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Turner td 700 fluorometer

Manufactured by Turner Designs
Sourced in United States

The Turner TD-700 fluorometer is a compact and versatile instrument designed for fluorescence measurement. It features a high-intensity LED light source and a sensitive photodetector to accurately measure fluorescence intensity. The TD-700 is capable of detecting a wide range of fluorescent compounds and can be used in various applications.

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4 protocols using turner td 700 fluorometer

1

Melt Pond Water Analysis Protocol

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To extract Chl a, 500 mL of melt pond water was filtered onto GF/F filters (Whatman) and the filters were placed in test tubes containing 10 mL ethanol (96%). The samples were stored in darkness at −18 °C until analysis using a fluorometer (Turner TD-700 fluorometer, Turner Designs, California, USA). For POC determination, an additional 500 ml was filtered through separate pre-combusted GF/F filters (Whatman). These filters were stored frozen (−18 °C) in pre-combusted aluminum foil packages. For analysis, the filters were acidified to remove inorganic carbon and thereafter packed into tin capsules for determination of the organic carbon content using a solid phase elemental analyzer (CHN EA1108-Elemental analyzer, CARLO ERBA). For determination of PO43−, NO3 and Br concentrations, 50 mL of the filtrate was stored frozen (−18 °C). PO43− and NO3 concentrations were measured by standard procedures as described in Grasshoff et al. (1983 ) and García-Robledo et al. (2014 (link)), respectively, while Br concentrations were measured using ion chromatography (IC, Dionex IC S-1500; Forster et al. 1999 (link)).
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2

Chlorophyll-a Extraction and Quantification

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Chlorophyll-a was measured following filtration onto 0.2 μm polycarbonate membranes (Millipore) and extraction with Dimethyl sulfoxide (DMSO) at room temperature. After a 30 s sonification, each sample was left to extract overnight, followed by a centrifugation and measurement by fluorometry on a Turner TD-700 fluorometer (Turner Designs, Sunnyvale, CA) calibrated with a solid standard.
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3

Measurement of Nutrient and Chlorophyll Concentrations

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Samples for the measurement of NO3 + NO2, PO43-, and Si(OH)4 concentrations were filtered through precombusted (450 °C for 4.5 h) 25 mm GF/F filters and stored in acid-cleaned FalconTM tubes (Thermo Fisher Scientific) at −20 °C until analysis using standard techniques [30 ] on a Lachat QuikChem 8000 Flow Injection Analyzer. Samples for the analysis of POC and PON were filtered onto precombusted (4 h @ 450 °C) 25 mm Whatman GF/F filters. Blank filters were made by filtering ca. 25 ml filtered (0.2 µm) seawater and were processed the same as the particulate samples. The filters were dried (60 °C) and stored at room temperature until analysis. Prior to analysis the samples were fumed with concentrated HCl, dried at 60 °C for 24 h, packed into tin capsules (Costech Analytical Technologies Inc. Valencia, CA) and analyzed on an Elemental Combustion System (Costech Analytical Technologies) interfaced to a Thermo Finnigan Delta V Advantage isotope ratio mass spectrometer (Thermo Fisher Scientific) at the SOEST Biogeochemical Stable Isotope Facility at the University of Hawai’i, Manoa. Fluorometric analysis of Chl a was measured [31 ] using a Turner Fluorometer TD-700 (Turner Designs, Inc., San Jose, CA).
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4

Nutrient and Chlorophyll Analysis Procedure

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Samples for the measurement of nitrate plus nitrite (NO3+NO2) and phosphate (PO43−) concentrations were filtered through precombusted (450 °C for 4 h) 25 mm WhatmanTM GF/F filters (MilliporeSigma, Burlington, MA) and stored in acid-cleaned FalconTM tubes (Thermo Fisher Scientific, Waltham, MA) at −20 °C until analysis using standard techniques [39 ] on a Lachat QuikChem 8000 Flow Injection Analyzer. The limit of detection (LOD) and limit of quantitation (LOQ), respectively, were 0.01 and 0.04 µmol l−1 for NO3+NO2, 0.01 and 0.02 µmol l−1 for PO43−. Three separate Chl a samples (ca. 150 ml) from each depth were filtered onto GF/F filters, extracted in the dark at 3 °C in 90% acetone for 24 h and measured fluorometrically using a Turner Fluorometer TD-700 (Turner Designs, Inc., San Jose, CA) as described in Welschmeyer et al. [40 (link)]. The LOD, calculated as 3× the standard deviation of the blank (90% acetone), was 0.002 µg Chl a l−1. With the exception of 200 m samples at five stations, the coefficient of variation for the averaged values was <10%.
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