Damos las gracias al USGS y de los Recursos de Agua y Vermont Lake Centro de Estudios para proporcionar financiación.

1. Extracción de fósforo <ol><li> Prepare una solución de 1 litro de 0,25 M de hidróxido sódico (NaOH, 40,00 g / mol) + 0,05 M de ácido etilendiaminotetraacético (EDTA, 292,24 g / mol). </li><li> Añadir 30 ml de la solución de NaOH + EDTA a 2 g de suelo húmedo o seco / muestra en un tubo cónico de 50 ml. </li><li> Incubar con agitación durante 16 horas a temperatura ambiente. </li><li> Centrífuga 3000 xg durante 3 minutos. </li></ol> 2. Extracto de la muestra de ajuste de pH <ol><li> Transferir una alícuota de 0,1 ml a 1,5 ml un micro-tubo de centrífuga. </li><li> Añadir 0,017 ml de 2,5 M de ácido acético, 0,144 ml de solución tampón de acetato 0,4 M (70,5% de acetato de sodio [CH3COONa, 82,03 g / mol] y el 29,5% de ácido acético, pH 5,0), y 0.739 ml de agua destilada. </li><li> El volumen final del extracto de ajuste será de 1 mL y el pH final será 5,0. </li></ol> 3. Foto enzima preparación de la solución <ol><li> Prepare 1 litro de acetato de sodio 0,1 M (CH3COONa, 82,03 g / mol) solución, pH 5,0. </li><li> Prepare 2 x 10 ml de ácido soluciones madre fosfatasa en el buffer de acetato de sodio preparado en el paso 3.1 de tal manera que las concentraciones finales son cada 0,5 unidades / ml. Fosfatasa ácida de tipo I de Triticum aestivum (germen de trigo, GP, por lo general 0,5 U mg-1 sólido, EC 3.1.3.2) La fosfatasa ácida Tipo IV-S de Solanum tuberosum (papa, PP, en general, 4,6 U mg-1 sólido, EC 3.1.3.2) * Las unidades de actividad son especificados por el proveedor, donde se define una unidad como la liberación de un micromol de ortofosfato para la solución por hora a 37 ° C. </li><li> Reconstituir liofilizado nucleasa P1 (CE 3.1.30.1) de Penicillium citrinum (hongos, NP1, generalmente de 500 U mg -1 sólido) en un ml de agua desionizada, esto ahora se puede almacenar a 4 ° C para su uso futuro. </li><li> Pipeta NP1 en uno de los tubos de 10 ml preparada en la etapa 3.2 de tal manera que la concentración final es de 2,5 unidades / mL NP1, mezclar suavemente invirtiendo varias veces. </li><li> Centrifugar las dos soluciones de la enzima 10 ml 3000 xg durante 30 minutos. </li></ol> 4. P curva de calibración y controles <ol><li> Prepare 1 L de 1 mM fosfato de potasio (K2HPO4, 174,18 g / mol) solución de reserva. </li><li> Añadir 1 ml de la 1 mM de potasio solución de reserva de fosfato a un tubo centrífugo de 1,5 ml y llevar a cabo siete diluciones seriadas 0,5 ml. </li><li> Desechar el tubo primero por lo que tiene 7 diluciones que van de 20 nmol, 0,625 nmol P. </li><li> Transferencia de 80 l de cada tubo por duplicado a las filas de B - H de una placa estándar de 96 pocillos. </li><li> Añadir 80 l de tampón de acetato de sodio (punto 3.1) de la fila A de las columnas 11 y 12, este es el punto de calibración 0 nmol P. </li><li> Cada columna 11 y 12 ahora contiene 8 muestras de referencia de 0 a 20 nmol nmol de fosfato inorgánico. </li><li> En la columna 10 contendrá los siguientes controles: <ol><li> Añadir 40μL PP + solución de la enzima GP + 40 l tampón acetato de sodio (punto 3.1) a los tres primeros pozos en la columna 10. </li><li> Añadir 40 l PP + GP + NP1 solución de la enzima de búfer + 40 l de acetato de sodio para los próximos tres pozos. </li><li> Añadir 40 l solución de acetato de sodio con 10 nmol de glucosa-6 fosfato (C 6 H 11 Na 2 O 9 P &amp;bullet; xH 2 O, 304,1 g / mol) + 40 l PP + solución de la enzima GP a un pozo y al final, así en la columna 10, añadir la solución de acetato de sodio en lugar de solución de enzima. </li></ol></li></ol> 5. + Muestra la enzima de incubación <ol><li> Cada muestra se está probando que ocupan los primeros nueve pozos en una fila de una placa estándar de 96 pocillos. </li><li> Distribución de 40 L de extractos de la muestra de pH ajustado de la Sección 2 de los pozos de 1-9 en un máximo de 8 líneas. </li><li> Después de todas las muestras han sido distribuidos * utilizar una pipeta multicanal para distribuir PP + solución de la enzima GP de columnas 1-3, PP + GP + NP1 a las columnas 4-6 y tampón de acetato sódico (preparado en la sección 3.1) a las columnas 7-9. * Este paso debe realizarse con rapidez para asegurar todas las muestras de obtener el tiempo de incubación equivalente. </li><li> Cubrir la placa de 96 pozos con una tapa y las muestras se incuban + soluciones enzimáticas, los controles y la curva de calibración exactamente 1 hora a 37 ° C. </li></ol> 6. Medición colorimétrica de Lanzamiento y P de fondo inorgánicos <ol><li> Prepare 50 ml de cada una de las siguientes soluciones en agua destilada: Solución A *: 0,1 M de ácido ascórbico (C6H8O6, 176,12 g / mol) + ácido tricloroacético 0,5 M (Cl3, CCOOH, 163,39 g / mol) Solución B: 0,01 M molibdato de amonio ((NH4) 2MoO4, 196,01 g / mol) Solución C: 0,1 M de citrato de sodio (HOC (COONa) (CH2COONa) 2 2H2O, 294,10 g / mol) + 0,2 M arseniato de sodio (NaAsO2, 129,91 g / mol) + 5% de ácido acético glacial (CH3CO2H, 60,05 g / mol) * Solución A debe prepararse diariamente. </li><li> Añadir 25 l de solución de SDS, 100 l de solución A, 20 L de la solución B y 50 l de C y la solución a todos los pozos de la pl de 96 pozoscomió. Hacer esto rápidamente con una pipeta multicanal. </li><li> Cubrir la placa e incubar 30 minutos a temperatura ambiente. </li><li> Medir la absorbancia a 850 nm en un micro-ajustable lector de placas. </li></ol> 7. Clasificación de los compuestos de P <ol><li> Importar datos en bruto en una hoja de cálculo (por ejemplo Microsoft Excel). </li><li> Trazar la curva de calibración de fósforo inorgánico: 0 a 40 nmol P sobre el eje X y la media de las mediciones de absorbancia por duplicado en el eje. </li><li> Realizar una regresión lineal y encontrar la ecuación de la recta de mejor ajuste. </li><li> Columnas 1-3: se aplica directamente la curva de calibración de fondo-esto es inorgánico P. </li><li> Columnas 4-6: Los valores medios de la muestra por triplicado y restar a los controles (P + enzima solución de fondo inorgánicos) del ingreso bruto absorción, esto es derivado de P hidrolizables monoésteres P. </li><li> Columnas 7-9: Lo mismo que 7.5, excepto los valores de absorbancia resta de las columnas 4-6 - esto es P desde hidrolizables diésteres P. </li><li> Convertir los datos de absorbancia en nmol P liberado mediante la aplicación de la ecuación de calibración. </li><li> nmol P liberado puede relacionarse a mg P / kg de suelo original. Por otra parte, la evaluación de las proporciones de cada clase de P también puede ser un enfoque útil para el análisis de datos. </li></ol> 8. Los resultados representativos: Una rápida inspección visual de la placa de 96 pozos después de la química colorimétrica ofrecerá pistas sobre si el procedimiento se realizó correctamente. La primera cosa a comprobar es el nivel de líquido en cada pozo de exploración del perfil lateral de la placa. No debe ser exactamente 275 l de reactivos en todos los pozos. A continuación, inspeccione visualmente el color de los pozos de la muestra por triplicado y duplicado los pozos de calibración. Estas técnicas se debe repetir el mismo tono de azul. A continuación, aplicar la curva de calibración de los dos pozos que contienen glucosa-6-fosfato y verificar que todos los liberados nmol 10 de inorgánicos P. Después de P total extraído se ha medido mediante ICP-OES o un método alternativo, asegúrese de que el P total de los valores calculados utilizando este protocolo no superen la cantidad de P que se extrajo. Nota: una cuidadosa gestión de los datos en la hoja de cálculo le ayudará a evitar errores cuantitativos. Usted tendrá que lidiar con un montón de números a la vez, creando así una plantilla será tiempo bien invertido. <img src="/files/ftp_upload/2660/2660fig1.jpg" alt="Figura 1" /> Figura 1. Una placa de 96 pozos que muestra los resultados de 8 muestras (filas AH) y una curva de calibración (columnas 11 y 12). Los controles están en la columna 10. Aumentar la intensidad de color entre las columnas 1-3 y 4-6 se debe a los compuestos hidrolizados monoéster P, entre las columnas 4-6 y 7-9 se debe a los compuestos hidrolizados diéster P. <img src="/files/ftp_upload/2660/2660fig2.jpg" alt="Figura 2" /> Figura 2. Distribución de las clases de P en un 0,25 M de NaOH 0,05 M de EDTA de extraer una muestra de suelo Vermont con alto rendimiento de la hidrólisis enzimática. Las barras de error indican la desviación estándar, n = 3.

