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opencc-by-4.0Sep 2017View details →

Fig. 2 in Seasonal abundance and spatial distribution of Diaphania hyalinata (Lepidoptera: Crambidae) on yellow squash in south Florida

Fig. 2. Weekly abundance (mean ± SE per 2 leaves) of total Diaphania hyalinata larvae on yellow squash during 4 planting seasons from 26 May through 30 Dec 2014. Means topped by the same lowercase letter are not significantly different (P> 0.05) (analysis of variance and Waller–Duncan K-ratio test). Bars above and below means represent standard errors.

opencc-by-4.0Sep 2017View details →

Fig. 1 in Seasonal abundance and spatial distribution of Diaphania hyalinata (Lepidoptera: Crambidae) on yellow squash in south Florida

Fig. 1. Weekly abundance (mean ± SE per 2 leaves) of small (L1 + L2), medium (L3 + L4), large (L5) Diaphania hyalinata larvae on yellow squash from a) 26 May through 16 Jun, b) 18 Jul through 8 Aug, c) 1 Sep through 22 Sep, and d) 9 Dec through 30 Dec 2014. Means topped by the same uppercase letter are not significantly different (P> 0.05) between larval sizes, and means topped by the same lowercase letter are not significantly different (P> 0.05) between sampling dates (analysis of variance and Waller–Duncan K-ratio test). Bars above and below means represent standard errors.

opencc-by-4.0Dec 2015View details →

Fig. 3 in Seasonal variation in the abundance and distribution of ticks that parasitize Microcebus griseorufus at the BezàMahafaly Special Reserve, Madagascar

Fig. 3. Possible life cycle of H. lemuris. Peak activity for larvae occurs in May, but larvae may be found feeding into June and October. Larvae attach to Microcebus hosts and after a blood meal, fall off and molt into nymphs. Nymphs are active and feed on Microcebus throughout the dry season and likely feed on other lemurs during part of the wet season. Adult-stage ticks remain active during the wet season, feeding on larger-bodied lemurs, such as L. catta, and P. verreauxi. Engorged females fall off and lay eggs in leaf litter. It is possible that all four stages can diapause if no suitable hosts or conditions are found (gray dotted line). Mice or rats may also serve as hosts to larvae during the dry season.

opencc-by-4.0Dec 2015View details →

Fig. 1. Monthly averages for A in Seasonal variation in the abundance and distribution of ticks that parasitize Microcebus griseorufus at the BezàMahafaly Special Reserve, Madagascar

Fig. 1. Monthly averages for A) tick intensity on mouse lemurs as it compares to B) rainfall and C) temperature, during the year-long study season. Shaded area indicates months included in the dry season. Environmental data were collected daily.

opencc-by-4.0Dec 2015View details →

Fig. 2 in Seasonal variation in the abundance and distribution of ticks that parasitize Microcebus griseorufus at the BezàMahafaly Special Reserve, Madagascar

Fig. 2. Differences in infestation rates at Parcel 1 by A) sex B) substrate C) males and substrate and D) females and substrate. * indicates P <0.05, **P <0.01; ***P <0.001 and compares variables on the x-axis.

opencc-by-4.0Dec 2023View details →

Figure 2. – Mean abundance per 750 m2 in Changes in distribution patterns of two vulnerable fish species (Epinephelus marginatus and Sciaena umbra) in the Scandola marine reserve (Corsica, NW Mediterranean): a possible effect of increased boat tourism

Figure 2. – Mean abundance per 750 m2 (± SE) of the dusky grouper Epinephelus marginatus (A) and the brown meagre Sciaena umbra (B) according to protection level at Scandola in 2012 and 2018. IR: integral reserve, BZ: buffer zone, UP: unprotected zone. Interannual difference are indicated for each protection level, *: significant at p <0.05, ns: not significant.

Figure 2 in Abundance And Distribution Of The Philippine Brown Deer (Rusa Marianna Desmarest, 1822) In The Obu Manuvu Ancestral Domain, Mindanao Island, Philippines

Figure 2. Philippine Brown Deer (Rusa marianna Desmarest, 1822) detected through camera trapping in (A) Salaysay, (B) Tawan-Tawan, and (C) Carmen. A (D) deceased female deer was also documented in Carmen, Davao City.

