Fotómetro de sobremesa multiparamétrico de calidad del agua
Product Overview
HI83399 is a compact multi-parameter photometer for measuring key water and wastewater quality parameters. This photometer is one of the most advanced photometers, featuring an innovative optical design that utilizes a reference detector and focusing lens to eliminate errors caused by light source variations and glass cuvette defects. 40 key water and wastewater quality parameters, 73 different methods, covering multiple ranges, are programmed into the meter. Digestion parameters for wastewater treatment include COD, total nitrogen, and total phosphorus, which are important for monitoring nutrient removal. HI83399 also provides an absorbance measurement mode for performance verification and for users who wish to develop their own concentration versus absorbance curves.
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To save valuable laboratory benchtop space, HI83399 doubles as a professional pH meter with its digital pH/temperature electrode input. Now, one meter can be used for both photometric and pH measurements.
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Advanced optical system
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Unrivaled performance for a benchtop photometer
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Digital pH electrode input
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Save valuable benchtop space by using one meter that serves as both a photometer and a laboratory pH meter
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Digestion parameters for water and wastewater treatment
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Allows measurement of COD, total nitrogen, and total phosphorus
| SKU | HI83399-02 |
|---|---|
| Product Name | Water & Wastewater Multiparameter (with COD) Photometer and pH meter - HI83399 |
| Quote Required | Yes |
| pH Range | Photometer |
| pH Resolution | Photometer |
| pH Accuracy | Photometer |
| pH Calibration | Automatic one or two point calibration with one set of standard buffers available (4.01, 6.86, 7.01, 9.18, 10.01) |
| pH Temperature Compensation | Automatic (-5.0 to 100.0 oC; 23.0 to 212.0 oF); limits reduced based on the pH electrode used |
| pH CAL Check (electrode diagnostics) | clean electrode and check buffer/check probe displayed during calibration |
| pH Method | Photometer |
| pH-mV Range | ±1000 mV |
| pH-mV Resolution | 0.1 mV |
| pH-mV Accuracy | ±0.2 mV |
| Dissolved Oxygen Range | 0.0 to 10.0 mg/L (as O2) |
| Dissolved Oxygen Resolution | 0.1 mg/L |
| Dissolved Oxygen Accuracy | ±0.4 mg/L ±3% of reading |
| Dissolved Oxygen Measurement Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, Azide modified Winkler method |
| Absorbance Range | 0.000 to 4.000 Abs |
| Absorbance Resolution | 0.001 Abs |
| Absorbance Accuracy | +/-0.003Abs @ 1.000 Abs |
| Alkalinity Range | Freshwater |
| Alkalinity Resolution | 1 mg/L |
| Alkalinity Accuracy | ±5 mg/L ±5% of reading |
| Alkalinity Method | Colorimetric method |
| Aluminum Range | 0.00 to 1.00 mg/L (as Al3+) |
| Aluminum Resolution | 0.01 mg/L |
| Aluminum Accuracy | ±0.04 mg/L ±4% of reading |
| Aluminum Method | Adaptation of the aluminon method |
| Ammonia Range | Low Range |
| Ammonia Resolution | Low and Medium Range |
| Ammonia Accuracy | Low Range |
| Ammonia Method | Adaptation of the ASTM Manual of Water and Environmental Technology, D1426-92, Nessler method |
