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203 results for “harbour”
Fig. 3 in Lungworm seroprevalence in free-ranging harbour seals and molecular characterisation of marine mammal MSP
Fig. 3. Alignment of MSP amino acid sequences of marine and terrestrial mammal parasitic nematodes using the Clustal W method.
Fig. 2 in Lungworm seroprevalence in free-ranging harbour seals and molecular characterisation of marine mammal MSP
Fig. 2. Alignment of MSP nucleotide sequences of marine and terrestrial mammal parasitic nematodes using the Clustal W method.
Fig. 1 in Lungworm seroprevalence in free-ranging harbour seals and molecular characterisation of marine mammal MSP
Fig. 1. Anthelmintic treatment pattern, blood sampling time points and corresponding OD values of harbour seals in rehabilitation. Harbour seals (n = 6) were treated twice with ivermectin at arrival (day 1) at the Seal Rehabilitation and Research Centre, Pieterburen, The Netherlands, and 21 days later and once with mebendazole between day 2 and 6. OD values in grey boxes show lungworm-ELISA positive serum samples, those highlighted in blue lungworm-ELISA negative samples. Harbour seal individuals highlighted in dark grey coughed up lungworms one day after arrival. (For interpretation of the references to colour in this figure legend, the reader is referred to the web version of this article.)
Fig. 5 in Molecular Identification of a Phage-infected Protochlamydia Strain Naturally Harboured by Non-Encysting Naegleria
Fig. 5. Detail of electron microscopy of Naegleria clarki infected by Pcb, showing three enlarged RBs containing filled and empty phages. A normal-size wrinkled EB is also visible. Scale bar: 0.5 µm.
Fig. 1 in Anisakid nematode species identification in harbour porpoises (Phocoena phocoena) from the North Sea, Baltic Sea and North Atlantic using RFLP analysis
Fig. 1. RFLP profiles obtained by digestion of ITS1-5.8S-ITS2 region with the restriction enzymes HinfI, RsaI and HaeIII. a)-i) lane 1–5: Anisakid nematodes from harbour porpoises. j)-l) lane 1–3: A. simplex s. s. from North Sea, Baltic and Norwegian harbour porpoises; lane 4–6: P. decipiens s. s. from North Sea and Baltic harbour and grey seals; lane 7–9: C. osculatum s. s. from North Sea and Baltic harbour and grey seals. L: 100-bp ladder.
Fig. 1 in Lungworm infections in harbour porpoises (Phocoena phocoena) in the German Wadden Sea between 2006 and 2018, and serodiagnostic tests
Fig. 1. Annual comparison of lungworm prevalence in harbour porpoises stranded along the North Sea coast of the German federal state SchleswigHolstein between 2006 and 2018. The median of total deaths (19 ± 9.23, black line), uninfected cases (10 ± 6.83, dotted line) and positive cases (8 ± 5.04, dashed line) are additionally depicted.
