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30 results for “indicator organisms”
Dissolved Organic Carbon Concentration, Dissolved Organic Matter Optical Properties, and Water Quality Indicators in the Plum Island Estuary (PIE), Massachusetts, USA (2018-2023)
This is a data set of paired in situ measurements of water quality parameters, total suspended solids concentration, and concentration and optical properties (absorption coefficient spectra and fluorescence indices) of dissolved organic matter (DOM) collected between 2018 and 2023 in the Plum Island Estuary and nearshore waters. In situ water quality measurements (salinity, temperature, optical dissolved oxygen saturation, turbidity, and dissolved organic matter fluorescence) were collected with a water quality sonde from the surface (top 1 m of water column), along with corresponding samples that were processed and analyzed in the lab for dissolved organic carbon (DOC) concentration, chromophoric DOM (CDOM), absorption coefficient spectra, DOM excitation-emission matrix (EEM) fluorescence, and total suspended sediment (TSS) concentration. The data were used in multiple studies (see manuscripts listed below) focusing on the dynamics of DOC and CDOM in the Plum Island Estuary.
SI Figure 4: SEM images of either unwashed (left) or washed (right) E. antarcticus nematodes. A. Unwashed head region with arrows pointing to attached material and possible fungal hyphae. B. Washed head region with arrows pointing to the remaining attached material. C. Unwashed annules with arrows pointing to commonly attached foreign material. D. Washed annules with arrows pointing to remaining attached material. E. Unwashed somatic pore with arrows pointing to the common organic material. F. Washed vulva with an arrow pointing to remaining attached organic material. G. Unwashed cuticle with arrows showing a possible biofilm. H. Washed cuticle showing single attached cells indicated with arrows. I. Unwashed cuticle showing an off-axis line of attached material. J. Washed cuticle showing a similar off-axis line of material (as indicated with arrow) but reduced in quantity compared to the unwashed. in External and internal microbiomes of Antarctic nematodes are distinct, but more similar to each other than the surrounding environment
SI Figure 4: SEM images of either unwashed (left) or washed (right) E. antarcticus nematodes. A. Unwashed head region with arrows pointing to attached material and possible fungal hyphae. B. Washed head region with arrows pointing to the remaining attached material. C. Unwashed annules with arrows pointing to commonly attached foreign material. D. Washed annules with arrows pointing to remaining attached material. E. Unwashed somatic pore with arrows pointing to the common organic material. F. Washed vulva with an arrow pointing to remaining attached organic material. G. Unwashed cuticle with arrows showing a possible biofilm. H. Washed cuticle showing single attached cells indicated with arrows. I. Unwashed cuticle showing an off-axis line of attached material. J. Washed cuticle showing a similar off-axis line of material (as indicated with arrow) but reduced in quantity compared to the unwashed.
Fig. 2 in Trophic organization and fish assemblage structure as disturbance indicators in headwater streams of lower Sorocaba River basin, São Paulo, Brazil
Fig. 2. Average values and confidence interval (IC95%) of individuals' density, Shannon and Margalef Indices for each treatment, structurally complex streams (TT) and simplified stream (TC).
Fig. 1 in Trophic organization and fish assemblage structure as disturbance indicators in headwater streams of lower Sorocaba River basin, São Paulo, Brazil
Fig. 1. Map of the study area showing São Paulo State within Brazil (top left panel); Sorocaba River basin (shaded) and sample region (square) within São Paulo State (bottom left panel); and elevation profile and hydrography with position of the sampled sites (circles) in the sample region (right panel).
Fig. 3 in Trophic organization and fish assemblage structure as disturbance indicators in headwater streams of lower Sorocaba River basin, São Paulo, Brazil
Fig. 3. Projections of the Non-Metric Multidimensional Scaling (NMDS) and the smallest convex hulls that contain all data of the structurally complex streams (TT1, TT2 and TT3) and simplified stream (TC) according to a) taxonomic structure and b) trophic groups.