Figure 4 in Abundance And Distribution Of The Philippine Brown Deer (Rusa Marianna Desmarest, 1822) In The Obu Manuvu Ancestral Domain, Mindanao Island, Philippines

Figure 4. Map showing the location of the camera trap stations according to (A) forest and non-forest ecosystems, (B) forest cover, (C) elevation ranges, (D) slope ranges, and (E) water bodies in the Obu Manuvu Ancestral Domain, Davao City, Philippines.

Figure 5 in Abundance And Distribution Of The Philippine Brown Deer (Rusa Marianna Desmarest, 1822) In The Obu Manuvu Ancestral Domain, Mindanao Island, Philippines

Figure 5. Conservation threats observed in the study areas: (A) deforestation, (B) hunting, (C) abandoned human camps, and (D) pollution.

Figure 4 in Abundance And Distribution Of The Philippine Brown Deer (Rusa Marianna Desmarest, 1822) In The Obu Manuvu Ancestral Domain, Mindanao Island, Philippines

Figure 4 in Abundance And Distribution Of The Philippine Brown Deer (Rusa Marianna Desmarest, 1822) In The Obu Manuvu Ancestral Domain, Mindanao Island, Philippines

opencc-by-4.0Oct 2015View details →

Figure 3 in Spatiotemporal distribution, abundance, and species-environment relationships of Scyphozoa (Cnidaria) species in Hisarönü, Marmaris, and Fethiye bays (Muğla, Turkey

Figure 3. RDA ordination plot for Scyphozoa species, environmental parameters, sampling months, and stations. Sampling stations in RDA plot indicated with □: Hisarönü 1; ■: Hisarönü 2; O: Marmaris 1; ●: Marmaris 2; ◇: Marmaris 3; ◆: Marmaris 4; ×: Marmaris 5; ∆: Fethiye 1; △: Fethiye 2; ▲: Fethiye 3. Scyphozoa species indicated by the following abbreviations: Aa: Aurelia aurita; Ct: Cotylorhiza tuberculata; Ca: Cassiopea andromeda. Sampling months in RDA plot indicated with: 1: September 2011; 2: October 2011; 3: November 2011; 4: December 2011; 5: January 2012; 6: February 2012; 7: March 2012; 8: April 2012; 9: May 2012; 10: June 2012; 11: July 2012; 12: August 2012; 13: September 2012; 14: October 2012. See Table 4 for abbreviations of environmental variables.

opencc-by-4.0Nov 2022View details →

Fig. 2 in South American Sea Lions Otaria flavescens, a good indicator of relative spatial and temporal changes in the distribution and abundance of marine resources?

Fig. 2. Frequency of occurrence of the main prey taxa in the diet of Otaria flavescens (Shaw, 1800) from the San MatÍas Gulf, Argentina.

opencc-by-4.0Jul 2024View details →

Coccolithophore Abundance, Size, Carbon And Distribution Estimates (CASCADE)