Fig. 2 in Lungworm infections in harbour porpoises (Phocoena phocoena) in the German Wadden Sea between 2006 and 2018, and serodiagnostic tests
Fig. 2. MSP-ELISA results of the 245 samples from harbour porpoises assignable to a specific infection status. Green = lungworm negative (born in captivity); light blue = presumed lungworm negative sera (negative direct detection); dark blue = presumed lungworm negative whole blood (negative direct detection); light red = lungworm positive sera (direct lungworm detection); dark red = lungworm positive whole blood (direct lungworm detection). (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Fig. 3 in Lungworm infections in harbour porpoises (Phocoena phocoena) in the German Wadden Sea between 2006 and 2018, and serodiagnostic tests
Fig. 3. Immunoblot pattern of (presumed) lungworm negative (lane numbers indicated in blue: 1–5 = animals born in human care; 2–5 sampled over three consecutive years; 6–8 = no infection detected) as well as lungworm positive (lane numbers indicated in red: lane 9 = moderate infection; lane 10 = severe infection; lanes 11–16 = direct lungworm detection) harbour porpoise sera. Lane 17 = D. viviparus positive control serum, M = Spectra™ Multicolour Broad Range Protein Ladder (Thermo Fisher Scientific GmbH, Dreieich, Germany). (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Rīgas pieostas apkaimju foto // Photos of the neighbourhoods around the Riga Harbour (2018-2022)
<p>[English - below]</p> <p>-- Fotogrāfijas (un daži video) pamatā uzņemtas pētnieciskā projekta “Dzīve līdzās ostai: ekonaratīvi, vietējā vēsture un vides aktīvisms Daugavas lejtecē” ietvaros kolektīvās un individuālās ekspedīcijās uz piecām apkaimēm (un dažām robežapkaimēm): Bolderāju, Daugavgrīvu, Kundziņsalu, Mangaļsalu un Vecmīlgrāvi. Dažas foto sērijas uzņemtas privātos ceļojumos, kā arī pēc formālajām projekta beigām.<br> -- foto autori ir Jānis Daugavietis (JD), Agita Pusvilka (AP), Dace Bula (DB), Ieva Garda-Rozenberga (IeG), Kristīne Āboliņa (KA), Kaspars Zellis (KZ).<br> -- Foto laika hronoloģiskais periods: 2018.gada jūlijs - 2022.gada novembris.<br> -- Failu nosaukumos var būt kļūdas (nepareiza apkaime).<br> -- Attēlus drīkst izmantot, atsaucoties uz to autoriem, projektu “Dzīve līdzās ostai”. Ja publicējamos attēlos redzami cilvēki, nepieciešama arī viņu atļauja.</p> <p>«Dzīve līdzās ostai: ekonaratīvi, vietējā vēsture un vides aktīvisms Daugavas lejtecē» (Nr. lzp-2018/1-0446). Projekta vadītāja Dr. philol. Dace Bula.</p> <p> </p> <p>-- The photographs (and some videos) were taken in the course of the research project “Life next to the port: econarratives, local history and environmental activism in the lower Daugava” during collective and individual expeditions to five neighbourhoods (and some border neighbourhoods): Bolderaja, Daugavgriva, Kundzinsala, Mangalsala and Vecmilgravis. Some of the photos were taken on private trips and after the formal end of the project.<br> -- photos by Jānis Daugavietis (JD), Agita Pusvilka (AP), Dace Bula (DB), Ieva Garda-Rozenberga (IeG), Kristīne Āboliņa (KA), Kaspars Zellis (KZ).<br> -- Chronological period of the photos: July 2018 - November 2022.<br> -- File names may contain errors (wrong neighbourhood).<br> -- Images may be used with attribution to their authors, the project “Life next to the port”. If people are featured in the images to be published, their permission is also required.</p> <p>“Living Next to the Port: Eco-Narratives, Local Histories and Environmental Activism in the Daugava Delta” (lzp-2018/1-0446). Project leader Dr. philol. Dace Bula.</p> <p> </p> <p>LU Literatūras, folkloras un mākslas institūts<br> Mūkusalas iela 3<br> Rīga, LV-1423<br> Tālr. (371) 67229017<br> <a href="mailto:info@lulfmi.lv">info@lulfmi.lv</a><br> <a href="http://lulfmi.lv">http://lulfmi.lv</a></p> <p><a href="https://www.facebook.com/DziveLidzasOstai">https://www.facebook.com/DziveLidzasOstai</a><br> <a href="http://lulfmi.lv/Dzive-lidzas-ostai">http://lulfmi.lv/Dzive-lidzas-ostai</a><br> <a href="https://zenodo.org/communities/ekohum/">https://zenodo.org/communities/ekohum/</a><br> <a href="http://garamantas.lv/lv/repository/1537251/LZP-projekts-Dzive-lidzas-ostai">http://garamantas.lv/lv/repository/1537251/LZP-projekts-Dzive-lidzas-ostai</a><br> <a href="http://lulfmi.lv/en/Living-Next-to-the-Port">http://lulfmi.lv/en/Living-Next-to-the-Port</a> [EN]</p>
Increasing numbers of harbour seals and grey seals in the Solent
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Reef effect of offshore structures on the occurrence and foraging activity of harbour porpoises
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Estimating the abundance of the critically endangered Baltic Proper harbour porpoise (Phocoena phocoena) population using passive acoustic monitoring