Text-fig. 42. Scanning electron microscope (SEM, a, b, e) and synchrotron radiation X-ray tomographic microscopy (SRXTM, c, d, f–g) images of "Tricarpellate flower sp. 1"; Catefica locality, Portugal. a, b) Flower bud in two different lateral views showing semiinferior ovary and perianth; c) Longitudinal section (orthoslice yz0340) through flower bud in (a and b) showing the semi-inferior gynoecium and perigynous insertion of other floral parts; d) Volume rendering of flower bud with pedicel preserved; note the depression/split in one of the corner apparently separating two perianth lobes of the outer perianth whorl (t-o) and exposing one tepal of the inner whorl (t-i); e) Flower bud with pedicel preserved; note broad tepals of the outer whorl (t-o) and tepal of the inner whorl abraded exposing a broad stamen (st); f, g) Transverse sections through flower bud in (a and b) at two different levels above the insertion of the perianth (f, rec-file 1310; g, xy0280) showing the trimerous organization of the flower and the free, laterally flattened carpels; yellow indicates the two whorls of the androecium, each with three stamens. Specimens, Catefica 50-S171520 (a–c, f), Catefica 50-S174902 (d), Catefica MM154-P0271 (e), Catefica 49-S175354 (g). Scale bars = 300 Μm (a–e). in The Early Cretaceous Mesofossil Flora Of Catefica, Portugal: Angiosperms
Text-fig. 42. Scanning electron microscope (SEM, a, b, e) and synchrotron radiation X-ray tomographic microscopy (SRXTM, c, d, f–g) images of "Tricarpellate flower sp. 1"; Catefica locality, Portugal. a, b) Flower bud in two different lateral views showing semiinferior ovary and perianth; c) Longitudinal section (orthoslice yz0340) through flower bud in (a and b) showing the semi-inferior gynoecium and perigynous insertion of other floral parts; d) Volume rendering of flower bud with pedicel preserved; note the depression/split in one of the corner apparently separating two perianth lobes of the outer perianth whorl (t-o) and exposing one tepal of the inner whorl (t-i); e) Flower bud with pedicel preserved; note broad tepals of the outer whorl (t-o) and tepal of the inner whorl abraded exposing a broad stamen (st); f, g) Transverse sections through flower bud in (a and b) at two different levels above the insertion of the perianth (f, rec-file 1310; g, xy0280) showing the trimerous organization of the flower and the free, laterally flattened carpels; yellow indicates the two whorls of the androecium, each with three stamens. Specimens, Catefica 50-S171520 (a–c, f), Catefica 50-S174902 (d), Catefica MM154-P0271 (e), Catefica 49-S175354 (g). Scale bars = 300 Μm (a–e).
Text-fig. 33. Synchrotron radiation X-ray tomographic microscopy (SRXTM, a, c) and scanning electron microscope (SEM, b, d) images of Paisia pantoporata (a–c) and?Paisia sp. (d); Catefica locality, Portugal. a) Lateral view (volume rendering) of flower showing the carpels (c) and the fleshy tepals (t) that have a slightly bulge near the base; b) Pollen grains in situ from stamen showing scattered pores and spiny supratectal ornamentation; c) Transverse section (orthoslice xz1024) through flower showing the pentamerous organization with five tepals (green) five stamens (yellow) and five carpels (red) all on the same radii; d) Lateral view of floral structure with three free carpels borne on the swollen receptacle that has poorly defined facets at the apex indicating the former presence of perianth parts. Specimens, Catefica 49-S101214 (a, c), Catefica 50-S170188 (b), Catefica MM125-P0292 (d). Scale bars = 300 Μm (a, c, d), 6 Μm (b). in The Early Cretaceous Mesofossil Flora Of Catefica, Portugal: Angiosperms
Text-fig. 33. Synchrotron radiation X-ray tomographic microscopy (SRXTM, a, c) and scanning electron microscope (SEM, b, d) images of Paisia pantoporata (a–c) and?Paisia sp. (d); Catefica locality, Portugal. a) Lateral view (volume rendering) of flower showing the carpels (c) and the fleshy tepals (t) that have a slightly bulge near the base; b) Pollen grains in situ from stamen showing scattered pores and spiny supratectal ornamentation; c) Transverse section (orthoslice xz1024) through flower showing the pentamerous organization with five tepals (green) five stamens (yellow) and five carpels (red) all on the same radii; d) Lateral view of floral structure with three free carpels borne on the swollen receptacle that has poorly defined facets at the apex indicating the former presence of perianth parts. Specimens, Catefica 49-S101214 (a, c), Catefica 50-S170188 (b), Catefica MM125-P0292 (d). Scale bars = 300 Μm (a, c, d), 6 Μm (b).