<ol>
	<li>Turner, B. L., Frossard, E., Baldwin, D. S. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Organic phosphorus in the environment. , (2005).</li><li>Murphy, J., Riley, J. P. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=A+modified+single+solution+method+for+determination+of+phosphate+in+natural+waters.">A modified single solution method for determination of phosphate in natural waters.</a> Anal. Chim. Acta. 27, 31-36 (1962).</li><li>Dick, W. A., Tabatabai, M. A. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Determination+of+orthophosphate+in+aqueous+solutions+containing+labile+organic+and+inorganic+phosphorus+compounds.">Determination of orthophosphate in aqueous solutions containing labile organic and inorganic phosphorus compounds.</a> J. Environ. Qual. 6, 82-85 (1977).</li><li>He, Z., Toor, G. S., Honeycutt, C. W., Sims, J. T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=An+enzymatic+hydrolysis+approach+for+characterizing+labile+phosphorus+forms+in+dairy+manure+under+mild+assay+conditions.">An enzymatic hydrolysis approach for characterizing labile phosphorus forms in dairy manure under mild assay conditions.</a> Bioresour. Technol. 97, 1660-1668 (2006).</li><li>He, Z., Honeycutt, C. W. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=A+modified+molybdenum+blue+method+for+orthophosphate+determination+suitable+for+investigating+enzymatic+hydrolysis+of+organic+phosphates.">A modified molybdenum blue method for orthophosphate determination suitable for investigating enzymatic hydrolysis of organic phosphates.</a> Commun. Soil Sci. Plant Anal. 36, 1373-1383 (2005).</li><li>Cade-Menun, B. J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Characterizing+phosphorus+in+environmental+and+agricultural+samples+by+31P+nuclear+magnetic+resonance+spectroscopy.">Characterizing phosphorus in environmental and agricultural samples by 31P nuclear magnetic resonance spectroscopy.</a> Talanta. 66, 359-371 (2005).</li><li>Johnson, N. R., Hill, J. E. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Phosphorus+species+composition+of+poultry+manure-amended+soil+using+high-throughput+enzymatic+hydrolysis.">Phosphorus species composition of poultry manure-amended soil using high-throughput enzymatic hydrolysis.</a> Soil Sci. Soc. Am. J. 74, 1786-1791 (2010).</li></ol>

