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3,688 results for “Milling”
Year 2005, 15 or 30 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2005 continuous measurements, every 15-30 minutes, were made of stage in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Some water temperature, conductivity, and dissolved oxygen numbers during the summer. Discharge is determined from stage using discharge vs stage regressions.
Year 2006, 10 or 30 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2006 continuous measurements, every 10-30 minutes, were made of stage in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Some water temperature, conductivity, and dissolved oxygen numbers during the summer. Discharge is determined from stage using discharge vs stage regressions.
Year 2007, 10 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2007, continuous measurements, every 10 minutes, were made of depth and stream temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Discharge is determined from stage using discharge vs stage regressions.
Year 2008, 15 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2008, continuous measurements, every 15 minutes, were made of depth and stream temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Discharge is determined from stage using discharge vs stage regressions.
Year 2009, 15 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2009, continuous measurements, every 15 minutes, were made of depth and stream temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Discharge is determined from stage using discharge vs stage regressions.
Year 2012, 15 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2012, continuous measurements, every 15 minutes, were made of depth and stream temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Discharge is determined from stage using discharge vs stage regressions.
Year 2013, 15 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2013, continuous measurements, every 15 minutes, were made of depth and stream temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Discharge is determined from stage using discharge vs stage regressions.
Year 2014, 15 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2014, continuous measurements, every 15 minutes, were made of depth and stream temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Discharge is determined from stage using discharge vs stage regressions.
Year 2015, 15 minute measurements of stage in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2015, continuous measurements, every 15 minutes, were made of depth and stream temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). Discharge is determined from stage using discharge vs stage regressions.
PIE LTER year 2012, 5 minute and 15 minute measurements of specific conductance, water temperature in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2012, continuous measurements, every 5 minutes for the first deployment and 15 minutes until the end of the year, were made of conductivity, water temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential). in the Ipswich River watershed.
PIE LTER year 2013, 15 minute measurements of specific conductance, water temperature in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2013, continuous measurements, every 15 minutes were made of conductivity, water temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential) in the Ipswich River watershed.
PIE LTER year 2014, 15 minute measurements of specific conductance, water temperature in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2014, continuous measurements, every 15 minutes were made of conductivity, water temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential) in the Ipswich River watershed.
PIE LTER year 2015, 15 minute measurements of specific conductance, water temperature in a small headwater stream draining a highly suburban catchment (72% residential), Saw Mill Brook, Burlington, MA.
Year 2015, continuous measurements, every 15 minutes were made of conductivity, water temperature in a small headwater stream, Saw Mill Brook, Burlington, MA, draining a highly suburban catchment (72% residential) in the Ipswich River watershed.
Stream Discharge for Cobb Mill Creek at the Virginia Coast Reserve 2002-2003 and 2010-2011
This dataset contains stream discharge data for Cobb Mill Creek for two 12-14 month-long time periods:Â from 02-28-2002 through 04-20-2003, and from 10-01-2010 through 9-30-2011.
Ficus nymphaeifolia Mill. from Colombia collected by F. Toro, E. Álvarez, A. Camargo #255
