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704 results for “Interference”
Reproductive interference alters species coexistence in nematodes due to asymmetric sperm-induced harm
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Dataset from 'Hesse, C., Koroknai, L., & Billino, J. (2018). Individual differences in processing resources modulate bimanual interference in pointing. Psychological Research. doi: 10.1007/s00426-018-1050-3
<p>--------------------------------------------------------------</p> <p>The folder contains 8 data files and 1 readme file describing the content of the data files.</p> <p>-------------------------------------------------------------</p> <p>For further questions, please contact:<br> c.hesse[at]abdn.ac.uk</p> <p> </p>
Fig. 1 in Reproductive Interference between Native and Introduced Lady Beetles (Coleoptera: Coccinellidae) in Puerto Rico
Fig. 1. Male Cycloneda sanguinea limbifer attempting to mate heterogeneric lady beetle females. a) With female Olla v-nigrum; b–d) With female Coelophora inaequalis. Laboulbeniales thalli can be seen on the elytra of two C. s. sanguinea (a and b, d).
Data and code for "A flux-tunable YBa2Cu3O7 quantum interference microwave circuit"
<p>Data and measurements scripts for the paper "A flux-tunable YBa2Cu3O7 quantum interference microwave circuit".<br><br>Funding by the Deutsche Forschungsgemeinschaft (DFG) via Grant Nos. BO 6068/1-1 and BO 6068/2-1.</p>
Data from: Interspecies interference and monitoring duration affect detection rates in chew cards
Pest monitoring methods should provide unbiased accurate estimates of pest densities and locations, while also minimizing time-in-field and costs. Recent pest mammal monitoring studies have found that chew cards are more effective than conventional mammal monitoring methods, but little experimental work has been done to determine optimal experimental duration or quantify the risks of saturation by one species biasing detections of other species. Here, we used chew cards in three sites within Awarua wetland (Southland, New Zealand) to investigate the optimal amount of time required to detect targeted pest species (rats, possums and mice), and to examine the potential of rats and possums to bias detection rates of other species. We found depressed detections of possums and rats where a contraspecific had been detected on a card, which is consistent with previous studies of a similar duration on interspecies interference. This experiment is the first to analyse the rates at which species detections accrue over the course of a survey, and we found rat detections lagged behind possums for the first four nights. We modelled the effect of survey duration and relative rat abundance on the likelihood of further possum detections. Duration and rat abundance interacted, meaning there are trade-offs to be considered with regard to duration: shorter durations may avoid the risk of saturation in areas of high pest density, but risk not sampling sparse or neophobic populations. Our data suggest that chew cards remain one of the most sensitive pest monitoring tools for rats and possums, compared to conventional methods such as tracking tunnels and wax tags. In areas of moderate pest densities, we suggest that a duration of five nights is optimal for detecting pests. However, in areas of high pest density the sensitivity of chew cards may render them unsuitable because of saturation and interspecies interference effects.
FIGURE 4. Dasydytes lamellatus differential interference contrast photomicrographs. A–B, D in New data on Brazilian semiplanktonic gastrotrichs (Gastrotricha: Chaetonotida)
FIGURE 4. Dasydytes lamellatus differential interference contrast photomicrographs. A–B, D: Ventral View, C: egg, E: Dorsal view. at: anterior cilia tuft; ca–b: cephalic long spines; db: dorsal cilia band; ta–tb: trunk spines; pt: posterior cilia tuft; r: rear spine; vt1–3: ventral cilia tufts.
FIGURE 1. Dasydytes lamellatus differential interference contrast photomicrographs. A in New data on Brazilian semiplanktonic gastrotrichs (Gastrotricha: Chaetonotida)
FIGURE 1. Dasydytes lamellatus differential interference contrast photomicrographs. A: Dorsal view, B: Ventral view, spined scales at posterior protuberance, C: Ventral motile spines with two lamella-like denticles, D: Ventral spine groups inserted at the head and trunk, E: Lateral view, F: egg. at: anterior tuft; ca–cb: cephalic long spines; db: cephalic dorsal cilia band; de: denticle; lt: lateral tuft; ss: short spines; ta–tb: trunk spines; r: rear spine.
