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22 results for “Brood survival”
Wood duck nest survival and duckling recruitment is minimally affected by interspecific brood parasitism from hooded mergansers and black-bellied whistling-ducks
<p>In the southeastern United States, wood ducks (<em>Aix sponsa</em>) have historically experienced interspecific brood parasitism (IBP) primarily from hooded mergansers (<em>Lophodytes cucullatus</em>), but the recent northward expansion of black-bellied whistling-ducks (<em>Dendrocygna autumnalis</em>) has added a new complexity to these interactions. We monitored nest boxes in Louisiana to evaluate the influence IBP had on wood duck daily nest survival rate (after, DSR) and duckling recruitment. We monitored 1,295 wood duck nests from 2020−2023 and found 112 (8.7%) were parasitized by hooded mergansers and 148 (11.5%) by whistling-ducks. Parasitic egg-laying by hooded mergansers lowered wood duck DSR, while DSR for nests parasitized by whistling-ducks was comparable to clutches containing only wood duck eggs. We considered the wood duck capture histories of 2,465 marked female ducklings and 540 banded adult females to estimate a duckling recruitment probability for the entire study period. We recaptured 50 ducklings as adults; 6 (12.0%) hatched from clutches parasitized by hooded mergansers, 1 (2.0%) from a clutch parasitized by a whistling-duck, and 43 (86.0%) from clutches containing only wood duck eggs. The duckling recruitment probability was 0.039 (95% credible interval = 0.028, 0.051). Nest initiation date had a negative effect on recruitment, wherein most recruits hatched from nests initiated earlier in the season. Given only ~9% of wood duck nests contained hooded merganser eggs, we conclude IBP writ large had no detrimental effect on DSR at a population level. The lower DSR of clutches parasitized by hooded mergansers is potentially linked to a high abundance of early-season parasites that produce "dump nests" and these clutches are often abandoned without being incubated. Despite ongoing parasitism by hooded mergansers and the range expansion of whistling-ducks, wood duck productivity in Louisiana appears to be minimally affected by interspecific brood parasitism.</p>
Data from: Wood ducks and hooded mergansers as interspecific brood parasites: An evaluation of parasitic egg survival
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Wood duck nest survival and duckling recruitment is minimally affected by interspecific brood parasitism from hooded mergansers and black-bellied whistling-ducks
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Figure 3 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 3 (continued from previous page). 27-30, Views of Idris sp. parasitoids emerging from the third brood and, as adult wasps, moving over to the fourth brood, still attended by the female Asemonea. It is likely that this brood will also be infected. 31, View of cocoon (remnant of first brood) and exuviae remaining in second brood, the only successful brood of the four, under the first leaf. Note the presence of a Myrmarachne sp. (arrow) in this Asemonea nest. 32, Five days later the female Asemonea was gone, leaving only scattered eggs from her third and fourth broods on the underside of the second Ficus leaf.
Figure 3 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 3 (continued from previous page, continued on next page). 15-16, The mantispid emerged from its cocoon (apparently remnant of first brood) and molted. 17, Detail of empty mantispid cocoon. 18, Mantispid near spiderlings of the second brood. 19, Female Asemonea tending her third brood. 20, View of mantispid and second brood beneath lower leaf, and female attending third brood beneath upper Ficus microcarpa leaf.
Figure 3 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 3 (continued from previous page, continued on next page). 21, Mantispid near its empty cocoon and exuvium, also near the developing second brood. 22, About one week later the female Asemonea was gone but the third brood was developing normally. The emergent (instar II) spiderlings shown here most likely came from the second brood. 23, A female Asemonea, perhaps the original female, moved into the nest near the third brood. 24, Same female Asemonea feeding on a chironomid midge in her nest near the second brood. 25, Gravid female Asemonea near the third brood, now clearly infected with Idris sp. parasitoids. 26, Same female after depositing a fourth brood of 18 eggs near the infected third brood.
