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Dr6000 spectrophotometer

Manufactured by HACH
49 citations
Sourced in United States, Germany
About the product

The DR6000 spectrophotometer is a laboratory instrument designed to measure the absorbance or transmittance of light in a sample. It is capable of analyzing a wide range of wavelengths and can be used for various applications in chemical analysis and environmental testing.

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49 protocols using «dr6000 spectrophotometer»

1

Comprehensive Biomass and Metabolite Analysis

2025
Biomass quantification was made by optical density (OD) at 600 nm using a UV-VIS DR6000 HACH spectrophotometer (Loveland, CO, USA) in a 1:10 dilution. Cell density was estimated using the standard curve of cell density (g/L) versus optical density (absorbance units) shown in Supplementary Figure S1.
Glucose, fructose, and ethanol concentrations were obtained by HPLC Agilent Technologies 1200 (Santa Clara, CA, USA) on an Aminex® (Dublin, Ireland) HPX-87H+ column (300 mm × 7.8 mm) under the following conditions: column temperature 65 °C, refractive index detector temperature 60 °C, injection volume 1 µL, and mobile phase sulfuric acid 0.5 mM at a constant flow rate of 0.6 mL/min [40 (link)].
Minor compound analysis was performed by GC/MS using an Agilent 7890A gas chromatograph equipped with an Agilent 5975C mass spectrometric detector (Santa Clara, CA, USA) following that reported by Acosta-García et al. [39 (link)]. In brief, the samples (1 µL) were injected in split mode (70:1) in an HP-FFAP column (30 m length × 0.32 mm inner diameter × 0.25 μm thickness; Agilent Technologies) to separate the compounds. High-purity helium (99.999%) was used as a carrier gas at a 1 mL/min constant flow. The injector temperature was 180 °C. The oven temperature was set to 40 °C for 3 min, then increased to 52 °C at 3 °C/min for 1 min, then increased to 200 °C at 10 °C/min, and held at 200 °C for 15 min. On the other hand, the mass spectrometer was operated at 230 °C, with an ionization voltage of −70 eV and SCAN mode (1.6 scans per second). An alkane ladder was injected to calculate the Kovats retention index of each compound. AMDIS software (v. 2.73, build 149.31) was used to identify the compounds.
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2

Water Quality Analysis Methods

2025
pH measurements were conducted using a standard F20-std-Kit pH meter manufactured by Mettler Toledo (Switzerland). BOD5 was determined using a BODTrakTM system. COD was calculated by preparing treatment samples in a reactor and employing a HACH model DRB200 (HACH Company, United States) for digestion at 150 °C for 2 h. Subsequent COD analysis was performed using a HACH DR6000 spectrophotometer (HACH Company, United States). Turbidity measurements were obtained using an AQUALYTIC HACH turbidity meter (HACH Company, United States). Total suspended solids (TSS) were determined according to standard method number 2540. A HACH-based HQ440d multiparameter probe (HACH Company, United States) was utilized for the analysis of total dissolved solids (TDS), pH, and electrical conductivity (EC). Color was measured at a wavelength of 450 nm using a HACH DR6000 spectrophotometer (HACH Company, United States) according to ASTM D2120 and expressed as platinum-cobalt units. Phenol concentration was determined according to ASTM D5530-D using a HACH DR6000 spectrophotometer at 510 nm. The pyridine colorimetric method was employed for the analysis.
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3

Comprehensive Characterization of Composite Materials

2024
The structural characteristics and elemental composition of the prepared materials were assessed using FESEM combined with EDX using a Nova Nano FE-SEM 450 model. The grain size distribution of ZF, CNM, and the composite ZFCNM was determined from FESEM images utilizing ImageJ software. Attenuated total reflectance-Fourier transform infrared (ATR-FTIR) spectra were acquired using a Bruker ATR-FTIR-8400S spectrophotometer to gain insights into molecular vibrations and structural information. Crystallinity and phase analysis of the materials were studied using XRD spectroscopy with a Bruker D8 Advance X-ray Powder Diffractometer, applying Cu Kα radiation (λ = 1.5406 nm). The analysis spanned a 2θ range of 10–70° with a step size angle of 0.01975°. Optical characteristics, including band gap energy, of ZF, CNM, and ZFCNM were determined through UV-visible diffuse reflectance spectroscopy (DRS) analysis. This was accomplished using a HACH (DR-6000) spectrophotometer at room temperature, employing the Tauc equation (eqn (1)): where α is the absorption coefficient, ℏ is Plank's constant, ν is the vibration frequency, and Eg (eV) is the energy band gap, while the “n” exponent is the type of transition and is equal to either ½ or 2 for a direct band gap or an indirect band gap energy, respectively. The textural features (e.g., pore volume, pore size distribution, and specific surface area) of synthesized ZF, CNM, and ZFCNM materials were determined through analysis of the N2 adsorption–desorption isotherms with the aid of the Brunauer–Emmett–Teller (BET) and the Barrett–Joyner–Halenda (BJH) model theories using Quantachrome (Autosorb-iQ-MP/XR) apparatus.
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4