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Data from: Vessel noise prior to pile driving at offshore windfarm sites deters harbour porpoises from potential injury zones
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Recombination data for the repeat-based holocentromere-harbouring genome of R. breviuscula
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Characterising underwater noise and changes in harbour porpoise behaviour during the decommissioning of an oil and gas platform
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Data from: Acoustically advertising male harbour seals in southeast Alaska do not make biologically relevant acoustic adjustments in the presence of vessel noise
Aquatically breeding harbour seal (Phoca vitulina) males use underwater vocalizations during the breeding season to establish underwater territories, defend territories against intruder males, and possibly to attract females. Vessel noise overlaps in frequency with these vocalizations and could negatively impact breeding success by limiting communication space. In this study we investigated whether harbour seals employed anti-masking strategies to maintain communication in the presence of vessel noise in Glacier Bay National Park and Preserve, Alaska. Harbour seals in this location did not sufficiently adjust source levels or acoustic parameters of vocalizations to compensate for acoustic masking. Instead, for every 1 dB increase in ambient noise, signal excess decreased by 0.84 dB, indicating a reduction in communication space when vessels passed. We suggest that harbour seals may already be acoustically advertising at or near a biologically maximal sound level, and therefore lack the ability to increase call amplitude to adjust to changes in their acoustic environment. This may have significant implications for this aquatically breeding pinniped, particularly for populations in high noise regions.
Metal Object, St Mawes Harbour, Cornwall
An iron object affixed onto the rocks at St Mawes, Cornwall. Perhaps once part of a ship. Created in Metashape with 37 photos. Source: Objaverse 1.0 / Sketchfab
Comparing distribution of harbour porpoises (Phocoena phocoena) derived from satellite telemetry and passive acoustic monitoring
<p>Data used for publication in Plos One. Two excel files. The satellite_filtered_data is the filtered satellite positions used for MaxEnt modelling in R. The CPOD_data_PPH is the raw C-POD data expressed here as porpoises positive hours (PPH) and can easily be converted to porpoise positive days (PPD).</p>
Data from: Repeatability of adaptation in sunflowers reveals that genomic regions harbouring inversions also drive adaptation in species lacking an inversion
<p>Local adaptation commonly involves alleles of large effect, which experience fitness advantages when in positive linkage disequilibrium (LD). Because segregating inversions suppress recombination and facilitate the maintenance of LD between locally adapted loci, they are also commonly found to be associated with adaptive divergence. However, it is unclear what fraction of an adaptive response can be attributed to inversions and alleles of large effect, and whether the loci within an inversion could still drive adaptation in the absence of its recombination-suppressing effect. Here, we use genome-wide association studies to explore patterns of local adaptation in three species of sunflower: <em>Helianthus annuus</em>, <em>H. argophyllus</em>, and <em>H. petiolaris</em>, which each harbour a large number of species-specific inversions. We find evidence of significant genome-wide repeatability in signatures of association to phenotypes and environments, which are particularly enriched within regions of the genome harbouring an inversion in one species. This shows that while inversions may facilitate local adaptation, at least some of the loci can still harbour mutations that make substantial contributions without the benefit of recombination suppression in species lacking a segregating inversion. While a large number of genomic regions show evidence of repeated adaptation, most of the strongest signatures of association still tend to be species-specific, indicating substantial genotypic redundancy for local adaptation in these species.</p>
Model of Dundee Harbour, 1945
This model shows Dundee's docks as they were some time after the Second World War. The model is signed and dated 1945 in the bottom left corner. This object was restored with grant aid from AIM, the Pilgrim Trust and restored by the Scottish Conservation Studio. Source: Objaverse 1.0 / Sketchfab
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Allen Brain Atlas
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