Figure 3 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 3 (continued from previous page, continued on next page). 7, Developing second brood (instar I) under the first leaf. 8, Female Asemonea with third brood under the second leaf (upper left) with cocoon that replaced the first brood and the developing second brood under the first leaf. 9-11,14, Cocoon and developing second brood. 12, Detail of small insect (Heteroptera) near the mantispid cocoon, from (10). 13, Female Asemonea attending her third brood of 10 eggs on the second leaf.
Figure 1 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 1 (continued from previous page). 8-9, The 9 instar I spiderlings continued to develop as the female returned to her original colour. 10-12, Still attended by the female, 7 remaining spiderlings molted to the emergent instar (instar II). 13, The female and all of her spiderlings were gone.
Figure 3 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 3 (continued on next page). 1-2, Female Asemonea tenuipes attending her nest including a mantispid cocoon and a normal brood of 19 eggs on the underside of a Ficus microcarpa leaf. 3-8, Eggs of the second brood of 19 eggs were hatching (3) as the female Asemonea tenuipes moved to a nearby leaf and deposited a new brood of 10 eggs (6).
Figure 2 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 2 (continued from previous page, continued on next page). 5-6, Neuropteran larva (possibly mantispid) feeding on eggs in the more recent or second brood. 7-10, The female Asemonea continued to attend to her nest, now inhabited by the cocooning neuropteran and 7 eggs that may have been damaged or infested by Idris.
Figure 1 in Impact of brood parasitoids and oophagy on survival of Asemonea tenuipes (Araneae: Salticidae: Asemoneinae) broods in Karnataka
Figure 1 (continued on next page). 1, Light green Female A. tenuipes tending her clutch of 9 eggs beneath a leaf of Ficus microcarpa. 2, 9 newly hatched spiderlings (instar I) with short legs. Note that the female was now darker. 3-7, The 9 instar I spiderlings continued to develop.
The role of reed management and habitat quality on brood parasitism and chick survival of the brood parasitic Common Cuckoo
<p>Despite efforts on ecosystem restoration and management, biodiversity loss remains one of the major environmental concerns of our time. Beyond the focus on threatened species, animals that indicate regional biodiversity hotspots and population trends, such as brood parasites, should also be targeted by conservation actions. We studied how reed habitat quality and management influence brood parasitism rate and offspring survival in Common Cuckoos Cuculus canorus parasitizing nests of Great Reed Warblers Acrocephalus arundinaceus. In six reed habitats in an intensive agricultural landscape. Data collected from 45 sites over 13 years showed that the brood parasitism rate was highest on large canals and was positively influenced by the availability of potential perches (Cuckoo vantage points) and the height where host nests were built. Cuckoo chick survival decreased with water depth and was not affected by other factors. Our results suggest that the habitat-dependent detectability of host nests was central in brood parasitism rate and that water level was central in Cuckoo chick survival. Our study shows that a maintenance of intermediate water levels is the most optimal for maintaining Cuckoo populations in intensive agricultural landscapes. Because brood parasites are excellent bioindicators as their presence predicts regional hotspots of taxonomic and functional diversity as well as population trends in bird communities, knowledge on their habitat requirements is relevant in management targeting diverse bird communities.</p>
Why do parents produce small broods of offspring that have lower body mass, survival, and lifetime reproductive success? A case study in a long-lived bird
<p class="MsoNormal"><span>Numerous studies have </span><span>examined the correlation between offspring </span><span>quantity</span><span> and quality</span><span>, and many have found that the most common brood size is often smaller than broods with the highest offspring quality or production. However, the reasons why these small broods with lower offspring quality are produced, are still poorly explained. Using data spanning 29 years, we investigated the effects of brood size on nestlings' body mass and the lifetime fitness for those offspring as adults (as proxies of offspring quality) in the Crested Ibis (<em>Nipponia nippon</em>). We also examined the temporal variation of brood size. We found that overall offspring quality increases with brood size and that individuals from broods of three had the highest quality, as quantified by larger body mass, higher adult survival, and lifetime reproductive success. Furthermore, brood size of an individual pair significantly varied across years, and the proportion of broods containing two offspring increased while broods of three decreased after 2000 when the population dispersed to low-quality habitat. These findings indicate that spatiotemporal variation in resources may impact variation in brood size and subsequent fitness consequences, and that small broods are more common in resource-poor years or low-quality habitats. In contrast, parents with access to high-quality resources produce larger broods of nestlings that achieve higher body mass and subsequently experience higher adult survival and lifetime fitness. This study highlights how variation in life history traits can be influenced by resource condition, and provides an insight into particular habitat that need conservation for Crested Ibis.</span></p>