Pollutant Degradation Using Catalytic Oxidation

2024
Pollutant degradation tests were conducted in a 50 mL beaker at room temperature (20.0 ± 2.0 °C) with magnetic stirring. Initially, 8.0 mg of the catalyst was added to 40.0 mL of a phenol solution (or other contaminants) at a specified concentration, followed by 2 min of ultrasonic dispersion and 20 min of magnetic stirring to ensure uniform suspension and achieve adsorption-desorption equilibrium. Subsequently, a precise amount of PMS stock solution was introduced to start the reaction. Samples were collected at regular intervals, immediately treated with L-ascorbic acid to stop the reaction, then subjected to high-speed centrifugation and filtered through a 0.22 μm PTFE filter. The analytes were quantified using ultra-performance liquid chromatography (UPLC, 1260 Infinity, Agilent Co., USA) equipped with a C18 column. All experiments were conducted in duplicate or triplicate to ensure reproducibility.
Cyclic stability was assessed through six successive BPA degradation tests. After each cycle, the catalyst was recovered by filtration, washed twice with deionized water, and resuspended in a fresh BPA solution via ultrasonication for subsequent use. The concentration of PMS was measured using low-concentration iodide methods with a UV-2450 spectrophotometer (Shimadzu Co., Japan). The effectiveness of treating real industrial wastewaters (see Supplementary Tables 5 and 6 for details) was gauged by measuring COD removal efficiency over 60 min using a DR-6000 spectrophotometer (Hach Co., USA).
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5

Photocatalytic Degradation of Organic Pollutants

2024
Pollutant degradation tests were conducted in a 50 mL beaker at room temperature (20.0 ± 2.0 °C) with magnetic stirring. Initially, 8.0 mg of the catalyst was added to 40.0 mL of a phenol solution (or other contaminants) at a specified concentration, followed by 2 min of ultrasonic dispersion and 20 min of magnetic stirring to ensure uniform suspension and achieve adsorption-desorption equilibrium. Subsequently, a precise amount of PMS stock solution was introduced to start the reaction. Samples were collected at regular intervals, immediately treated with L-ascorbic acid to stop the reaction, then subjected to high-speed centrifugation and filtered through a 0.22 μm PTFE filter. The analytes were quantified using ultra-performance liquid chromatography (UPLC, 1260 Infinity, Agilent Co., USA) equipped with a C18 column. All experiments were conducted in duplicate or triplicate to ensure reproducibility.
Cyclic stability was assessed through six successive BPA degradation tests. After each cycle, the catalyst was recovered by filtration, washed twice with deionized water, and resuspended in a fresh BPA solution via ultrasonication for subsequent use. The concentration of PMS was measured using low-concentration iodide methods with a UV-2450 spectrophotometer (Shimadzu Co., Japan). The effectiveness of treating real industrial wastewaters (see Supplementary Tables 5 and6 for details) was gauged by measuring COD removal efficiency over 60 min using a DR-6000 spectrophotometer (Hach Co., USA).
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Corresponding organizations : CAS Key Laboratory of Urban Pollutant Conversion, University of Science and Technology of China, Hefei National Center for Physical Sciences at Nanoscale

Top 5 most cited protocols using «dr6000 spectrophotometer»

