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opennotspecifiedMar 2013View details →

Subspecies and Distribution. M.a.assamensisMcClelland,1839—S&SEAsia,200-2750mabovesealevel,EofthegreatbendoftheBrahmaputraRiver,inSWChina(SEXizangAutonomousRegion[=Tibet],SWYunnan,Guizhou,SWGuangxiprovinces),NEIndia(EArunachalPradesh,EAssam,Nagaland,Meghalaya,M.a.,Mizoram,andTripurastates),SandEthroughN&EMyanmar,N&WThailand,Laos,andNVietnam. M. a. pelops Hodgson, 1840 — Himalayas up to 3100 m above sea level, from C Nepal (W limit Tipling, 83° 36' E) E through NE India (N West Bengal, Sikkim, W Assam states), and Bhutan (E limit M.a. River, 90° 58" E), with a widely disjunct record, of what may be a geographic relict, in coastal SW Bangladesh (Sundarbans). in Cercopithecidae

Subspecies and Distribution. M.a.assamensisMcClelland,1839—S&SEAsia,200-2750mabovesealevel,EofthegreatbendoftheBrahmaputraRiver,inSWChina(SEXizangAutonomousRegion[=Tibet],SWYunnan,Guizhou,SWGuangxiprovinces),NEIndia(EArunachalPradesh,EAssam,Nagaland,Meghalaya,M.a.,Mizoram,andTripurastates),SandEthroughN&EMyanmar,N&WThailand,Laos,andNVietnam. M. a. pelops Hodgson, 1840 — Himalayas up to 3100 m above sea level, from C Nepal (W limit Tipling, 83° 36' E) E through NE India (N West Bengal, Sikkim, W Assam states), and Bhutan (E limit M.a. River, 90° 58" E), with a widely disjunct record, of what may be a geographic relict, in coastal SW Bangladesh (Sundarbans).

Figure 2 in The current state of DNA barcoding of macroalgae in the Mediterranean Sea: presently lacking but urgently required

Figure 2: Rhodophyta data by country from Taxonomy page on the Barcode of Life Data System (BOLD). Source: http://www.boldsystems.org/index.php/TaxBrowser_Home

Figure 6 in The current state of DNA barcoding of macroalgae in the Mediterranean Sea: presently lacking but urgently required

Figure 6: Pinnate fronds of Caulerpa taxifolia var. distichophylla growing among the white flabellate blades of Padina sp. Photo taken in Maltese waters in June 2017.

Figure 1 in The current state of DNA barcoding of macroalgae in the Mediterranean Sea: presently lacking but urgently required

Figure 1: Polygon used to delineate the Mediterranean Sea whilst searching for records in the Barcode of Life Data System (BOLD). Source: http://www.boldsystems.org/

Figure 5 in The current state of DNA barcoding of macroalgae in the Mediterranean Sea: presently lacking but urgently required

Figure 5: DNA barcoding of macroalgae by Mediterranean country: Italy, France, Croatia, Spain and Greece lead in the literature-based results.

Figure 4 in The current state of DNA barcoding of macroalgae in the Mediterranean Sea: presently lacking but urgently required

Figure 4: DNA barcoding by country obtained from the literature-based results of 121 papers: USA, Canada, Korea, Australia, Chile and France lead in the number of barcodes world-wide.

opencc-zeroDec 2012View details →

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Data from: Wintering sea duck distribution along the Atlantic coast of the United States

Although monitoring data for sea ducks (Tribe Mergini) are limited, current evidence suggests that four of the most common species wintering along the eastern coast of the United States—long-tailed duck Clangula hyemalis, white-winged scoter Melanitta fusca, surf scoter Melanitta perspicillata, and black scoter Melanitta americana—may be declining, while the status of American common eider Somateria mollissima dresseri is uncertain. The apparent negative trends, combined with the fact that sea duck life histories are among the most poorly documented of North American waterfowl, have led to concerns for these species and questions about the impacts of human activities, such as hunting, as well as catastrophic events and environmental change. During winter, thousands of sea ducks are found along the U.S. Atlantic coast, where they may be affected by proposed wind-power development, changes to marine traffic, aquaculture practices, sand mining, and other coastal development. Possible impacts are difficult to quantify because traditional winter waterfowl surveys do not cover many of the marine habitats used by sea ducks. Thus, the U.S. Fish and Wildlife Service conducted an experimental survey of sea ducks from 2008 to 2011 to characterize their winter distributions along the U.S. Atlantic coast. Each year, data were collected on 11 species of sea ducks on >200 transects, stretching from Maine to Florida. In this paper, we describe distribution of common eider, long-tailed duck, white-winged scoter, surf scoter, and black scoter. Densities of the two species with the most northerly distribution, white-winged scoter and common eider, were highest near Cape Cod and Nantucket. Long-tailed duck was most abundant around Cape Cod, Nantucket Shoals, and in Chesapeake Bay. Surf scoter also concentrated within Chesapeake Bay; however, they were additionally found in high densities in Delaware Bay, and along the Maryland–Delaware outer coast. Black scoter, the most widely distributed species, occurred at high densities along the South Carolina coast and the mouth of Chesapeake Bay. Spatial patterns of high-density transects were consistent among years for all species except black scoter, which exhibited the most interannual variation in distribution. The distance from land, depth, and bottom slope where flocks were observed varied among species and regions, with a median distance of 3.8 km from land along the coastal transects and 75% of flocks observed over depths of <16 m. Common eider and long-tailed duck were observed closer to shore and over steeper ocean bottoms than were the three scoter species. Our results represent the first large-scale quantitative description of winter sea duck distribution along the U.S. Atlantic coast, and should guide the development of sea duck monitoring programs and aid the assessment of potential impacts of ongoing and proposed offshore development.