Por su propia naturaleza, un método rápido para el uso de volúmenes pequeños requiere mucho cuidado. Por lo tanto, los pasos más importantes son los relacionados con las soluciones de pipeteo en el plato. Precisa, y lo más importante, la técnica consistente pipeta son esenciales para el éxito de este ensayo. La extracción de NaOH-EDTA permitirá que la mayoría de la P en muchas muestras que se caracteriza en tres clases: ortofosfato, P monoéster y diéster P. Los suelos, los abonos, los sedimentos o cualquier otra muestra del medio ambiente que contiene NaOH-EDTA-P extraíble se puede caracterizar . Formas de P en muestras ambientales no son necesariamente estables y esta técnica se asegurará de muestras se caracterizan antes de las muestras están en peligro sin necesidad de emplear un ejército de investigadores. Este análisis es especialmente útil cuando un gran número de muestras se van a procesar. Las necesidades de reactivos y las necesidades de espacio se han reducido a un nivel manejable (por ejemplo, 1,5 mL tubos de microcentrífuga en lugar de 50 ml frascos de vidrio). Esta adaptación también limita la producción de residuos.

<table border="1"><tbody><tr><th> Nombre del reactivo </th><th> Empresa </th><th> Número de catálogo </th></tr><tr><td> NaOH </td><td> Sigma-Aldrich </td><td> S8045 </td></tr><tr><td> EDTA </td><td> Sigma-Aldrich </td><td> EDS </td></tr><tr><td> Ácido acético glacial </td><td> Sigma-Aldrich </td><td> 242853 </td></tr><tr><td> Acetato de sodio </td><td> Sigma-Aldrich </td><td> S2889 </td></tr><tr><td> Trigo fosfatasa ácida </td><td> Sigma-Aldrich </td><td> P3627 </td></tr><tr><td> Papa fosfatasa ácida </td><td> Sigma-Aldrich </td><td> P1146 </td></tr><tr><td> Nucleasa P1 </td><td> Sigma-Aldrich </td><td> N8630 </td></tr><tr><td> Fosfato de Potasio </td><td> Sigma-Aldrich </td><td> P2222 </td></tr><tr><td></td><td> Sigma-Aldrich </td><td></td></tr><tr><td></td><td> Sigma-Aldrich </td><td></td></tr><tr><td> La glucosa-6-fosfato </td><td> Sigma-Aldrich </td><td> G7250 </td></tr><tr><td> SDS </td><td> Sigma-Aldrich </td><td> L4390 </td></tr><tr><td> Ácido Ascórbico </td><td> Sigma-Aldrich </td><td> A5960 </td></tr><tr><td> TCA </td><td> Sigma-Aldrich </td><td> T9159 </td></tr><tr><td> Molibdato de amonio </td><td> Sigma-Aldrich </td><td> A1343 </td></tr><tr><td> Citrato de sodio </td><td> Sigma-Aldrich </td><td> S1804 </td></tr><tr><td> Arseniato de sodio </td><td> Sigma-Aldrich </td><td> S9663 </td></tr></tbody></table>

high-throughput measurement and classification of organic p in environmental samples

Muchos tipos de orgánicos de fósforo (P) existen moléculas en las muestras ambientales 1. Las mediciones tradicionales de P no detectan estos compuestos orgánicos P, ya que no reaccionan con los reactivos colorimétricos 2,3. Hidrólisis enzimática (EH) es un método emergente para caracterizar con precisión las formas de P orgánico en las muestras de 4,5 ambiental. Este método sólo triunfó en la precisión de Fósforo-31 Espectroscopia de Resonancia Magnética Nuclear (RMN-31 P)-un método que es caro y requiere de técnicos especializados training6. Hemos adaptado un método de hidrólisis enzimática capaz de medir tres clases de fósforo (P monoéster, diéster de P y P inorgánico) a un sistema de lector de microplacas 7. Este método ofrece a los investigadores un medio rápido y preciso, asequible y fácil de usar para medir las especies P en suelos, sedimentos, fertilizantes y, si las muestras de concentrado, acuáticos. Este es el único método de alto rendimiento para la medición de las formas y la enzima labilidad de P orgánico que se pueden realizar en un laboratorio estándar. Los datos resultantes proporciona una idea de los científicos que estudian el contenido de nutrientes del sistema y el potencial de eutrofización.