1

Comprehensive Beer Quality Analysis

The basic
nonvolatile quality specifications are reported (Table 1). These quality specifications
were measured in duplicate for the samples evaluated in both the sensory
and consumer studies. The density, real extract (Er), and alcohol
content by weight (ABW) of decarbonated samples were measured using
a DMA 4100M and Alcolyzer Plus (Anton Paar, VA, USA). The pH and TA
were determined using an Orion Versa Star Pro advance electrochemistry
meter with an Orion ROSS Ultra refillable pH/ATC triode (8157BNUMD)
(Thermo Fisher Scientific, MA, U.S). The standard protocol outlined
by the American Society of Brewing Chemists (ASBC) was followed to
analyze TA.19 In brief, 0.1 M NaOH was
used to titrate the decarbonated samples at 25 °C to pH 8.2,
and the TA was reported as percent lactic acid.
BUs and color
were determined by both the ASBC and European Brewing Congress (EBC)
standard protocol, respectively, using a Hach DR6000 spectrophotometer
(Hach, CO, U.S.).19 BUs were determined
by adding 10 mL of cold carbonated beer (∼2 °C), 20 mL
of 2,2,4-trimethylpentane (TMP, isooctane) and 1 mL of 3 N HCl to
a 50 mL centrifuge tube and shaking for 15 min with a mechanical wrist
action shaker. The tubes were then centrifuged for 15 min at 5000
rpm, and the absorbance of the TMP (top) layer was measured at 275
nm and multiplied by 50 to report the BU value. For the color analysis,
the absorbance of decarbonated beer at 25 °C was measured at
both 430 and 700 nm. To report the EBC color value, the absorbance
at 430 nm was multiplied by 25. Samples with excessive turbidity were
filtered and remeasured. To determine the CO2 content,
samples were brought to 25 °C in a water bath and then measured
using a Haffmans Inpack 2000 CO2 calculator (Pentair Haffmans,
Zürich, CH). Turbidity of decarbonated samples at 25 °C
was measured using a Hach 2100AN turbidimeter (Hach, Loveland, CO).
Hop acids (Table S7) were determined
using reversed-phase high-performance liquid chromatography (HPLC)
operated under conditions outlined in the European Brewing Congress
(EBC) standard method 9.47.20 Isohumulones,
reduced isohumulones (rho, tetra, and hexa), and humulinones were
quantified at a wavelength of 270 nm using the international calibration
standards ICS-I4, ICS-T3, ICS-R3, ICS-H2, and ICS-Hum1, while humulones
(cohumulone, n-/ad-humulone, and total humulones (cohumulone + n-/ad-humulone)
were quantified at a wavelength of 340 nm using the international
calibration extract ICE4. All standards were purchased from Labor
Veritas AG, Zürich, CH.
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Corresponding organizations : University of California, Davis, Versuchs- und Lehranstalt für Brauerei in Berlin

2

Characterization of Y. lipolytica Lipid Production

For food waste fermentation, TS, VS, and pH were measured according to the standard method [30 ]. Suspended solids were separated from the fermentation effluent via centrifugation at 5000 rpm for 10 min, the liquid supernatant was filtrated through a 0.45-μm membrane, soluble COD (SCOD), total nitrogen (TN), and VFAs were measured. The SCOD was analyzed following the HACH method. VFAs were determined using GC (Shimadzu, GC-2014) with a flame ionization detector and capillary column (Stabilwax-DA, 30 m × 0.25 mm × 0.25 μm). The temperature program followed that of previous methods [31 (link)].
For Y. lipolytica cultivation, a sterile pipette was used to periodically withdraw 1.5-mL samples from the batch cultures. To describe cell growth, cell concentrations were measured as the absorbance of the culture broth at 600 nm (OD600, DR-6000 spectrophotometer, HACH). Biomass production was expressed as DCW (dry cell weight). Cells were harvested from 10 mL of culture medium by centrifugation at 10,000 rpm for 10 min; washed with ethanol (95%) and hexanes to remove extracellular fatty acids [32 (link)]; and dried to constant weight at 105 °C in an oven, and then weighed.
Lipids were extracted in accordance with the method of Bligh and Dyer [32 (link)] with modifications [33 ]. Lipids were extracted from lyophilized biomass using a mixture of chloroform and methanol (2:1 v/v). The lipid mixture was centrifuged at 5000g for 25 min to completely dissolve the lipids in the solvent. Then, the organic phase was washed twice with 0.15% (w/v) NaCl solution. The purified chloroform layer was evaporated to dryness with nitrogen gas (Nitrogen Evaporation System). Lipid production was expressed as gram lipid per liter culture media. The lipid content was expressed as gram lipid per gram DCW (%).
The fatty acid composition of lipids was determined by GC analysis of FAMEs. FAMEs were converted from fatty acids via saponification followed by methylation in accordance with the method of [34 ]. FAMEs were analyzed by using a GC-8600 gas chromatograph (Tianpu Instrument Co., Ltd., Beijing, China) equipped with a flame-ionized detector and CP-Sil 88 capillary column (Agilent, USA, 60 m × 0.25 mm × 0.36 µm). The column temperature was maintained at 190 °C for 10 min, increased from 190 to 240 °C at a rate of 10 °C/min, and maintained at 240 °C for 15 min. Hydrogen was used as the carrier gas at 1.0 mL/min. The split ratio was 1:30 (v/v). The injector and the detector temperatures were set at 270 and 300 °C, respectively. Fatty acids were identified by comparing their retention times with those of standard solutions, then quantified based on their respective peak areas and normalized.
To further confirm the cell growth and lipid accumulation in Y. lipolytica, fluorescent testing was carried out with laser scanning fluorescence microscopy (LSCM). An amount of 10 μL cell sample from batch cultures was carefully collected at the end of the stationary phase, subsequently stained with 10 μL Nile Red, and imaged with laser scanning confocal microscopy (Leica TCS SP2) under an exciting wavelength of 543 nm.
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Corresponding organizations : University of Science and Technology Beijing