Text-fig. 8. Scanning electron microscope (SEM) images of staminate inflorescences and pollen of Proencistemon portugallicus gen. et sp. nov.; Catefica locality, Portugal. a, b) Staminate inflorescences composed of numerous tetrasporangiate stamens; each stamen lacks a filament and there is no clear indication of other floral organs; note apparently paired arrangement of stamens in (b) (asterisks); c) Pollen in situ in anther from specimen in (a) showing poorly defined trichotomocolpate aperture and semitectate-reticulate tectum; d) Detail of pollen from specimen in (a) showing narrow muri with beaded surface ornamentation; e) Distal and proximal views of pollen in situ in an anther fragment; f) Orbicules attached to surface of in situ pollen from anther fragment. Specimens, Catefica M282-P0341 (holotype, a, c, d), Catefica 150-S174257 (b), Catefica 50-S170393 (e, f). Scale bars = 600 Μm (a, b), 6 Μm (c, e), 1.5 Μm (d, f). in The Early Cretaceous Mesofossil Flora Of Catefica, Portugal: Angiosperms
Text-fig. 8. Scanning electron microscope (SEM) images of staminate inflorescences and pollen of Proencistemon portugallicus gen. et sp. nov.; Catefica locality, Portugal. a, b) Staminate inflorescences composed of numerous tetrasporangiate stamens; each stamen lacks a filament and there is no clear indication of other floral organs; note apparently paired arrangement of stamens in (b) (asterisks); c) Pollen in situ in anther from specimen in (a) showing poorly defined trichotomocolpate aperture and semitectate-reticulate tectum; d) Detail of pollen from specimen in (a) showing narrow muri with beaded surface ornamentation; e) Distal and proximal views of pollen in situ in an anther fragment; f) Orbicules attached to surface of in situ pollen from anther fragment. Specimens, Catefica M282-P0341 (holotype, a, c, d), Catefica 150-S174257 (b), Catefica 50-S170393 (e, f). Scale bars = 600 Μm (a, b), 6 Μm (c, e), 1.5 Μm (d, f).
Simultaneous determination method of 10 organophosphate esters in oyster, an environmental indicator organism
<p><span>Oyster is a common indicator organism of environment pollution. A method was built to simultaneously determine ten common commercial organophosphate ester flame retardants in oysters. After the careful optimization of conditions, the organophosphate esters (OPEs) in oyster sample were extracted with hexane assisted by ultrasound, purified with NH2 solid-phase extraction column, eluted with the mixture solution of dichloromethane and ethyl acetate at the ratio of 1:1 (v/v), and finally detected by gas chromatography coupled with tandem triple quadrupole mass spectrometry (GC–MS/MS). All the ten compounds in the concentrations ranging from 0.5 ng·mL-1 to 100 ng·mL-1 showed good linearity with their R2 higher than 0.9991. The limits of detection and limits of quantification for the organophosphate esters were from 0.03 ng·g-1 to 0.47 ng·g-1 (dry weight) and from 0.1 ng·g-1 to 1.56 ng·g-1 (dry weight), respectively. At the three spiking levels with five replicates, recoveries of organophosphate esters ranged from 82% to 108% with the relative standard deviation ranging from 0.9% to 6.4%. In the samples collected from mariculture farms, nine OPE compounds were detected in oysters with the concentration ranging from 6.52 ng·g-1 to 22 ng·g-1 (dry weight). It indicated the method was suitable for OPEs determination in oysters.</span></p>
Quantifying Progress: Metrics and Indicators for Measuring Digital Transformation Maturity in Organizations
<p><span>As organizations increasingly embark on digital transformation journeys, the need for effective metrics and indicators to measure progress and maturity becomes paramount. This paper investigates the development and application of metrics for quantifying digital transformation maturity in organizations. Through an extensive review of literature and examination of case studies, the paper identifies key dimensions and stages of digital maturity. It proposes a framework encompassing both quantitative and qualitative metrics that can be used to assess an organization's digital transformation journey. The paper explores challenges associated with defining meaningful metrics and offers insights into adapting measurement frameworks to diverse organizational contexts. By addressing this critical gap in the literature, the paper aims to provide practitioners, researchers, and decision-makers with a valuable resource for evaluating and benchmarking digital transformation progress, fostering a more nuanced understanding of the multifaceted nature of organizational digital maturity.</span></p>
Simultaneous determination method of 10 organophosphate esters in oyster, an environmental indicator organism
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Single-cell visualization indicates direct role of sponge host in uptake of dissolved organic matter
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FIGURE 5 in Electric organ discharges of South African Marcusenius species (Teleostei: Mormyridae) and their effectiveness as indicators of local species diversity
FIGURE 5. Male. Discriminant analysis (DA) of characters of the electric organ discharge (EOD) waveform of five male samples of South African Marcusenius species, compared to M. devosi specimens from Kenya (D symbols). B, S and P symbols, M. pongolensis specimens from different South African locations; K symbols, M. krameri. EOD waveform characters that were included in DA as given in Table 2, but Ndur excluded because of irrelevance in the male sample.