Watch this Scientific Journal Video about High-Throughput Measurement and Classification of Organic P in Environmental Samples at JoVE.com

High-Throughput Measurement and Classification of Organic P in Environmental Samples

Este protocolo describe un método de alto rendimiento de la hidrólisis enzimática que utiliza un lector de microplacas para medir y clasificar el suelo como el fósforo P monoésteres, diésteres P e inorgánicos P. Hasta 96 muestras se puede medir de una sola vez en un laboratorio estándar.

Alto Rendimiento de medición y clasificación de P orgánico en las muestras ambientales

Many types of organic phosphorus (P) molecules exist in environmental samples1.  Traditional P measurements do not detect these organic P compounds since ...

high-throughput-measurement-classification-organic-p-environmental

Research

JoVE Journal

Biology

12.5K vistas.  University of Vermont. Este protocolo describe un método de alto rendimiento de la hidrólisis enzimática que utiliza un lector de microplacas para medir y clasificar el suelo como el fósforo P monoésteres, diésteres P e inorgánicos P. Hasta 96 muestras se puede medir de una sola vez en un laboratorio estándar.

Video: High-Throughput Measurement and Classification of Organic P in Environmental Samples

High-throughput Screening and Biosensing with Fluorescent C. elegans Strains

High-throughput screening (HTS) is a powerful approach for identifying chemical modulators of biological processes. However, many compounds identified in screens using cell culture models are often found to be toxic or pharmacologically inactive in vivo1-2. Screening in whole animal models can help avoid these pitfalls and streamline the path to drug development.
C. elegans is a multicellular model organism well suited for HTS. It is small (&lt;1 mm) and can be economically cultured and dispensed in liquids. C. elegans is also one of the most experimentally tractable animal models permitting rapid and detailed identification of drug mode-of-action3.
We describe a protocol for culturing and dispensing fluorescent strains of C. elegans for high-throughput screening of chemical libraries or detection of environmental contaminants that alter the expression of a specific gene. Large numbers of developmentally synchronized worms are grown in liquid culture, harvested, washed, and suspended at a defined density. Worms are then added to black, flat-bottomed 384-well plates using a peristaltic liquid dispenser. Small molecules from a chemical library or test samples (e.g., water, food, or soil) can be added to wells with worms. In vivo, real-time fluorescence intensity is measured with a fluorescence microplate reader. This method can be adapted to any inducible gene in C. elegans for which a suitable reporter is available. Many inducible stress and developmental transcriptional pathways are well defined in C. elegans and GFP transgenic reporter strains already exist for many of them4. When combined with the appropriate transgenic reporters, our method can be used to screen for pathway modulators or to develop robust biosensor assays for environmental contaminants. 
We demonstrate our C. elegans culture and dispensing protocol with an HTS assay we developed to monitor the C. elegans cap &#x2018;n&#x2019; collar transcription factor SKN-1. SKN-1 and its mammalian homologue Nrf2 activate cytoprotective genes during oxidative and xenobiotic stress5-10. Nrf2 protects mammals from numerous age-related disorders such as cancer, neurodegeneration, and chronic inflammation and has become a major chemotherapeutic target11-13.Our assay is based on a GFP transgenic reporter for the SKN-1 target gene gst-414, which encodes a glutathione-s transferase6. The gst-4 reporter is also a biosensor for xenobiotic and oxidative chemicals that activate SKN-1 and can be used to detect low levels of contaminants such as acrylamide and methyl-mercury15-16.

High-throughput Screening and Biosensing with Fluorescent C. elegans Strains

A procedure for liquid-based culturing and dispensing of C. elegans strains expressing fluorescent reporter proteins is described that does not require expensive sorting equipment. This approach can be applied to numerous inducible C. elegans genes for drug discovery or biosensing of contaminants.

Selección de alto rendimiento y biosensores fluorescentes con C. elegans Las cepas

High-throughput screening (HTS) is a powerful approach for identifying chemical modulators of biological processes.  However, many compounds identified in ...