opennotspecifiedMay 2021View details →

FIGURE. Typical habitats of Ramalina species on northern South America. A. High paramo, Laguna Anteojos, Sierra Nevada de Merida, where grows on rocks R. anteojina at 4100 m. B. Sub-paramo (timberline), La Aguada, Sierra Nevada de Merida, 3100 m, where are found R. dictyota and R. reducta on shrubs. C. Andean cloud forest, La Victoria, Sierra Nevada de Merida where R. cochlearis, R. cumanensis and R. victoriana are found growing as epiphytes. D. Populations of R. usnea, R. morrocoyensis and R. paradisensis growing as epiphytes on mangroves and Suriana maritima at sea level, National Park Morrocoy, state Falcón; the latter two species are known only from this locality. E. Ramalina usnea is the only species of this genus reported from the Alto Orinoco, Amazonas, near La Esmeralda, 150 m, growing as corticolous in submontane forests, at the top of the picture the Cerro Duida. F. Xerophytic forests from the National Park Cerro Santa Ana, state Falcón, where Ramalina santanensis and R. microphylla are known only growing on soil and rocks at 200–400 m. Photos V. Marcano. in The genus Ramalina Acharius (Ascomycota, Lecanoromycetes, Ramalinaceae) in northern South America

FIGURE. Typical habitats of Ramalina species on northern South America. A. High paramo, Laguna Anteojos, Sierra Nevada de Merida, where grows on rocks R. anteojina at 4100 m. B. Sub-paramo (timberline), La Aguada, Sierra Nevada de Merida, 3100 m, where are found R. dictyota and R. reducta on shrubs. C. Andean cloud forest, La Victoria, Sierra Nevada de Merida where R. cochlearis, R. cumanensis and R. victoriana are found growing as epiphytes. D. Populations of R. usnea, R. morrocoyensis and R. paradisensis growing as epiphytes on mangroves and Suriana maritima at sea level, National Park Morrocoy, state Falcón; the latter two species are known only from this locality. E. Ramalina usnea is the only species of this genus reported from the Alto Orinoco, Amazonas, near La Esmeralda, 150 m, growing as corticolous in submontane forests, at the top of the picture the Cerro Duida. F. Xerophytic forests from the National Park Cerro Santa Ana, state Falcón, where Ramalina santanensis and R. microphylla are known only growing on soil and rocks at 200–400 m. Photos V. Marcano.

opencc-by-4.0Jul 2023View details →

A sea state dependent gas transfer velocity for CO$_2$ unifying theory, model and field data

Dataset for "A sea state dependent gas transfer velocity for CO2 unifying theory, model and field data" WaveWatch III simulated  significant wave height (Hs, unit:m), volume of entrained air ('wva', unit m/s), 10-meter wind vector  ( 'uwnd','vwnd', unit, m/s) for 9 datasets from 11 cruises. The information of dataset is shown in name of each file.

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Data from: Wintering sea duck distribution along the Atlantic coast of the United States

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publicMar 2013View details →

Figure 3 in The current state of DNA barcoding of macroalgae in the Mediterranean Sea: presently lacking but urgently required

Figure 3: Total number of DNA barcodes obtained from the literature-based results of 121 papers.

opencc-by-4.0Dec 2014View details →

Figure 2 in Shallow-water polychaete assemblages in the northwestern Mediterranean Sea and its possible use in the evaluation of good environmental state

Figure 2. Cluster analysis of polychaete fauna for the Gulf of Lions region (France; upper graph) and the Northern Mediterranean Spanish coast (Spain; lower graph). Asterisk observed in lower graph indicates stations associated with the Detritic Sand Community (DS)

opencc-by-4.0Jun 2024View details →

The state of the AMOC revealed from the Subpolar North Atlantic Sea Surface Salinity

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opencc-by-4.0Oct 2017View details →

Figure 2 in Ostracods in the plankton of the Sivash Bay (the Sea of Azov) during its transformation from brackish to hypersaline state

Figure 2. Cyprideis torosa, female and male (A, B); Loxoconcha bulgarica, male and female (C, D); Loxoconcha aestuarii, female and male (E, F); Cytherois cepa, female and male (G, H); Leptocythere devexa, female and male (I, J).

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Data from: Geometric control of ciliated band regulatory states in the sea urchin embryo

The trapezoidal ciliated band (CB) of the postgastrular sea urchin embryo surrounds the oral ectoderm, separating it from adjacent embryonic territories. Once differentiated, the CB is composed of densely arranged cells bearing long cilia that endow the larva with locomotion and feeding capability. The spatial pattern from which the CB will arise is first evidenced during pregastrular stages by expression of the pioneer gene onecut. Immediately after gastrulation, the CB consists of four separate regulatory state domains, each of which express a unique set of transcription factors. These are: (1) The oral apical CB, located within the apical neurogenic field; (2) The animal lateral CB, which bilaterally separates the oral from aboral ectoderm; (3) The vegetal lateral CB, which bilaterally serves as signaling centers; and (4) The vegetal oral CB, which delineates the boundary with the underlying endoderm. Remarkably, almost all of the regulatory genes specifically expressed within these domains are down-regulated by interference with Soxb1 expression, implying activation by this factor in common. In this work we show how the boundaries of the CB subdomains are established, and thus ascertain the design principle by which the geometry of this unique and complex regulatory state pattern is genomically controlled. Each of these boundaries, on either side of the CB, is defined by spatially confined transcriptional repressors, the products of regulatory genes operating across the border of each subdomain. In total, this requires deployment of about ten different repressors, which we identify in this work, thus exemplifying the high informational requirement of spatial regulatory organization during embryogenesis.

opencc-zeroDec 2014View details →