<div>CASCADE is a global dataset for 139 extant coccolithophore taxonomic units. CASCADE includes a trait database (size and cellular organic and inorganic carbon contents) and taxonomic-specific global spatiotemporal distributions (Lat/Lon/Depth/Month/Year) of coccolithophore abundance and organic and inorganic carbon stocks. CASCADE covers all ocean basins over the upper 275 meters, spans the years 1964-2019 and includes 33,119 taxonomic-specific abundance observations. Within CASCADE, we characterise the underlying uncertainties due to measurement errors by propagating error estimates between the different studies.</div> <div> </div> <div>Full details of the data set are provided in the associated Scientific Data manuscript. The repository contains five main folders: 1) "Classification", which contains YAML files with synonyms, family-level classifications, and life cycle phase associations and definitions; 2) "Concatenated literature", which contains the merged datasets of size, PIC and POC and which were corrected for taxonomic unit synonyms; 3) "Resampled cellular datasets", which contains the resampled datasets of size, PIC and POC in long format as well as a summary table; 4) "Gridded data sets", which contains gridded datasets of abundance, PIC and POC; 5) "Species lists", which contains spreadsheets of the "common" (>20 obs) and "rare" (<20 obs) species and their number of observations.</div> <div> </div> <div>The CASCADE data set can be easily reproduced using the scripts and data provided in the associated github repository: <a title="Opens in new tab" href="https://github.com/nanophyto/CASCADE/tree/v0.1.1" target="_blank" rel="noopener">https://github.com/nanophyto/CASCADE/</a> (<a href="../doi/10.5281/zenodo.12797197">zenodo.12797197</a>)</div> <div> <p>Correspondence to: Joost de Vries, joost.devries@bristol.ac.uk</p> <p>v.3 fixes:</p> <ol> <li><em>actually</em> fixes Guerreiro et al., 2023 longitude issue</li> <li>replaces negative PIC predictions from GLM with NA (an issue with some small HOL species)</li> </ol> <p>v.2 fixes:</p> <p>1. The wrongly specified <em>S. neapolitana</em> was removed from synonyms.yml (this species is now<em> S. nana</em>)<br>2. Longitudes were corrected for Guerreiro et al., 2023<br>3. A double entry for Dimizia et al., 2015 was fixed<br>4. Units in Sal et al., 2013 were correct to cells/L (previously cells/ml)<br>5. Data from Sal et al., 2013 was re-done, as some species were missing<br>6. Duplicate entries from Baumann et al., 2000 were dropped</p> </div>

opencc-by-4.0Mar 2010View details →

Figure 15-16. Rank abundance chart for Phanaeini species. 15 in Diversity and distribution of the scarab beetle tribe Phanaeini in the northern states of the Brazilian Northeast (Coleoptera: Scarabaeidae: Scarabaeinae)

Figure 15-16. Rank abundance chart for Phanaeini species. 15) Recorded in Ceará during February-June 2008. Light grey indicates specimens observed in Atlantic forest; dark grey indicates specimens observed in caatinga. 16) Recorded in Maranhão during February and May 2008. All specimens were broadly observed in cerrado habitat (see species accounts for details).

Figure 9 in Micromammalian distribution and abundance in the Western Cape Province, South Africa, as evidenced by Barn owls Tyto alba (Scopoli)

Figure 9. Proportional representation of 3-month age classes (C1–8) of Otomys irroratus at Geelbek in the West Coast National Park by month and season.

Figure 10 in Micromammalian distribution and abundance in the Western Cape Province, South Africa, as evidenced by Barn owls Tyto alba (Scopoli)

Figure 10. Proportion of total measured Otomys irroratus individuals born per month at Geelbek in the West Coast National Park during 1984–8, based on material collected during 1985–8, compared with mean monthly rainfall at Langebaanweg for the same period.

Figure 8 in Micromammalian distribution and abundance in the Western Cape Province, South Africa, as evidenced by Barn owls Tyto alba (Scopoli)

Figure 8. Variation in (A) maxillary and (B) mandibular alveolar length in Tatera afra from selected sites with mean annual precipitation increasing from left to right. SFN and SFS, Steenbokfontein North and South (139 mm); AGA, Andriesgrond (248 mm); BBS, Blombos (464 mm); KFN, Kraaifontein (569 mm); STB, Stellenbosch Airfield (629 mm).

Figure 6 in Micromammalian distribution and abundance in the Western Cape Province, South Africa, as evidenced by Barn owls Tyto alba (Scopoli)

Figure 6. Dominant species in quarter-degree squares where the micromammalian sample comprises>100 individuals. Blank squares yielded samples of fewer than 100 individuals. Ch, Cryptomys hottentotus; Da, Desmodillus auricularis; Mm, Mus minutoides; Mv, Myosorex varius; Oi, Otomys irroratus; Rp, Rhabdomys pumilio; Sv, Suncus varilla; Ta, Tatera afra.

Figure 1 in Micromammalian distribution and abundance in the Western Cape Province, South Africa, as evidenced by Barn owls Tyto alba (Scopoli)

Figure 1. Location of the Western Cape Province in South Africa (A) and of Western Cape Province quarterdegree squares yielding Tyto alba pellet samples discussed in this paper (B).