Investigación

Biología

High Throughput Screening of Fungal Endoglucanase Activity in Escherichia coli

Cellulase enzymes (endoglucanases, cellobiohydrolases, and &beta;-glucosidases) hydrolyze cellulose into component sugars, which in turn can be converted into fuel alcohols1. The potential for enzymatic hydrolysis of cellulosic biomass to provide renewable energy has intensified efforts to engineer cellulases for economical fuel production2. Of particular interest are fungal cellulases3-8, which are already being used industrially for foods and textiles processing.
Identifying active variants among a library of mutant cellulases is critical to the engineering process; active mutants can be further tested for improved properties and/or subjected to additional mutagenesis. Efficient engineering of fungal cellulases has been hampered by a lack of genetic tools for native organisms and by difficulties in expressing the enzymes in heterologous hosts. Recently, Morikawa and coworkers developed a method for expressing in E. coli the catalytic domains of endoglucanases from H. jecorina3,9, an important industrial fungus with the capacity to secrete cellulases in large quantities. Functional E. coli expression has also been reported for cellulases from other fungi, including Macrophomina phaseolina10 and Phanerochaete chrysosporium11-12. 
We present a method for high throughput screening of fungal endoglucanase activity in E. coli. (Fig 1) This method uses the common microbial dye Congo Red (CR) to visualize enzymatic degradation of carboxymethyl cellulose (CMC) by cells growing on solid medium. The activity assay requires inexpensive reagents, minimal manipulation, and gives unambiguous results as zones of degradation (&#x201C;halos&#x201D;) at the colony site. Although a quantitative measure of enzymatic activity cannot be determined by this method, we have found that halo size correlates with total enzymatic activity in the cell. Further characterization of individual positive clones will determine , relative protein fitness. 
Traditional bacterial whole cell CMC/CR activity assays13 involve pouring agar containing CMC onto colonies, which is subject to cross-contamination, or incubating cultures in CMC agar wells, which is less amenable to large-scale experimentation. Here we report an improved protocol that modifies existing wash methods14 for cellulase activity: cells grown on CMC agar plates are removed prior to CR staining. Our protocol significantly reduces cross-contamination and is highly scalable, allowing the rapid screening of thousands of clones. In addition to H. jecorina enzymes, we have expressed and screened endoglucanase variants from the Thermoascus aurantiacus and Penicillium decumbens (shown in Figure 2), suggesting that this protocol is applicable to enzymes from a range of organisms.

High Throughput Screening of Fungal Endoglucanase Activity in Escherichia coli

We describe a low cost, high throughput method to screen for fungal endoglucanase activity in E. coli. The method relies on a simple visual readout of substrate degradation, does not require enzyme purification, and is highly scalable. This allows for the rapid screening of large libraries of enzyme variants.

Cribado de alto rendimiento de la actividad endoglucanasa por hongos en Escherichia coli</em

Cellulase enzymes (endoglucanases, cellobiohydrolases, and &beta;-glucosidases) hydrolyze cellulose into component sugars, which in turn can be converted ...

Absolute Quantum Yield Measurement of Powder Samples

Measurement of fluorescence quantum yield has become an important tool in the search for new solutions in the development, evaluation, quality control and research of illumination, AV equipment, organic EL material, films, filters and fluorescent probes for bio-industry.
Quantum yield is calculated as the ratio of the number of photons absorbed, to the number of photons emitted by a material. The higher the quantum yield, the better the efficiency of the fluorescent material.
For the measurements featured in this video, we will use the Hitachi F-7000 fluorescence spectrophotometer equipped with the Quantum Yield measuring accessory and Report Generator program. All the information provided applies to this system. 
Measurement of quantum yield in powder samples is performed following these steps:
<ol>
 <li>Generation of instrument correction factors for the excitation and emission monochromators. This is an important requirement for the correct measurement of quantum yield. It has been performed in advance for the full measurement range of the instrument and will not be shown in this video due to time limitations.</li>
 <li>Measurement of integrating sphere correction factors. The purpose of this step is to take into consideration reflectivity characteristics of the integrating sphere used for the measurements.</li>
 <li>Reference and Sample measurement using direct excitation and indirect excitation.</li>
 <li>Quantum Yield calculation using Direct and Indirect excitation. Direct excitation is when the sample is facing directly the excitation beam, which would be the normal measurement setup. However, because we use an integrating sphere, a portion of the emitted photons resulting from the sample fluorescence are reflected by the integrating sphere and will re-excite the sample, so we need to take into consideration indirect excitation. This is accomplished by measuring the sample placed in the port facing the emission monochromator, calculating indirect quantum yield and correcting the direct quantum yield calculation.</li>
 <li>Corrected quantum yield calculation.</li>
 <li>Chromaticity coordinates calculation using Report Generator program.</li>
</ol>
The Hitachi F-7000 Quantum Yield Measurement System offer advantages for this
application, as follows:
<ul>
 <li>High sensitivity (S/N ratio 800 or better RMS). Signal is the Raman band of water measured under the following conditions: Ex wavelength 350 nm, band pass Ex and Em 5 nm, response 2 sec), noise is measured at the maximum of the Raman peak. High sensitivity allows measurement of samples even with low quantum yield. Using this system we have measured quantum yields as low as 0.1 for a sample of salicylic acid and as high as 0.8 for a sample of magnesium tungstate.</li>
 <li>Highly accurate measurement with a dynamic range of 6 orders of magnitude allows for measurements of both sharp scattering peaks with high intensity, as well as broad fluorescence peaks of low intensity under the same conditions. </li>
 <li>High measuring throughput and reduced light exposure to the sample, due to a high scanning speed of up to 60,000 nm/minute and automatic shutter function. </li>
 <li>Measurement of quantum yield over a wide wavelength range from 240 to 800 nm.</li>
 <li>Accurate quantum yield measurements are the result of collecting instrument spectral response and integrating sphere correction factors before measuring the sample.</li>
 <li>Large selection of calculated parameters provided by dedicated and easy to use software.
</li>
</ul> 
During this video we will measure sodium salicylate in powder form which is known to have a quantum yield value of 0.4 to 0.5.

In this video we will demonstrate measuring and calculating absolute quantum yield and chromaticity coordinates directly in powder samples using the Hitachi F-7000 Quantum Yield Measuring System.

