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Aa 6800 spectrometer

Manufactured by Shimadzu
Sourced in Japan

The AA-6800 spectrometer is a high-performance atomic absorption spectrometer designed for elemental analysis. It uses a flame or graphite furnace atomization technique to detect and quantify trace elements in a variety of sample types. The AA-6800 features advanced optics, a high-sensitivity detector, and automated operation for efficient and reliable analytical performance.

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4 protocols using aa 6800 spectrometer

1

Trace Element Analysis in Blood Samples

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Blood samples were collected in the Venesection Unit of Gaziantep University
Medical Faculty Hospital. With the subject seated, the antecubital area of the
forearm was sterilized by being wiped with cotton soaked in an alcoholic
solution. Five millilitres of venous blood was drawn using a BD Vacutainer
needle, then transferred to and gathered in tubes (VACUETTE® Tube,
8 ml, US, Z Serum Separator Clot Activator containing microscopic silica
particles to stimulate coagulation). The blood samples were then allowed to
coagulate for 10–15 min at room temperature. The specimens were centrifuged for
10 min at 4000 rev/min in a centrifuge. The serum was then separated and
preserved in a micro Eppendorf tube and stored at –80°C. Zn and Cu levels were
measured using atomic absorption spectroscopy (Shimadzu AA-6800 spectrometer),
Se levels were measured using inductively coupled plasma mass spectrometry
(NexION® 350 ICP-MS spectrometer), and Fe levels were measured
using a Beckman Coulter® device (Au5800, Japan, 2007). These analyses
were carried out at the Central Laboratory of Gaziantep University’s Medical
Faculty Hospital.
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2

Soil Heavy Metal Analysis by AAS

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Soil metal contents were determined by atomic absorption spectrometry (AAS) with a SHIMADZU AA-6800 spectrometer (Shimadzu, Tokyo, Japan) using the aqua regia di-gestion. The entire soil sample was dried, ground to a fine powder, and sieved through a 100 μm sieve [102 (link)]. This was undertaken in order to have a homogeneous soil sample so that the entire soil sample is subjected to the mineralization process and because it is known that grinding increases the specific surface area, i.e., an improvement of the soil/extraction solution contact surface occurs. Three grammes of soil were weighed into a beaker, to which 7 mL of HCl and 21 mL of HNO3 were added. After 3 h of mineralization, the supernatant was filtered through a 0.45 μm pore size filter into a 100 mL volumetric flask, filled to the mark with distilled water, and then subjected to heavy metal analysis by AAS. Investigations were carried out under constant conditions of temperature, actual air humidity, and ventilation: T = (27 ± 1) °C and RH = (65 ± 2)%, without forced ventilation of ambient air.
In order to determine the degree of soil pollution, the results obtained were compared with the values established in Order 756/1997 [13 ] concerning normal values, alert threshold values, and intervention threshold values (Table 1).
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3

Comprehensive Soil Characterization

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Characterization of the soil samples was carried out in terms of pH, texture, structure and content of metals (Cu, Pb, Cr and Ni). Soil pH was determined in soil/water extract 1/5 (w/v) using a HANNA pH meter. Soil texture was determined by gravimetric method with RETSCH AS 200 sieve and soil structure was determined by Sekera method. Soil metal content was determined by atomic absorption spectrometry (AAS) with a SHIMADZU AA-6800 spectrometer (Shimadzu, Tokyo, Japan) using the aqua regia digestion. The soil samples were dried, grounded to a fine powder and sieved through a 100 μm sieve. Three grams of each sample of soil were weighed into a beaker and 7 mL of HCl and 21 mL of HNO3 were added. The mixture was then refluxed for 2 h. After cooling to room temperature, the supernatant was filtered and diluted to 100 mL.
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4

Comprehensive Physicochemical Characterization of Materials

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The metal content in the samples was determined through FAAS, using a Shimadzu AA6800 spectrometer equipped with a flame and graphite furnace modules. The spectrometer was adjusted to the most intense spectral peak of each metal. The infrared spectra were collected via transmittance mode in a Nicolet Nexus 670 spectrometer, and the samples were subjected to 32 scans in a resolution of 4 cm -1 . The pellets of the samples were manufactured by compressing 400 g of a KBr sample mix-ture (1% in sample). Elemental analysis was carried out in an EA 1110 CHNS-O analyzer from CE Instruments using 2.2 mg of material. The specific surface area of the material was measured using a Micromeritics AS-AP2010 apparatus (Micromeritics Instrument Corporation) with 1.0 g of the materials. The measurements were accomplished with 0.5000 g of the material, which was previously treated at 100 °C under vacuum. The analyses were carried out using nitrogen at 77 K, and the BET model was applied. The morphological structure of the material's particle was obtained in a Zeiss DSM 960 scanning electron microscope by applying a voltage of 20 kV.
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