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15 results for “macrobenthos”
Macrobenthos Sampling data for the North Inlet Estuary, Georgetown,South Carolina, from 1981 to 1992 North Inlet LTER (Reformatted to the ecocomDP Design Pattern)
This data package is formatted as an ecocomDP (Ecological Community Data Pattern). For more information on ecocomDP see https://github.com/EDIorg/ecocomDP. This Level 1 data package was derived from the Level 0 data package found here: https://pasta.lternet.edu/package/metadata/eml/knb-lter-nin/9/1. The abstract below was extracted from the Level 0 data package and is included for context: This data package consists of Macrobenthos Sampling Data for North Inlet Stations Bread and Butter Creek from 1981 to 1992, and Debidue Creek from 1981 to 1984, North Inlet LTER. The purpose of this study was to document the composition and abundance of macrobenthic subtidal populations over time at one mud and one sand site. Macrobenthos was defined here as those animals retained on a 0.5 mm mesh screen.
Рис. 4. Распределение станций отбора проб по глубине и типу грунта (круЖком обведены станции, на которых макробентос не обнаруЖен; БО – биогенные остатки, ГМ – галька мелкаЯ, Гр – гравий, И – ил, П – песок). Fig. 4. Distribution of sampling stations by depth and type of bottom sediments (circles are around the stations where no macrobenthos was detected; БО – biogenic residues, ГМ – pebbles, Гр – gravel, И – silt, П – sand). in Species composition and distribution of bivalve mollusks in plankton and benthos in Nevelsky Strait in summer
Рис. 4. Распределение станций отбора проб по глубине и типу грунта (круЖком обведены станции, на которых макробентос не обнаруЖен; БО – биогенные остатки, ГМ – галька мелкаЯ, Гр – гравий, И – ил, П – песок). Fig. 4. Distribution of sampling stations by depth and type of bottom sediments (circles are around the stations where no macrobenthos was detected; БО – biogenic residues, ГМ – pebbles, Гр – gravel, И – silt, П – sand).
Рис. 5. АналиЗ линейной коррелЯции параметров макробентоса от доминируюЩей фракции в пробе грунта (А, Б) и глубины (В, Г). Fig. 5. Analysis of the linear correlation of macrobenthos parameters with the dominant fraction in the bottom sample (А, Б) and depth (В, Г). in Species composition and distribution of bivalve mollusks in plankton and benthos in Nevelsky Strait in summer
Рис. 5. АналиЗ линейной коррелЯции параметров макробентоса от доминируюЩей фракции в пробе грунта (А, Б) и глубины (В, Г). Fig. 5. Analysis of the linear correlation of macrobenthos parameters with the dominant fraction in the bottom sample (А, Б) and depth (В, Г).
Figure 7 in Long - term variations in macrobenthos diversity at the Istanbul Strait's (Bosporus) outlet area of the Black Sea
Figure 7. Shannon (H′) & evenness (J) indices for T. stroemi - A. stepanovi communities at the Bosporus outlet area (depth 70 - 98 m – 1958, depth 96 - 152 m - 2010*) - (A); & M. phaseolina (depth 83-113м -1960, depths 116-117 м - 2010*)-(B) communities at the Bosporus outlet area.
Figure 2 in Long - term variations in macrobenthos diversity at the Istanbul Strait's (Bosporus) outlet area of the Black Sea
Figure 2. Dependence of the abundance and species richness of the benthos in the Bosporus outlet area on water depth and on the dissolved-oxygen concentration measured just above the sediment: RV 'Maria S. Merian' 15/1, April-May 2010.
Figure 1 in Long - term variations in macrobenthos diversity at the Istanbul Strait's (Bosporus) outlet area of the Black Sea
Figure 1. Macrobenthos sampling stations in the Istanbul Strait"s (Bosporus) outlet area of the Black Sea (RV 'Maria S. Merian' 15/1, April-May 2010) – (a), July 1958 and June 1960 RV "Academic Kovalevsky" cruises in the Bosporus area – (b).
Figure 6 in Long - term variations in macrobenthos diversity at the Istanbul Strait's (Bosporus) outlet area of the Black Sea
Figure 6. Simpson (D) & Berger-Parker (B\P) indices for T. stroemi – A, stepanovi *) - (A); & M. phaseolina (depth 83-113м -1960, depths 116-117 м - 2010*)-(B) communities at the Bosporus outlet area.