3

Wastewater Analysis of Beverage Factory

The samples were collected from a beverage manufacturing factory located at Nilai, Negeri Sembilan, Malaysia and tested according to the method adopted from the Standard Methods for the examination of water and wastewater analysis [30 ]. COD was measured using an HACH Spectrophotometer DR6000 (Standard Method 5220 D for low range value and high range value) after being heated in COD reactor at 150 °C for 2 h. TSS measurement was carried out after filtration using a 0.45 µm filter on the vacuum pump, and the sample was heated in a drying oven at 103 °C. The gravimetric method was applied for TSS measurement.
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Corresponding organizations : Universiti Putra Malaysia, Jabatan Perkhidmatan Awam Malaysia, Islamic University of Technology, Swinburne University of Technology

4

Comprehensive Characterization of Nanomaterials

UV–Vis/DRS absorption studies were performed in a HACH DR6000 spectrophotometer. Dynamic Light Scattering (DLS) was completed in a Malvern Zetasizer ZSU3100, and Mass magnetic susceptibility was determined in an MSB MK1 Sherwood balance. Transmission Electron Microscopy was performed in a JEOL 2010 (200 kV) using C-coated copper grids. A JEOL JSM 5900 Scanning Electron Microscopy (20 kV) equipped with an Oxford AZtec Energy Dispersive X-Ray Spectrometry was utilized to study morphology. The X-ray diffraction studies were obtained using a Bruker D8 Advance equipped with a Cu Ka = 0.154 nm radiation source. COD was measured through the dichromate modification of the EPA 410.4 method with HI94754C-25 kits for high ranges (0 to 15,000 mg/L). BOD5 was determined using the Standard 5210B method (APHA) with a HACH BOD Trak II kit.
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5

Physicochemical Characteristics Influencing HCoV Decay

The physicochemical characteristics of water and wastewater plays an indispensable role in HCoVs decay, since it has been suggested that the inactivation HCoVs has a close relationship with temperature, total organic matter, and hostile bacteria presence in water (Gundy et al., 2008 ). For this reason, the main parameters of the collected aqueous samples were measured following standard methods at Magalies Water Services Laboratory (ISO/IEC 17025:2017 accredited) in Brits, North West, South Africa. Specifically, the pH, temperature, and EC were measured using an HQ40d Portable Meter (Hach Company - US). The DR6000 spectrophotometer (Hach Company - US) was used to measure COD, orthophosphate, nitrate, and ammonia content in sewage water (highly concentrated samples) and the Gallery™ Plus Discrete Analyzer (Thermo Fisher Scientific Inc. - US) was used to measure the same parameters in surface and potable water (less concentrated samples). Finally, free chlorine was measured using the DR900 colorimeter (Hach Company - US).
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Corresponding organizations : Scientific Services, University of South Africa, Heriot-Watt University

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