Absoluta Quantum medición del rendimiento de las muestras de polvo

Measurement of fluorescence quantum yield has become an important tool in the search for new solutions in the development, evaluation, quality control and ...

Chemically-blocked Antibody Microarray for Multiplexed High-throughput Profiling of Specific Protein Glycosylation in Complex Samples

In this study, we describe an effective protocol for use in a multiplexed high-throughput antibody microarray with glycan binding protein detection that allows for the glycosylation profiling of specific proteins. Glycosylation of proteins is the most prevalent post-translational modification found on proteins, and leads diversified modifications of the physical, chemical, and biological properties of proteins. Because the glycosylation machinery is particularly susceptible to disease progression and malignant transformation, aberrant glycosylation has been recognized as early detection biomarkers for cancer and other diseases. However, current methods to study protein glycosylation typically are too complicated or expensive for use in most normal laboratory or clinical settings and a more practical method to study protein glycosylation is needed. The new protocol described in this study makes use of a chemically blocked antibody microarray with glycan-binding protein (GBP) detection and significantly reduces the time, cost, and lab equipment requirements needed to study protein glycosylation. In this method, multiple immobilized glycoprotein-specific antibodies are printed directly onto the microarray slides and the N-glycans on the antibodies are blocked. The blocked, immobilized glycoprotein-specific antibodies are able to capture and isolate glycoproteins from a complex sample that is applied directly onto the microarray slides. Glycan detection then can be performed by the application of biotinylated lectins and other GBPs to the microarray slide, while binding levels can be determined using Dylight 549-Streptavidin. Through the use of an antibody panel and probing with multiple biotinylated lectins, this method allows for an effective glycosylation profile of the different proteins found in a given human or animal sample to be developed.
Introduction
Glycosylation of protein, which is the most ubiquitous post-translational modification on proteins, modifies the physical, chemical, and biological properties of a protein, and plays a fundamental role in various biological processes1-6. Because the glycosylation machinery is particularly susceptible to disease progression and malignant transformation, aberrant glycosylation has been recognized as early detection biomarkers for cancer and other diseases 7-12. In fact, most current cancer biomarkers, such as the L3 fraction of &alpha;-1 fetoprotein (AFP) for hepatocellular carcinoma 13-15, and CA199 for pancreatic cancer 16, 17 are all aberrant glycan moieties on glycoproteins. However, methods to study protein glycosylation have been complicated, and not suitable for routine laboratory and clinical settings. Chen et al. has recently invented a chemically blocked antibody microarray with a glycan-binding protein (GBP) detection method for high-throughput and multiplexed profile glycosylation of native glycoproteins in a complex sample 18. In this affinity based microarray method, multiple immobilized glycoprotein-specific antibodies capture and isolate glycoproteins from the complex mixture directly on the microarray slide, and the glycans on each individual captured protein are measured by GBPs. Because all normal antibodies contain N-glycans which could be recognized by most GBPs, the critical step of this method is to chemically block the glycans on the antibodies from binding to GBP. In the procedure, the cis-diol groups of the glycans on the antibodies were first oxidized to aldehyde groups by using NaIO4 in sodium acetate buffer avoiding light. The aldehyde groups were then conjugated to the hydrazide group of a cross-linker, 4-(4-N-MaleimidoPhenyl)butyric acid Hydrazide HCl (MPBH), followed by the conjugation of a dipeptide, Cys-Gly, to the maleimide group of the MPBH. Thus, the cis-diol groups on glycans of antibodies were converted into bulky none hydroxyl groups, which hindered the lectins and other GBPs bindings to the capture antibodies. This blocking procedure makes the GBPs and lectins bind only to the glycans of captured proteins. After this chemically blocking, serum samples were incubated with the antibody microarray, followed by the glycans detection by using different biotinylated lectins and GBPs, and visualized with Cy3-streptavidin. The parallel use of an antibody panel and multiple lectin probing provides discrete glycosylation profiles of multiple proteins in a given sample 18-20. This method has been used successfully in multiple different labs 1, 7, 13, 19-31. However, stability of MPBH and Cys-Gly, complicated and extended procedure in this method affect the reproducibility, effectiveness and efficiency of the method. In this new protocol, we replaced both MPBH and Cys-Gly with one much more stable reagent glutamic acid hydrazide (Glu-hydrazide), which significantly improved the reproducibility of the method, simplified and shorten the whole procedure so that the it can be completed within one working day. In this new protocol, we describe the detailed procedure of the protocol which can be readily adopted by normal labs for routine protein glycosylation study and techniques which are necessary to obtain reproducible and repeatable results.

In this study, we describe an improved protocol for a multiplexed high-throughput antibody microarray with lectin detection method that can be used in glycosylation profiling of specific proteins. This protocol features new reliable reagents and significantly reduces the time, cost, and lab equipment requirements as compared to the previous procedure.

Anticuerpos, químicamente bloqueado Microarray de multiplexado de alto rendimiento de perfiles de glicosilación de proteínas específicas en muestras complejas

 In this study, we describe an effective protocol for use in a multiplexed high-throughput antibody microarray with glycan binding protein detection that ...