<p><strong>File Name</strong>: <span>TOLI-22383-ZAR-05-299.jpg</span></p> <p><strong>CÓDIGO FOTO</strong>: <span>TOLI-22383-ZAR-05-299-</span></p> <p><strong>Fotografía</strong>: <span>SI</span></p> <p><strong>Nº TOLI</strong>: <span>TOLI-22383</span></p> <p><strong>PARCELA</strong>: <span>ZAR-05</span></p> <p><strong>CÓDIGO</strong>: <span>299</span></p> <p><strong>Nº COLECTA</strong>: <span>255</span></p> <p><strong>NUEVOS COLECTORES</strong>: <span>Alejandro Camargo, Felipe Toro & Esteban Alvarez</span></p> <p><strong>COLECTORES</strong>: <span>F. Toro, E. Álvarez, A. Camargo</span></p> <p><strong>Nº MUESTRAS MONTADAS</strong>: <span>2</span></p> <p><strong>Homologación</strong>: <span>No homologado</span></p> <p><strong>Nueva fecha del evento </strong>: <span>30/11/2018.</span></p> <p><strong>Fecha del evento</strong>: <span>15/10/2006.</span></p> <p><strong>Proyecto </strong>: <span>Recursos Botánicos Disponibles en Línea (BRAVO) para la flora Colombiana</span></p> <p><strong>Hábitat</strong>: <span>Bosque húmedo tropical (bh-T)</span></p> <p><strong>Comentario del evento</strong>: <span>Bosque de tierra firme</span></p> <p><strong>Continente</strong>: <span>SA</span></p> <p><strong>Pais</strong>: <span>Colombia</span></p> <p><strong>Estado/Provincia</strong>: <span>Amazonas</span></p> <p><strong>Municipio</strong>: <span>Leticia</span></p> <p><strong>Localidad</strong>: <span>Resguardo Indígena Ticuna-Huitoto Km 6-11.</span></p> <p><strong>Elevación minima en metros</strong>: <span>200</span></p> <p><strong>Elevación maxima en metros</strong>: <span>300</span></p> <p><strong>Latitud</strong>: <span>-4.004</span></p> <p><strong>Longitud original</strong>: <span>-69.896</span></p> <p><strong>datum geodésico</strong>: <span>WGS 84</span></p> <p><strong>Latitud decimal</strong>: <span>-4.004</span></p> <p><strong>Longitud decimal</strong>: <span>-69.896</span></p> <p><strong>Identificado por</strong>: <span>Diego Suescún</span></p> <p><strong>Fecha de identificación</strong>: <span>15/02/2019.</span></p> <p><strong>Nombre cientifico</strong>: <span>Ficus nymphaeifolia Mill.</span></p> <p><strong>Reino</strong>: <span>Plantae</span></p> <p><strong>Filo</strong>: <span>Magnoliophyta</span></p> <p><strong>Clase</strong>: <span>Equisetopsida</span></p> <p><strong>Orden</strong>: <span>Rosales</span></p> <p><strong>Familia nueva</strong>: <span>Moraceae</span></p> <p><strong>Género nuevo</strong>: <span>Ficus </span></p> <p><strong>especie nueva</strong>: <span>nymphaeifolia</span></p> <p><strong>Autoría del nombre científico</strong>: <span>Mill.</span></p> <p><strong></strong>: <span>Moraceae</span></p> <p><strong>genero herbario</strong>: <span>Ficus</span></p> <p><strong>especie herbario</strong>: <span>nymphaeifolia</span></p> <p><strong>Especie de herbario para TNRS</strong>: <span>Ficus nymphaeifolia</span></p> <p><strong>Especie corregida herbario y desde TNRS</strong>: <span>Ficus nymphaeifolia</span></p> <p><strong>Familia corregida desde TNRS</strong>: <span>Moraceae</span></p> <p><strong></strong>: <span>1518</span></p>
Ficus citrifolia Mill. from Colombia collected by W. López, J. Rodriguez, M. Salas #1234
<p><strong>File Name</strong>: <span>TOLI-21446-AMA-02-D22-12.jpg</span></p> <p><strong>CÓDIGO FOTO</strong>: <span>TOLI-21446-AMA-02-D22-12-</span></p> <p><strong>Fotografía</strong>: <span>SI</span></p> <p><strong>Nº TOLI</strong>: <span>TOLI-21446</span></p> <p><strong>PARCELA</strong>: <span>AMA-02</span></p> <p><strong>CÓDIGO</strong>: <span>D22-12</span></p> <p><strong>Nº COLECTA</strong>: <span>1234</span></p> <p><strong>NUEVOS COLECTORES</strong>: <span>Wilmar López Oviedo</span></p> <p><strong>COLECTORES</strong>: <span>W. López, J. Rodriguez, M. Salas</span></p> <p><strong>Nº MUESTRAS MONTADAS</strong>: <span>1</span></p> <p><strong>Homologación</strong>: <span>Homologado</span></p> <p><strong>Nueva fecha del evento </strong>: <span>27/11/2018.</span></p> <p><strong>Fecha del evento</strong>: <span>01/05/2012.</span></p> <p><strong>Proyecto </strong>: <span>Recursos Botánicos Disponibles en Línea (BRAVO) para la flora Colombiana</span></p> <p><strong>Hábitat</strong>: <span>Bosque muy húmedo tropical (bmh-T)</span></p> <p><strong>Comentario del evento</strong>: <span>Bosque de tierra firme</span></p> <p><strong>Continente</strong>: <span>SA</span></p> <p><strong>Pais</strong>: <span>Colombia</span></p> <p><strong>Estado/Provincia</strong>: <span>Chocó</span></p> <p><strong>Municipio</strong>: <span>Nuquí</span></p> <p><strong>Centro poblado / Cabecera municipal</strong>: <span>Arusí</span></p> <p><strong>Localidad</strong>: <span>Reserva Natural El Amargal</span></p> <p><strong>Elevación minima en metros</strong>: <span>50</span></p> <p><strong>Elevación maxima en metros</strong>: <span>300</span></p> <p><strong>Latitud</strong>: <span>5.578</span></p> <p><strong>Longitud original</strong>: <span>-77.500</span></p> <p><strong>datum geodésico</strong>: <span>WGS 84</span></p> <p><strong>Latitud decimal</strong>: <span>5.578</span></p> <p><strong>Longitud decimal</strong>: <span>-77.500</span></p> <p><strong>Identificado por</strong>: <span>Jaime Cabezas</span></p> <p><strong>Fecha de identificación</strong>: <span>24/09/2019.