Figure 4 in Long - term variations in macrobenthos diversity at the Istanbul Strait's (Bosporus) outlet area of the Black Sea
Figure 4. Plots of log-normal model for T. stroemi – A. stepanovi (depth 70 - 98 m – 1958, depth 96 - 152 m - 2010*) - (a); M. phaseolina communities (depth 83-113м -1960, depths 116-117 м - 2010*)-(b): (y axis) - cumulative % of species against (x axis) - individuals per species in geometric classes.
Figure 8 in Long - term variations in macrobenthos diversity at the Istanbul Strait's (Bosporus) outlet area of the Black Sea
Figure 8. Menhinick (DMn) & Margalef (DMG) indices for T. stroemi – A. stepanovi (depth 70 - 98 m – 1958, depth 96 - 152 m - 2010*) *) - (A); & M. phaseolina (depth 83-113м -1960, depths 116-117 м - 2010*)-(B) communities at the Bosporus outlet area.
Figure 5 in Long - term variations in macrobenthos diversity at the Istanbul Strait's (Bosporus) outlet area of the Black Sea
Figure 5. Structure of density for T. stroemi – A. stepanovi (depth 70 - 98 m – 1958, depth 96 - 152 m - 2010*) - (a); & M. phaseolina communities (depth 83-113м -1960, depths 116-117 м - 2010*)-(b).
Linked collectors and determiners for: MACROBENTHOS COMPOSITION FROM THE RIO LAGARTOS HYPERHALINE COASTAL LAGOON SYSTEM, YUCATAN, MEXICO.
Natural history specimen data linked to collectors and determiners held within, "MACROBENTHOS COMPOSITION FROM THE RIO LAGARTOS HYPERHALINE COASTAL LAGOON SYSTEM, YUCATAN, MEXICO". Claims or attributions were made on Bionomia by volunteer Scribes, <a href="https://bionomia.net/dataset/4bdc7171-c006-41b8-b3bf-e6f5227206b3">https://bionomia.net/dataset/4bdc7171-c006-41b8-b3bf-e6f5227206b3</a> using specimen data from the dataset aggregated by the Global Biodiversity Information Facility, <a href="https://gbif.org/dataset/4bdc7171-c006-41b8-b3bf-e6f5227206b3">https://gbif.org/dataset/4bdc7171-c006-41b8-b3bf-e6f5227206b3</a>. Formatted as a Frictionless Data package.
Macrobenthos Sampling data for the North Inlet Estuary, Georgetown,South Carolina, from 1981 to 1992 North Inlet LTER (Reformatted to a Darwin Core Archive)
This data package is formatted as a Darwin Core Archive (DwC-A, event core). For more information on Darwin Core see https://www.tdwg.org/standards/dwc/. This Level 2 data package was derived from the Level 1 data package found here: https://pasta.lternet.edu/package/metadata/eml/edi/353/2, which was derived from the Level 0 data package found here: https://pasta.lternet.edu/package/metadata/eml/knb-lter-nin/9/1. The abstract below was extracted from the Level 0 data package and is included for context: This data package consists of Macrobenthos Sampling Data for North Inlet Stations Bread and Butter Creek from 1981 to 1992, and Debidue Creek from 1981 to 1984, North Inlet LTER. The purpose of this study was to document the composition and abundance of macrobenthic subtidal populations over time at one mud and one sand site. Macrobenthos was defined here as those animals retained on a 0.5 mm mesh screen.
Supplementary material 2 from: Van den Bulcke L, De Backer A, Ampe B, Maes S, Wittoeck J, Waegeman W, Hostens K, Derycke S (2021) Towards harmonization of DNA metabarcoding for monitoring marine macrobenthos: the effect of technical replicates and pooled DNA extractions on species detection. Metabarcoding and Metagenomics 5: e71107. https://doi.org/10.3897/mbmg.5.71107
Tables S1–S8
Supplementary material 1 from: Van den Bulcke L, De Backer A, Ampe B, Maes S, Wittoeck J, Waegeman W, Hostens K, Derycke S (2021) Towards harmonization of DNA metabarcoding for monitoring marine macrobenthos: the effect of technical replicates and pooled DNA extractions on species detection. Metabarcoding and Metagenomics 5: e71107. https://doi.org/10.3897/mbmg.5.71107
Figures S1–S14
Macrobenthos Sampling data for the North Inlet Estuary, Georgetown,South Carolina, from 1981 to 1992 North Inlet LTER
This data package consists of Macrobenthos Sampling Data for North Inlet Stations Bread and Butter Creek from 1981 to 1992, and Debidue Creek from 1981 to 1984, North Inlet LTER. The purpose of this study was to document the composition and abundance of macrobenthic subtidal populations over time at one mud and one sand site. Macrobenthos was defined here as those animals retained on a 0.5 mm mesh screen.
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