A High-throughput Method for Measurement of Glomerular Filtration Rate in Conscious Mice

The measurement of glomerular filtration rate (GFR) is the gold standard in kidney function assessment. Currently, investigators determine GFR by measuring the level of the endogenous biomarker creatinine or exogenously applied radioactive labeled inulin (3H or 14C). Creatinine has the substantial drawback that proximal tubular secretion accounts for ~50% of total renal creatinine excretion and therefore creatinine is not a reliable GFR marker. Depending on the experiment performed, inulin clearance can be determined by an intravenous single bolus injection or continuous infusion (intravenous or osmotic minipump). Both approaches require the collection of plasma or plasma and urine, respectively. Other drawbacks of radioactive labeled inulin include usage of isotopes, time consuming surgical preparation of the animals, and the requirement of a terminal experiment. Here we describe a method which uses a single bolus injection of fluorescein isothiocyanate-(FITC) labeled inulin and the measurement of its fluorescence in 1-2 &mu;l of diluted plasma. By applying a two-compartment model, with 8 blood collections per mouse, it is possible to measure GFR in up to 24 mice per day using a special work-flow protocol. This method only requires brief isoflurane anesthesia with all the blood samples being collected in a non-restrained and awake mouse. Another advantage is that it is possible to follow mice over a period of several months and treatments (i.e. doing paired experiments with dietary changes or drug applications). We hope that this technique of measuring GFR is useful to other investigators studying mouse kidney function and will replace less accurate methods of estimating kidney function, such as plasma creatinine and blood urea nitrogen.

Measurement of glomerular filtration rate (GFR) is the gold standard for kidney function assessment. Here we describe a high-throughput method which allows the determination of GFR in conscious mice by using a single bolus injection, determination of fluorescein isothiocyanate (FITC)-inulin in plasma and calculation of GFR by a two-phase exponential decay model.

Un método de alto rendimiento para la medición de la tasa de filtración glomerular en ratones conscientes

The measurement of  glomerular filtration rate (GFR) is the gold standard in kidney function  assessment. Currently, investigators determine GFR by ...

High-throughput Screening for Chemical Modulators of Post-transcriptionally Regulated Genes

Both transcriptional and post-transcriptional regulation have a profound impact on genes expression. However, commonly adopted cell-based screening assays focus on transcriptional regulation, being essentially aimed at the identification of promoter-targeting molecules. As a result, post-transcriptional mechanisms are largely uncovered by gene expression targeted drug development. Here we describe a cell-based assay aimed at investigating the role of the 3&#39; untranslated region (3&#8217; UTR) in the modulation of the fate of its mRNA, and at identifying compounds able to modify it. The assay is based on the use of a luciferase reporter construct containing the 3&#8217; UTR of a gene of interest stably integrated into a disease-relevant cell line. The protocol is divided into two parts, with the initial focus on the primary screening aimed at the identification of molecules affecting luciferase activity after 24 hr of treatment. The second part of the protocol describes the counter-screening necessary to discriminate compounds modulating luciferase activity specifically through the 3&#8217; UTR. In addition to the detailed protocol and representative results, we provide important considerations about the assay development and the validation of the hit(s) on the endogenous target. The described cell-based reporter gene assay will allow scientists to identify molecules modulating protein levels via post-transcriptional mechanisms dependent on a 3&#8217; UTR.

Here we describe a cell-based reporter gene assay as a valuable tool to screen chemical libraries for compounds modulating post-transcriptional control mechanisms exerted through 3&#8217; UTR.

Selección de alto rendimiento para moduladores químicos de genes post-transcripcionalmente regulados

Both transcriptional and post-transcriptional regulation have a profound impact on genes expression. However, commonly adopted cell-based screening assays ...

Precise, High-throughput Analysis of Bacterial Growth

Bacterial growth is a central concept in the development of modern microbial physiology, as well as in the investigation of cellular dynamics at the systems level. Recent studies have reported correlations between bacterial growth and genome-wide events, such as genome reduction and transcriptome reorganization. Correctly analyzing bacterial growth is crucial for understanding the growth-dependent coordination of gene functions and cellular components. Accordingly, the precise quantitative evaluation of bacterial growth in a high-throughput manner is required. Emerging technological developments offer new experimental tools that allow updates of the methods used for studying bacterial growth. The protocol introduced here employs a microplate reader with a highly optimized experimental procedure for the reproducible and precise evaluation of bacterial growth. This protocol was used to evaluate the growth of several previously described Escherichia coli strains. The main steps of the protocol are as follows: the preparation of a large number of cell stocks in small vials for repeated tests with reproducible results, the use of 96-well plates for high-throughput growth evaluation, and the manual calculation of two major parameters (i.e., maximal growth rate and population density) representing the growth dynamics. In comparison to the traditional colony-forming unit (CFU) assay, which counts the cells that are cultured in glass tubes over time on agar plates, the present method is more efficient and provides more detailed temporal records of growth changes, but has a stricter detection limit at low population densities. In summary, the described method is advantageous for the precise and reproducible high-throughput analysis of bacterial growth, which can be used to draw conceptual conclusions or to make theoretical observations.

Quantitative evaluation of bacterial growth is essential to understanding microbial physiology as a systems-level phenomenon. A protocol for experimental manipulation and an analytical approach are introduced, allowing for precise, high-throughput analysis of bacterial growth, which is a key subject of interest in systems biology.

Análisis precisos, alto rendimiento de crecimiento bacteriano

Bacterial growth is a central concept in the development of modern microbial physiology, as well as in the investigation of cellular dynamics at the ...