</span></p> <p><strong>Familia antigua</strong>: <span>Moraceae</span></p> <p><strong>Especie antigua</strong>: <span>Ficus citrifolia Mill.</span></p> <p><strong>Nombre cientifico</strong>: <span>Ficus citrifolia Mill.</span></p> <p><strong>Reino</strong>: <span>Plantae</span></p> <p><strong>Filo</strong>: <span>Magnoliophyta</span></p> <p><strong>Clase</strong>: <span>Equisetopsida</span></p> <p><strong>Familia nueva</strong>: <span>Moraceae</span></p> <p><strong>genero herbario</strong>: <span>NN</span></p> <p><strong>Especie de herbario para TNRS</strong>: <span>NN </span></p> <p><strong>Especie corregida herbario y desde TNRS</strong>: <span>Indet indet</span></p> <p><strong>Familia corregida desde TNRS</strong>: <span>Moraceae</span></p> <p><strong></strong>: <span>914</span></p> <p><strong>Sin nombre cientif</strong>: <span>1</span></p>
FIG. 4 in Annotated checklist of Afrotropical Trogolaphysa Mills, 1938 (Hexapoda: Collembola: Paronellidae) and description of a new species from Madagascar
FIG. 4. — Distribution of collections of Trogolaphysa judithnajtae n. sp. in Madagascar.
FIG. 1. — Trogolaphysa judithnajtae n in Annotated checklist of Afrotropical Trogolaphysa Mills, 1938 (Hexapoda: Collembola: Paronellidae) and description of a new species from Madagascar
FIG. 1. — Trogolaphysa judithnajtae n. sp., habitus holotype. Scale bar: 0.5 mm.
Does recent fire activity impact fire-related traits of Pinus halepensis Mill. and Pinus sylvestris L. in the French Mediterranean area?
<p>Data used for analyses in the paper by Romero B. and Ganteaume A., published in Annals of Forest Science in 2020.</p> <p>PS : <em>Pinus sylvestris</em></p> <p>PH : <em>Pinus halepensis</em></p>
Signatures of local adaptation to climate in natural populations of sweet chestnut (Castanea sativa Mill.) from southern Europe
Context: Temperate forest species, such as chestnut (Castanea sativa Mill.), are currently threatened by increasing temperature together with disruption and reduction of precipitation due to climate change. In this context, understanding the adaptation processes of species will help to manage and ensure the conservation of forests. Aims: We studied the relationship between genetic variability and climate variables in natural populations of C. sativa using a landscape genomics approach aimed to identify local adaption processes. Methods: Using five genomic SSRs and eight functional EST-SSRs markers, 268 individuals belonging to ten different natural European chestnut populations distributed in contrasting climatic sites were genotyped. In addition, associations between allelic variation and climatic variables (environmental association analyses approach) were performed using Samada and LFMM. Results: Results highlighted a strong inter-relationship between climate variables and evolutionary processes resulting in adaptive variation. STRUCTURE analysis based on functional markers split the populations in three separate gene pools (K=3), mostly in agreement with the different climatic conditions existing in the studied areas. Divergent spatial patterns of genetic variation between rainy and arid areas were found. We detected a total of 202 associations with climate among 22 different alleles, 9% of which related with the outlier locus FIR059, known to be implicated in regulatory mechanisms during water stress adaptation processes. Conclusions: Landscape genomics analyses revealed a pattern of adaptive variation, where specific climatic variables influenced the frequencies distribution and fixation of several alleles, resulting in local adaptation processes of the populations in the investigated areas. Our findings underline the close inter-relationship existing between climate and genetic variability, and indicate how this approach could provide valuable information for the management of forest species in a rapidly changing environment.
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Allen Brain Atlas
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