FIGURE 4 in Electric organ discharges of South African Marcusenius species (Teleostei: Mormyridae) and their effectiveness as indicators of local species diversity
FIGURE 4. Female. Discriminant analysis (DA) of characters of the electric organ discharge (EOD) waveform of five female plus juvenile samples of South African Marcusenius species, compared to M. devosi specimens from Kenya (D symbols). B, S and P symbols, M. pongolensis specimens from different South African locations; K symbols, M. krameri. EOD waveform characters that were included in DA as given in Table 3, but PNsep excluded because of irrelevance in the female sample.
FIGURE 2 in Electric organ discharges of South African Marcusenius species (Teleostei: Mormyridae) and their effectiveness as indicators of local species diversity
FIGURE 2. Electric organ discharge of a Marcusenius krameri with the positive peak amplitude normalized to 1 V, as an example for showing the characters analysed and their definitions. EOD shown was field-recorded from male specimen Mogol27 (ZSM 39535(7) from Mokolo River).
FIGURE 1. A in Electric organ discharges of South African Marcusenius species (Teleostei: Mormyridae) and their effectiveness as indicators of local species diversity
FIGURE 1. A, partial geography of southern Africa showing localities where fish were sampled. B, partial geography of South Africa. Locality 1, Tana River, Kenya, Marcusenius devosi. Locality 2, Mokolo River, M. krameri. Locality 3, Sabie River, M. pongolensis. Locality 4, Kosi Bay area, Kosi River system, M. pongolensis. Locality 5, Pongola River, M. pongolensis. Locality 6, Type locality for M. pongolensis. Locality 7, Mhlatuze River, M. caudisquamatus.
FIGURE 3 in Electric organ discharges of South African Marcusenius species (Teleostei: Mormyridae) and their effectiveness as indicators of local species diversity
FIGURE 3. Electric organ discharges (EOD) of a male bulldog (below) and a female specimen (above) in each panel. Abscissa, time bar is 2 ms for all panels, ordinate, amplitude (V). EODs are normalised to the same positive peak amplitude from baseline = 1 V. Kosi Bay, Marcusenius pongolensis from the Kosi System, specimens PM09A90 (female, SL 10.9 cm) and PM09A91 (male, SL 16.2 cm), SAIAB 88637(2). Sabie River, M. pongolensis, specimens 8Sabi (male, SL 13.4 cm) and 9Sabi (female, SL 12.3 cm), both SAIAB 54446(11). Pongola River, M. pongolensis, specimens Pon02 (male, SL 18 cm), SAIAB 79148(5), and Pon09 (female, SL 15.5 cm), ZSM 35087(5). Witrivier River, M. pongolensis, specimen Wit 02, male, SL 18 cm, and Wit 01, female, SL 9.9 cm, both SAIAB 88846(2). Tana River, M. devosi, specimens SAIAB 79139(14), Ta32na, male, SL 10.1 cm, and ZSM 35092, Ta11na, female, SL 11.2 cm. Mhlatuze River, M. caudisquamatus, specimen PM09A242, male, SL 17.5 cm, and PM09A238, female, SL 10.2 cm, both SAIAB 191225(6). Mokolo River, M. krameri, specimen Mogol27, ZSM 39535(7), male, SL 9 cm, and Mogol29, SAIAB 88888(15), female, SL 9.7 cm.
Figure 4 in Community properties of benthic molluscs as indicators of environmental stress induced by organic enrichment
Figure 4. MDS plots of Functional Feeding Groups (FFG) where mean abundance of each group is superimposed.
Figure 3 in Community properties of benthic molluscs as indicators of environmental stress induced by organic enrichment
Figure 3. MDS plot (a) and cluster analysis (b) of species abundances highlighting three main groups of areas.
Figure 2 in Community properties of benthic molluscs as indicators of environmental stress induced by organic enrichment
Figure 2. Probability funnels of diversity indices Δ+ (a) and Λ+ (b) for all sampling stations and seasons in the study area.
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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