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Whatman glass fiber filter

Manufactured by Cytiva

Whatman glass fiber filters are a type of laboratory filtration media used to separate solid particles from liquids or gases. They are made from borosilicate glass fibers and are available in a range of sizes and thicknesses to suit various applications. Whatman glass fiber filters are designed to provide efficient and reliable filtration performance.

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5 protocols using whatman glass fiber filter

1

Spatial Variation of Water Quality in the Taiwan Strait

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In May 2019, surface (0.5 m) water samples from 16 stations along five north to south transects were collected on board the R/V China Marine Surveillance 203 (Fig. 1). The main physical–chemical parameters, i.e., temperature, conductivity, salinity, pH, and turbidity, as well as the concentration of total dissolved solids (TDS), chlorophyll-a, and blue-green algae-phycoerythrin (BGA-PE) were measured using a CTD probe and after filtration of water volumes through Whatman glass fiber filters, respectively, according to the standard analytical procedures used for the determination of these parameters. The carbon substrate utilization patterns and the total prokaryotic abundance were estimated.

Location of the sampling sites in Taiwan Straits

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2

Water Sampling and Analysis Protocols

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Water samples were collected from ~ 0.25 m depth using acid-washed, triple-rinsed polycarbonate or high-density polyethylene bottles and stored on ice until processed, usually the same evening. Secchi depth (SD) was measured by standard limnological procedures. Samples were collected at various depths on a few NLF lakes in 2018 to determine effects of stratification on CDOM and Fediss. Raw water was filtered through 0.45 μm Geotech trace-metal-certified capsule filters or pre-combusted (4 h at 450 oC) 0.7 μm Whatman glass fiber filters. Filtered water for DOC and Fediss analyses was acidified using 0.1 mL of 2 M HCl per 50 mL of sample and refrigerated (DOC) or frozen (Fediss) in pre-cleaned glass or plastic bottles, respectively. Unfiltered water for FeT analyses was acidified with 1 mL of concentrated HNO3 per 50 mL sample and stored in the same manner as the Fediss samples. Un-acidified filtered water for CDOM analysis was refrigerated in 40 mL glass vials with no headspace. Filter blanks (DI water) showed no measurable DOC or CDOM. Chlorophyll-a (chl-a) was collected by vacuum filtration of water samples onto 0.22 μm cellulose nitrate filters that were then stored frozen until analysis.
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3

Hydrochemical and Biological Assessments

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Concentrations in water of phosphate (PO4-P, ascorbic acid method), nitrite (NO2-N, using sulfanilamide and naftil colorimetric reagents) and nitrate (NO 3 -N, using Cadmium to reduce it to nitrite) were determined according to Golterman et al. (1978) . Ammonia levels were determined spectrophotometrically with the phenolic acid method (Koroleff, 1976) and total alkalinity (CaCO 3 ) with the phenolphthalein method (Mackereth et al., 1978) . For chlorophyll-a, the water was filtered through Whatman glass fiber filters (0.45 µm pore), extracted during 24 hours with wormed ethanol 90%, and read in a colorimeter following Nusch (1980) .
Concentrations in sediment of total nitrogen (Nsed, digestion with sulphuric acid), total phosphorus (Psed, calcination with sodium carbonate) and organic matter (OMsed, calcination method) were determined following Andersen (1976) .
Cladocera and Copepoda were identified in a reticulated acrylic chamber under stereomicroscope (40x augmentation). Rotifera and phytoplanktonic algal units (isolated cells, colonies, filaments) were identified and counted in Sedgewick-Rafter chamber under a Leitz microscope (100x augmentation) after 30 min sedimentation. Plankton concentrations were expressed as number of organisms per water volume following APHA (1992).
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4

Soil PAH Characterization Protocol

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The extraction and analysis of soil samples from the MVs for PAH characterization followed the method in Nor et al. [42 ]. In this method, about 500 mg of the soil samples were dissolved using a mixture of 25 mL n-hexane and acetone (7:3, v/v). A microwave extraction arrangement was used with its pressure carefully controlled for 45 minutes. After cooling, the extract was filtered with a Whatman glass fiber filter in a glass bottle, followed by a concentration of the extract to 1.5 mL using a rotatory evaporator. PAH was determined by the GC quadrupole Mass Spectrometer (GC-MSD) (Agilent 5975 MSD). The sample was separated into its components by chromatographic separation using a capillary column of an internal diameter of 30 m×0.25 mm and film thickness of 0.25 μm, HP-5MS and a helium carrier gas of high purity (99.5%), having a flow rate of 1 mL/min from a steel cylindrical pipe. The chromatographic separation conditions include an injector temperature of 250°C and an initial 70°C temperature of the chromatographic column which was held for 1 minute. The temperature increase by 30°C/min to 200°C, by 35°C/min to 250°C, and by 10°C/min to 300°C and this was maintained for 25 minutes. The PAH content of the soil samples was quantified from the resulting chromatogram as earlier reported [43 ,44 ].
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5

Soil TPH Extraction and Analysis

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The TPH content of the soil samples was extracted according to the methods earlier described by some authors [36 –38 ]. 10 g of the soil sample was carefully mixed with 150 mL dichloromethane which was used as the extraction solvent and extracted for 4 hours 30 minutes. This was done in the presence of 2.5 g of dried sodium sulfate and 300 μg/mL of 1-chloro-octadecane as a surrogate standard. 0.3 g of silica was introduced into the extraction mixture after the extraction to facilitate the adsorption of polar materials like animal fats and oil from vegetable materials. The extracts were later passed through a Whatman glass fiber filter for filtration. The materials not removed by silica gel such as oil and grease were considered PHs [39 ]. The separation and determination of TPH contained in the soil samples were carried out with Gas Chromatography equipped with Flame Ionization Detector (GC-FID) (Agilent 6890N). A concentrated 3 μL of the sample was introduced into the GC column with a micro-syringe previously rinsed with dichloromethane (blank) and the sample. The TPH was determined at a specific chromatogram in mg/kg [40 ,41 ].
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