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Drb200 cod reactor

Manufactured by HACH
Sourced in United States

The DRB200 COD Reactor is a laboratory equipment designed for the determination of Chemical Oxygen Demand (COD) in water samples. It provides a controlled environment for the digestion of samples at a specified temperature, which is a crucial step in the COD analysis process.

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3 protocols using drb200 cod reactor

1

Microalgae Growth Determination Protocol

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Chemical oxygen demand (COD) was measured by the US-EPA Standard Method 5220 using a HACH DRB200 COD reactor and HACH DR3900 spectrophotometer. Ammonium (NH3-N), total nitrogen (TN) and total phosphorus (TP) were determined by HACH standard kits using the HACH DR3900. Orthophosphate (PO4 3-) was measured using ion chromatography (IC) (Thermo Fisher, Australia). The system was equipped with a Dionex AS-AP auto-sampler and a Dionex AS19 IC column (7. The optical density and dry weight of microalgae culture were determined daily using a UV spectrophotometer (UV 6000 Shimadzu; Australia) at a wavelength of 680 nm and by gravimetric analysis, respectively to assess microalgae growth. For the optical density measurement, 3 mL of homogeneous microalgae cell suspension was transferred into a cuvette to measure the optical density. For gravimetric analysis, 50 mL of microalgae cell suspension was filtered through a 1.1 m pre-weighed glass filter paper. The filter paper was then dried at 60 °C for 4 hours to a constant mass. A linear regression coefficient (R 2 ) of 0.96 was confirmed between the optical density and dry weight biomass.
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2

Comprehensive Biogas Process Analysis

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The TS, VS, ammonia, and alkalinity were analyzed according to Standard Methods for the Examination of Water and Wastewater (APHA, 1999) . COD was analyzed using test kits (Ultra High Range, HACH, Loveland, CO, USA) with a HACH DRB200 COD Reactor and a HACH DR3900 spectrophotometer. Biogas production was recorded and normalized to STP conditions based on the local climatological data. The composition of biogas was analyzed using a gas chromatograph (GC126N, INESA, Shanghai, China) equipped with a thermal conductivity detector and a 2 m*3mm TDX-01 column (INESA, Shanghai, China) . The volatile fatty acids (VFAs) were determined using the direct injection method as previously described (Mu et al., 2018) . The composition of VFAs was characterized by GC-FID (6890B, Agilent Technologies, Palo Alto, CA, USA) using helium as carrier gas and a capillary column (DB-FFAP, 30 m × 0.25 mm × 0.25um, Agilent Technologies, Palo Alto, CA, USA). To visualize cell attachment to CMs, samples were prepared according to previously described method (Chen et al., 2014) , and the scanning electron micrographs were taken using Field Emission Scanning Electron Microscope (ZEISS Sigma, Germany).
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3

Comprehensive Water Quality Analysis

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Key water quality parameters of the primary effluent were measured according to standard methods. COD was measured using a Hach DRB200 COD Reactor and Hach DR3900 spectrophotometer (program number 435 COD HR) following the US-EPA Standard Method 5220. Adequate dilutions and adjustments were made to minimise chloride interference during sample measurements. A Shimadzu analyzer (TOC-V CSH ) was used to determine TOC concentration. An inductively coupled plasma-optical emission spectroscopy (ICP-OES) system (ICP-OES 710, Agilent, Australia) was used to determine the sodium ion concentration in the samples. Temperature, pH, and electrical conductivity were measured using an Orion 4-Star pH/conductivity meter (Thermo Scientific, Waltham, MA).
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