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Ion meter glp 22

Manufactured by Crison
Sourced in Spain

The Ion-Meter GLP 22 is a laboratory instrument designed for measuring the concentration of ions in various solutions. It provides accurate and reliable measurements of pH, conductivity, and other ion-related parameters. The device is suitable for use in a wide range of applications, including water testing, environmental analysis, and industrial process monitoring.

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5 protocols using ion meter glp 22

1

Canine Urine and Serum Biomarkers

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Urine color and turbidity were evaluated as recommended by WSAVA [18 (link)]. Urinalysis was obtained with a dipstick, pH and density were determined with a potentiometer (pH and Ion-Meter GLP 22, Crison, Barcelona, Spain) and a refractometer, respectively. Hemogram was performed using a hematology analyzer (Sysmex XT-2000iV, Norderstedt, Germany). The serum chemistry profile and urinary CT were determined using a chemistry analyzer (Mindray BS-380, Shenzhen, China). Serum CRP was measured by immunoturbidimetry using a Roche Cobas c501 analyzer (Roche Diagnostics, Basel, Switzerland) with the Gentian Canine CRP Kit (Gentian Diagnostics, Stockholm, Sweden). Serum SOD activity was determined using the SOD Assay Kit (Enzo, New York, NY, USA) following the manufacturer’s instructions and a Cytation 3 microplate reader (Bio-Tek Instruments, Winooski, VT, USA) controlled by Gen 5 software (Bio-Tek Instruments, Winooski, VT, USA) for colorimetric detection. The value of Cu/ZnSOD activity was expressed as units per g of serum total protein (TP).
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2

Fecal Ammonia and Volatile Fatty Acids Analysis

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Analysis was run in duplicate. Thawed feces were diluted to 1:10 (w/v) in 20 mL of water, sonicated, and incubated for 10 min at room temperature. The pH was determined using a potentiometer (pH and Ion-Meter GLP 22, Crison, Barcelona, Spain). The concentration of ammonia-N was determined using the method of Smith et al. (27 ) adapted to dog feces. Briefly, 1 g of feces were solubilized in 10 mL of KCl 2 M, centrifuged for 60 min at 5200 × g at 4°C, and the supernatant filtered using a 0.45 μm pore size polyethersulfone syringe filter (FILTER-LAB, Barcelona, Spain). Forty μL of supernatant were mixed with 40 μL of water, 2.5 mL of phenol solution and 2 mL of alkaline hypochlorite solution. After incubation for 10 min at 37°C and 40 min in the dark at 22°C, the absorbance of samples was read at 550 nm in a SynergyTM HT Multimode plate reader (BioTek® Instruments Inc., Winooski, VT). An ammonia solution (32 mg/dL) was used as standard. For volatile fatty acids (VFA) analysis, feces were acidified with ortho-phosphoric acid solution, centrifuged for 60 min at 2360 × g at 4°C, and the supernatant analyzed by gas chromatography as described by Pereira et al. (28 (link)).
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3

Urinalysis Methods and Measurements

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Color and turbidity were evaluated as recommended by Alleman and Wamsley (45 ). Urinalysis was performed with a dipstick, and pH and density, respectively, determined with a potentiometer (pH and Ion-Meter GLP 22, Crison, Barcelona, Spain) and a refractometer (URIVET hand refractometer, HPM003, Zuzi).
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4

Aqueous Extraction and Analysis of Aerial Plant Biomass

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Aqueous extracts from fresh aerial parts were prepared in a 1:2 (w/v) ratio at a temperature lower than 30 °C by mechanical grinding. Nitrates (mg NO3-·kg−1 fw) and pH were measured directly by pH and ION-Meter GLP 22+ (CRISON) equipment and with the respective electrodes, after calibrating each electrode. The total acidity was determined potentiometrically with 0.05 N NaOH solution, and the results are expressed as a percentage of citric acid.
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5

Fecal Ammonia and Volatile Fatty Acid Analysis

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Feces were thawed, and pH was determined using a potentiometer (pH and Ion-Meter GLP 22, Crison, Barcelona, Spain). Ammonia-N concentration was determined according to the method of Smith and Murphy (47 ) adapted to dog feces as described by Cabrita, Guilherme-Fernandes (48 (link)). Briefly, 1 g of feces were solubilized in 10 mL of KCl 2 M, centrifuged for 60 min at 5200 × g at 4°C, and the supernatant filtered using a 0.45 μm pore size polyethersulfone syringe filter (FILTER-LAB, Barcelona, Spain). Forty μL of supernatant were then mixed with 40 μL of water, 2.5 mL of phenol solution, and 2 mL of alkaline hypochlorite solution. After incubation for 10 min at 37°C and 40 min in the dark at 22°C, the absorbance of samples was read at 550 nm in a SynergyTM HT Multimode plate reader (BioTek® Instruments Inc., Winooski, VT). An ammonia solution (32 mg/dL) was used as a standard. Volatile fatty acid analysis was performed by gas chromatography in the supernatant from feces acidified with an orthophosphoric acid solution and centrifuged for 15 min at 2,360 × g at 4°C as described by Pereira, Maia (49 (link)).
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