The role of reed management and habitat quality on brood parasitism and chick survival of the brood parasitic Common Cuckoo
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Why do parents produce small broods of offspring that have lower body mass, survival, and lifetime reproductive success? A case study in a long-lived bird
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Data from: Impact of brood parasitism and predation on nest survival of the fan-tailed gerygone in New Caledonia
<p>Predation and brood parasitism are common reasons for nesting failure in passerine species and the additive impact by invasive species is a major conservation concern, particularly on tropical islands. Recognising the relative contribution of the different components of nesting failure rates is important to understand co-evolutionary interactions within brood parasite-host systems. In the remote archipelago of New Caledonia, the fan-tailed gerygone <i>Gerygone flavolateralis</i> is the exclusive host of the brood-parasitic shining bronze-cuckoo <i>Chalcites lucidus</i>. Additionally, invasive rodents also possibly have an impact on breeding success. To estimate the impact of potential nest predators, we 1) video monitored nests to identify predators, 2) estimated the probability of predation based on nest visibility and predator abundance and 3) tested the possibility that the location of experimental nests and lack of odour cues decrease the predation by rodents. In addition, we estimated nest survival rates using data collected in different habitats over the course of 8 breeding seasons. Nesting success of fan-tailed gerygone was relatively low and predation was the main cause of nesting failure. We recorded mainly predation by native birds, including the shining bronze-cuckoo, whereas predation by rats was rare. In open habitats predation by cuckoos was much lower than predation by other avian predators. Neither predator activity around nests nor nest visibility influenced the probability of predation. Experimental nests in more accessible locations and containing an odorous bait were more exposed to rodent predation. Apparently, the fan-tailed gerygone has either never been specifically vulnerable to predation by rats or has developed anti-predator adaptations.</p>
Fig. 3. Copris tripartitus new adult weight from brood balls. 1 in Fecundity And Offspring Survival Of Copris Tripartitus Waterhouse (Coleoptera, Scarabaeidae: Scarabaeinae) Under Laboratory Rearing Conditions
Fig. 3. Copris tripartitus new adult weight from brood balls. 1) cared for; 2) not cared by for by females.
Data from: Impact of brood parasitism and predation on nest survival of the fan-tailed gerygone in New Caledonia
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Data from: The influence of social structure on brood survival and development in a socially polymorphic ant: insights from a cross-fostering experiment
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Mismatch between strong nest site selection and low survival of nests and broods for American woodcock and its implications for conservation
<p>Code and data for the paper entitled "Mismatch between strong nest site selection and low survival of nests and broods for Scolpax minor (American woodcock) and its implications for conservation" published in Ornitholgical Applications (2025). R code for landscape nest site selection is called <a href="../api/records/10927854/draft/files/landscape_nest_selectionornapplications.R/content" target="_blank" rel="noopener">landscape_nest_selectionornapplications.R</a> and data is called usedand5000availpoints.csv. R Code for local nest site selection is called <a href="../api/records/10927854/draft/files/local_nest_selectionornapplications.R/content" target="_blank" rel="noopener">local_nest_selectionornapplications.R</a> and data is called 2021_2022_nestdataveragedwithuse.csv. R code for nest survival is called <a href="../api/records/10927854/draft/files/nestsurvivalornapplications.R/content" target="_blank" rel="noopener">nestsurvivalornapplications.R</a> and data is called nestencounterwweather.csv and nestencounterhistoryweatherhabitat.csv. R code for brood survival is called <a href="../api/records/10927854/draft/files/broodsurvivalornapplications.R/content" target="_blank" rel="noopener">broodsurvivalornapplications.R</a> and data is called broodencounterhistoryweather.csv. All datasets are within the zipped folder called Nest Site Selection and Survival Analyses.zip</p>
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