FIGURE 7. Neogossea acanthocolla differential interference contrast photomicrographs. A–B in New data on Brazilian semiplanktonic gastrotrichs (Gastrotricha: Chaetonotida)
FIGURE 7. Neogossea acanthocolla differential interference contrast photomicrographs. A–B: dorsal view, C–E: Lateral view, F–G: Dorsal view. ac: anterior constriction; at: anterior cilia tuft; br: neck brush spines; cs: cephalic short spines; db: dorsal cilia band; mv: median ciliary tuft; pb: posterior bulb; ts: trunk scales.
FIGURE 2. Dasydytes lamellatus differential interference contrast photomicrographs. A in New data on Brazilian semiplanktonic gastrotrichs (Gastrotricha: Chaetonotida)
FIGURE 2. Dasydytes lamellatus differential interference contrast photomicrographs. A: Dorsal view, B: Ventral view, ciliature tufts, C: lateral ciliature tuft, D: E: Cephalic ciliature. at: anterior cilia tuft; ca–cb: cephalic long spine; ce: cephalion; db: dorsal cilia band; lt: lateral cilia tuft; ta–tb: trunk spines; r: rear spine; ss: short spines; ta: trunk spines; vt1–3: ventral cilia tufts.
FIGURE 6. Haltidytes pseudosquamosus differential interference contrast photomicrographs. A in New data on Brazilian semiplanktonic gastrotrichs (Gastrotricha: Chaetonotida)
FIGURE 6. Haltidytes pseudosquamosus differential interference contrast photomicrographs. A: Dorsal view, B: Dorsal view, ciliature tufts, C: Dorsal view, spines path, D, E: Cephalic ciliature. at: anterior cilia tuft; db: dorsal cilia band; nb: neck sensory bristle; nf: nefridia; pt: posterior cilia tuft.
FIGURE 5. Haltidytes pseudosquamosus differential interference contrast photomicrographs. A in New data on Brazilian semiplanktonic gastrotrichs (Gastrotricha: Chaetonotida)
FIGURE 5. Haltidytes pseudosquamosus differential interference contrast photomicrographs. A: Dorsal view, B: Ventral view, spines insertion, C: Dorsal view, spines insertion, D, dorsal view, spine paths, E: posterior spine denticle. de: denticles; nf: nefridia; ta–d: trunk spines.
Synergistic effects of warming and internal nutrient loading interfere with the long-term stability of lake restoration and induce sudden re-eutrophication
<p><strong>This repository contains the dataset linked to the following publication:</strong></p> <p><strong>Article title: </strong>Synergistic effects of warming and internal nutrient loading interfere with the long-term stability of lake restoration and induce sudden re-eutrophication</p> <p><strong>Journal: </strong><em>Environmental Science & Technology</em></p> <p><strong>DOI</strong>: 10.1021/acs.est.2c07181</p> <p><strong>Abstract:</strong> Phosphorus (P) precipitation is among the most effective treatments to mitigate lake eutrophication. However, after a period of high effectiveness, studies have shown possible re-eutrophication and the return of harmful algal blooms. While such abrupt ecological changes were attributed to the internal P loading, the role of lake warming and its potential synergistic effects with internal loading, thus far, has been understudied. Here, in a eutrophic lake in central Germany, we quantified the driving mechanisms of the abrupt re-eutrophication and cyanobacterial blooms in 2016 (30 years after the first P precipitation). A process-based lake ecosystem model (GOTM-WET) was established using a high-frequency monitoring dataset covering contrasting trophic states. Model analyses suggested that the internal P release accounted for 68% of the cyanobacterial biomass proliferation, while lake warming contributed to 32%, including direct effects via promoting growth (18%) and synergistic effects via intensifying internal P loading (14%). The model further showed that the synergy was attributed to prolonged lake hypolimnion warming and oxygen depletion. Our study unravels the substantial role of lake warming in promoting cyanobacterial blooms in re-eutrophicated lakes. The warming effects on cyanobacteria via promoting internal loading need more attention in lake management, particularly for urban lakes.