High-throughput Measurement of Dictyostelium discoideum Macropinocytosis by Flow Cytometry

Large-scale non-specific fluid uptake by macropinocytosis is important for the proliferation of certain cancer cells, antigen sampling, host cell invasion and the spread of neurodegenerative diseases. The commonly used laboratory strains of the amoeba Dictyostelium discoideum have extremely high fluid uptake rates when grown in nutrient medium, over 90% of which is due to macropinocytosis. In addition, many of the known core components of mammalian macropinocytosis are also present, making it an excellent model system for studying macropinocytosis. Here, the standard technique to measure internalized fluid using fluorescent dextran as a label is adapted to a 96-well plate format, with the samples analyzed by flow cytometry using a high-throughput sampling (HTS) attachment.
Cells are fed non-quenchable fluorescent dextran for a pre-determined length of time, washed by immersion in ice-cold buffer and detached using 5 mM sodium azide, which also stops exocytosis. Cells in each well are then analyzed by flow cytometry. The method can also be adapted to measure membrane uptake and phagocytosis of fluorescent beads or bacteria.
This method was designed to allow measurement of fluid uptake by Dictyostelium in a high-throughput, labor and resource efficient manner. It allows simultaneous comparison of multiple strains (e.g. knockout mutants of a gene) and conditions (e.g. cells in different media or treated with different concentrations of inhibitor) in parallel and simplifies time-courses.

High-throughput Measurement of Dictyostelium discoideum Macropinocytosis by Flow Cytometry

Macropinocytosis, large-scale non-specific fluid uptake, is important in many areas of clinical biology including immunology, infection, cancer, and neurodegenerative diseases. Here, existing techniques have been adapted to allow high-throughput, single-cell resolution measurement of macropinocytosis in the macropinocytosis model organism Dictyostelium discoideum using flow cytometry.

Medida de alto rendimiento de macropinocitosis discoideum de Dictyostelium por citometría de flujo

Large-scale non-specific fluid uptake by macropinocytosis is important for the proliferation of certain cancer cells, antigen sampling, host cell invasion ...

High-throughput Measurement of Gut Transit Time Using Larval Zebrafish

Zebrafish are used as alternative model organisms for drug safety testing. The gastrointestinal (GI) tract of zebrafish has genetic, neuronal, and pharmacological similarities to that of the mammals. GI intolerance during clinical testing of drug candidates is common and may pose a serious threat to human health. Testing for GI toxicity in preclinical mammalian models can be expensive in terms of time, test compound, and labor. The high-throughput method presented here may be used to predict GI safety issues. Compared to mammalian models, this method allows for more expedient assessment of test compound effects on GI transit while using low quantities of compound. In this method, larval zebrafish (7 days post fertilization) are fed food containing a fluorescent label. After feeding, each larval fish is placed into a well of a 96-conical-bottom-well plate and dosed with test compound (dissolved in water) or the vehicle. As gut transit occurs, fecal matter accumulates on the bottom of the wells, and the rate at which this happens is monitored by measuring fluorescence from the bottom of the well repeatedly over time using a plate spectrophotometer. The fluorescence from larvae in a given treatment group are averaged and these values are graphed along with standard error, for each measurement time, yielding a curve representing average transit of food over time. Effects on gut transit time are identified by comparing the area under the curve for each treatment group to that of the vehicle-treated group. This method detected changes in zebrafish GI transit time induced by drugs with known clinical GI effects; it can be employed to interrogate dozens of treatments for GI effects per day. As such, safer compounds can be quickly prioritized for mammalian testing, which expedites discovery and proffers 3Rs advancement.

The goal of this protocol is to measure the transit time of fluorescently labeled food through the gut of larval zebrafish in a high throughput fashion.

Medida de alto rendimiento de tiempo de tránsito intestinal utilizando larvas peces cebra

Zebrafish are used as alternative model organisms for drug safety testing. The gastrointestinal (GI) tract of zebrafish has genetic, neuronal, and ...

Quasi-metagenomic Analysis of Salmonella from Food and Environmental Samples

Quasi-metagenomics sequencing refers to the sequencing-based analysis of modified microbiomes of food and environmental samples. In this protocol, microbiome modification is designed to concentrate genomic DNA of a target foodborne pathogen contaminant to facilitate the detection and subtyping of the pathogen in a single workflow. Here, we explain and demonstrate the sample preparation steps for the quasi-metagenomics analysis of Salmonella enterica from representative food and environmental samples including alfalfa sprouts, ground black pepper, ground beef, chicken breast and environmental swabs. Samples are first subjected to the culture enrichment of Salmonella for a shortened and adjustable duration (4&#8211;24 h). Salmonella cells are then selectively captured from the enrichment culture by immunomagnetic separation (IMS). Finally, multiple displacement amplification (MDA) is performed to amplify DNA from IMS-captured cells. The DNA output of this protocol can be sequenced by high throughput sequencing platforms. An optional quantitative PCR analysis can be performed to replace sequencing for Salmonella detection or assess the concentration of Salmonella DNA before sequencing.

Quasi-metagenomic Analysis of Salmonella from Food and Environmental Samples

Here, we present a protocol to prepare DNA samples from food and environmental microbiomes for concerted detection and subtyping of Salmonella through quasimetagenomic sequencing. The combined use of culture enrichment, immunomagnetic separation (IMS), and multiple displacement amplification (MDA) allows effective concentration of Salmonella genomic DNA from food and environmental samples.&#160;