”, “limited deviation” or “substantial deviation”. The assessments are each supported by narrative accounts. The pilot assessment involved analysis of 24 datasets documenting 41 indicators. Several indi-cators were included in multiple ecosystems. In total there were 27 indicators used for forest ecosystems, 24 for alpine ecosystems, and 16 in each of wetlands and open lowlands. In the forest ecosystems, substantial deviation from the reference condition was identified for five of the ecosystem characteristics. The two exceptions were primary productivity where there was a limited deviation from the reference condition, and biological diversity where there was no deviation from the reference condition (but the latter was based on a single indicator and hence an entirely inadequate indicator coverage). The deviations were found primarily in climatic variables, cervids and their forage and predators, and dead wood. Overall, the forest ecosystem was assessed as having a substantial deviation from the ref-erence condition. In the alpine ecosystems, substantial deviation from the reference condition was identified for the abiotic ecosystem characteristic, largely attributed to indicators associated with tem-perature, seasonality, and snow. Limited deviation from the reference condition was as-sessed for functionally important species and primary productivity (both based on a partially NINA Report 2094 4 adequate indicator coverage) and for biological diversity, functional groups within trophic levels and landscape ecological patterns (but these were based on an inadequate indicator coverage). For the ecosystem characteristic biomass distribution among trophic levels, the quality of evidence was insufficient to conclude regarding the condition of the single indicator involved, and no overall assessment of this ecosystem characteristic could be undertaken. Overall, the alpine ecosystem was assessed as having limited deviation from the reference condition. For both open lowland and wetland ecosystems, several ecosystem characteristics were not assessed due to a lack of relevant indicator datasets. For this reason, no overall assess-ment of the ecosystems as a whole could be undertaken. However, for both ecosystems, there was a substantial deviation from the reference condition for abiotic factors (tempera-ture, seasonality, and snow). In open lowlands, there was a substantial deviation in func-tionally important species (ungulates) and limited deviation in primary productivity and bio-logical diversity. In wetlands, there was a limited deviation from the reference condition in primary productivity, biological diversity, and landscape ecological patterns. Most challenges encountered during this pilot assessment related to the inadequacy of the datasets for assessing ecosystem condition. Reasons behind this include that ecosystem ex-tents are not adequately mapped, particularly those characterised by small and fragmented patches, and a taxonomic or geographical limitation of datasets and environmental monitoring. The report suggests further development of indicators for operational application. Finally, the report also suggests knowledge needs and prioritisation for further research to support the future implementation of ecosystem assessments in Norway.
... There is also evidence that increased primary productivity increases predation on the nests of ground-breeding birds, in particular, in the colder bioclimatic sub-zones of the Low Arctic tundra . The links to anthropogenic drivers are assessed as certain, especially the relationship with phenological mismatch, which affects migration and access to food supply during nesting (Carey 2009, Crick 2004, Miller-Rushing et al. 2010. Species that are specifically adapted to the habitat structures, competitive, or trophic conditions (nutrient supply and predation pressure) in intact tundra ecosystems are expected to decline in a warming Arctic (Lehikoinen et al. 2019, Lehikoinen et al. 2014 The most important anthropogenic driver of changes in this indicator is climate change. ...
... Altered species interactions during reproduction may be more impactful than abiotic effects (Ockendon et al., 2014). While it remains contested if trophic mismatches can have population-level consequences (Both et al., 2006;Franks et al., 2018;Johansson et al., 2015;Miller-Rushing et al., 2010;Reed et al., 2013;Saino et al., 2011), inadequate food resources can cause reduced growth rates and may lead to reduced survival or fitness (Gaston et al., 2009;Lameris et al., 2018Lameris et al., , 2022Ross et al., 2018;Sedinger et al., 1995). A greater mechanistic understanding is needed as well as identification of baselines for defining optimal food resource characteristics. ...
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Abstract Climate change is leading to phenological shifts across a wide range of species globally. Polar oceans are hotspots of rapid climate change where sea ice dynamics structure ecosystems and organismal life cycles are attuned to ice seasonality. To anticipate climate change impacts on populations and ecosystem services, it is critical to understand ecosystem phenology to determine species activity patterns, optimal environmental windows for processes like reproduction, and the ramifications of ecological mismatches. Since 1991, the Palmer Antarctica Long‐Term Ecological Research (LTER) program has monitored seasonal dynamics near Palmer Station. Here, we review the species that occupy this region as year‐round residents, seasonal breeders, or periodic visitors. We show that sea ice retreat and increasing photoperiod in the spring trigger a sequence of events from mid‐November to mid‐February, including Adélie penguin clutch initiation, snow melt, calm conditions (low winds and warm air/sea temperature), phytoplankton blooms, shallow mixed layer depths, particulate organic carbon flux, peak humpback whale abundances, nutrient drawdown, and bacterial accumulation. Subsequently, from May to June, snow accumulates, zooplankton indicator species appear, and sea ice advances. The standard deviation in the timing of most events ranged from ~20 to 45 days, which was striking compared with Adélie penguin clutch initiation that varied 30 days) than mean dates and the variability in timing was low (
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Species respond idiosyncratically to environmental variation, which may generate phenological mismatches. We assess the consequences of such mismatches for solitary bees. During 9 years, we studied flowering phenology and nesting phenology and demography of five wood-nesting solitary bee species representing a broad gradient of specialization/generalization in the use of floral resources. We found that the reproductive performance and population growth rate of bees tended to be lower with increasing nesting–flowering mismatches, except for the most generalized bee species. Our findings help elucidate the role of phenological mismatches for the demography of wild pollinators, which perform key ecosystem functions and provide important services for humanity. Furthermore, if climate change increases phenological mismatches in this system, we expect negative consequences of climate change for specialist bees.
... Climate can strongly influence phenology (the timing of life-history events) by speeding up or delaying events such as emergence, peak activity and reproduction [1]. In turn, phenology can influence individual fitness [2,3], species interactions [4,5] and ecosystem function [6]. Shifts in climate may alter phenology and consequently organismal fitness by exposing organisms to unfavorable abiotic environments and through altering the strength of species interactions ( phenological mismatch). ...
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The timing of life events (phenology) can be influenced by climate. Studies from around the world tell us that climate cues and species' responses can vary greatly. If variation in climate effects on phenology is strong within a single ecosystem, climate change could lead to ecological disruption, but detailed data from diverse taxa within a single ecosystem are rare. We collated first sighting and median activity within a high-elevation environment for plants, insects, birds, mammals and an amphibian across 45 years (1975–2020). We related 10 812 phenological events to climate data to determine the relative importance of climate effects on species’ phenologies. We demonstrate significant variation in climate-phenology linkage across taxa in a single ecosystem. Both current and prior climate predicted changes in phenology. Taxa responded to some cues similarly, such as snowmelt date and spring temperatures; other cues affected phenology differently. For example, prior summer precipitation had no effect on most plants, delayed first activity of some insects, but advanced activity of the amphibian, some mammals, and birds. Comparing phenological responses of taxa at a single location, we find that important cues often differ among taxa, suggesting that changes to climate may disrupt synchrony of timing among taxa.
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