</p> <p><strong>SYNOPSIS: </strong>Warming synergistically promotes re-eutrophication with internal nutrient loading and exacerbates cyanobacterial blooms in urban lakes 30 years after phosphorus mitigation.</p> <p> </p> <p><strong>Data description </strong>by Xiangzhen Kong (<a href="mailto:xzkong@niglas.ac.cn">xzkong@niglas.ac.cn</a>), 2023-02-20</p> <p>---Wet chemical analysis on water samples taken at five depths (0.5, 2.5, 5.0, 7.0 and 9.0 m) from the deepest point in the lake (BA1) at biweekly intervals from 2018.5-2021.8.</p> <p> File name:</p> <ul> <li>BAB_BA1_TN_mgL.obs (total nitrogen concentration)</li> <li>BAB_BA1_NH4_mgL.obs (ammonium nitrogen concentration)</li> <li>BAB_BA1_NO3_mgL.obs (nitrate nitrogen concentration)</li> <li>BAB_BA1_TP_mgL.obs (total phosphorus concentration)</li> <li>BAB_BA1_SRP_mgL.obs (Soluble reactive phosphorus concentration)</li> <li>BAB_BA1_DP_mgL.obs (dissolved P concentration)</li> <li>BAB_BA1_DOC_mgL.obs (Dissolved organic carbon concentration)</li> <li>BAB_BA1_Si_mgL.obs (dissolved silicon concentration)</li> <li>BAB_BA1_Chla_HPLC_DIN_mgL.obs (Chl-a concentration)</li> </ul> <p> </p> <p>---CTD probe profile data from the deepest point in the lake (BA1) from 2017.8 to 2021.8 at biweekly basis with approximately 0.1 m vertical resolution</p> <p> File name:</p> <ul> <li>t_prof_file_barleber_ctm644.obs (water temperature)</li> <li>oxy_prof_file_barleber_ctm644 (Dissolved oxygen)</li> <li>turb_prof_file_barleber_ctm644.obs (Turbidity)</li> <li>chla_prof_file_barleber_ctm644.obs (Chl-a concentration)</li> </ul> <p> </p> <p>---BBE probe profile data from the deepest point in the lake (BA1) from 2017.8 to 2021.8 at biweekly basis with approximately 0.1 m vertical resolution</p> <p> File name:</p> <ul> <li>totalChla_prof_file_barleber_FP2101.obs (Chl-a concentration)</li> <li>bluegreen_prof_file_barleber_FP2101.obs (Blue-green algae Chl-a concentration)</li> <li>green_prof_file_barleber_FP2101.obs (Green algae Chl-a concentration)</li> <li>diatom_prof_file_barleber_FP2101.obs (Diatom Chl-a concentration)</li> </ul> <p> </p> <p> </p>
Temporal Interference Stimulation for Social Cognition
ClinicalTrials.gov study NCT06607432. IPD Sharing: YES. Countries: 1. Publications: 2.
Effects of an Exergame Focused on Cognitive-motor Interference on the Cognitive and Motor Capacities of Older Adults
ClinicalTrials.gov study NCT04803799. IPD Sharing: NO. Countries: 1. Publications: 1.
Non-interference Study of MR and Yellow Fever Vaccines Among Bangladeshi Infants Aged 9-12 Months
ClinicalTrials.gov study NCT06815835. IPD Sharing: NO. Countries: 1. Publications: 14.
Testing Interference-based Methods to Mitigate Gambling Craving - A Multiple Single Case Design
ClinicalTrials.gov study NCT03493399. IPD Sharing: Not stated. Countries: 1. Publications: 5.
Temporal Interference Methods for Non-invasive Deep Brain Stimulation, Study 1.2
ClinicalTrials.gov study NCT07339072. IPD Sharing: NO. Countries: 1. Publications: 3.
Temporal Interference and Depression
ClinicalTrials.gov study NCT05295888. IPD Sharing: NO. Countries: 1. Publications: 1.
Temporal Interference Methods for Non-invasive Deep Brain Stimulation, Study 1.1
ClinicalTrials.gov study NCT07215299. IPD Sharing: NO. Countries: 1. Publications: 3.
Evaluation of Interference Between Cell Phones and Implantable Cardioverter Defibrillators
ClinicalTrials.gov study NCT02330900. IPD Sharing: Not stated. Countries: 1. Publications: 1.
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