| Anionic Surfactants Range | 0.00 to 3.50 mg/L (as SDBS) |
| Anionic Surfactants Resolution | 0.01 mg/L |
| Anionic Surfactants Accuracy | ±0.04 mg/L ±3% of reading |
| Anionic Surfactants Method | Adaptation of the USEPA method 425.1 and Standard Methods for the Examination of Water and Wastewater, 20th edition, 5540C, Anionic Surfactants as MBAS |
| Bromine Range | 0.00 to 8.00 mg/L (as Br2) |
| Bromine Resolution | 0.01 mg/L |
| Bromine Accuracy | ±0.08 mg/L ±3% of reading |
| Bromine Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, DPD method. |
| Calcium Range | Freshwater |
| Calcium Resolution | 1 mg/L |
| Calcium Accuracy | Freshwater |
| Calcium Method | Freshwater |
| Chemical Oxygen Demand Range | Low Range |
| Chemical Oxygen Demand Resolution | 1 mg/L |
| Chemical Oxygen Demand Accuracy | Low Range |
| Chemical Oxygen Demand Method | Adaptation of the USEPA 410.4 ISO dichromate methods Mercury-free dichromate green method (LR & MR); dichromate method (HR) |
| Chloride Range | 0.0 to 20.0 mg/L (as Cl⁻) |
| Chloride Resolution | 0.1 mg/L |
| Chloride Accuracy | ±0.5 mg/L ±6% of reading at 25 °C |
| Chlorine Dioxide Range | 0.00 to 2.00 mg/L (as ClO2) |
| Chlorine Dioxide Resolution | 0.01 mg/L |
| Chlorine Dioxide Accuracy | ±0.10 mg/L ±5% of reading |
| Chlorine Dioxide Method | Adaptation of the Chlorophenol Red method. |
| Free Chlorine Range | 0.00 to 5.00 mg/L (as Cl2) Ultra Low Range |
| Free Chlorine Resolution | 0.01 mg/L Ultra Low Range |
| Free Chlorine Accuracy | ±0.03 mg/L ±3% of reading Ultra Low Range |
| Total Chlorine Range | 0.00 to 5.00 mg/L (as Cl2) Ultra Low Range |
| Total Chlorine Resolution | 0.01 mg/L Ultra Low Range |
| Total Chlorine Accuracy | ±0.03 mg/L ±3% of reading Ultra Low Range |
| Chlorine Method | Adaptation of the EPA 330.5 DPD method Free Chlorine (ULR) & Total Chlorine (UHR) |
| Chromium, Hexavalent Range | Low Range |
| Chromium, Hexavalent Resolution | 1 μg/L |
| Chromium, Hexavalent Accuracy | Low Range |
| Chromium, Hexavalent Method | Adaptation of the ASTM Manual of Water and Environmental Technology, D1687-92, Diphenylcarbohydrazide method. |
| Color, Water Range | 0 to 500 PCU (Platinum Cobalt Units) |
| Color, Water Resolution | 1 PCU |
| Color, Water Accuracy | ±10 PCU ±5% of reading |
| Color, Water Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, Colorimetric Platinum Cobalt method. |
| Copper Range | Low Range |
| Copper Resolution | 0.001 mg/L; 0.01 mg/L |
| Copper Accuracy | Low Range |
| Copper Method | Adaptation of the EPA bicinchoninate method |
| Cyanuric Acid Range | 0 to 80 mg/L (as CYA) |
| Cyanuric Acid Resolution | 1 mg/L |
| Cyanuric Acid Accuracy | ±1 mg/L ±15% of reading |
| Cyanuric Acid Method | Adaptation of the turbidimetric method |
| Fluoride Range | Low Range |
| Fluoride Resolution | 0.01 mg/L; 0.1 mg/L |
| Fluoride Accuracy | Low Range |
| Fluoride Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, SPADNS method |
| Hardness, Total Range | Low Range |
| Hardness, Total Resolution | 1 mg/L |
| Hardness, Total Accuracy | Low Range |
| Hardness, Total Method | Adaptation of the EPA recommended method 130.1 |
| Hardness, Calcium Range | 0.00 to 2.70 mg/L (as CaCO3) |
| Hardness, Calcium Resolution | 0.01 mg/L |
| Hardness, Calcium Accuracy | ±0.11 mg/L ±5% of reading |
| Hardness, Calcium Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, Calmagite method |
| Hardness, Magnesium Range | 0.00 to 2.00 mg/L (as CaCO3) |
| Hardness, Magnesium Resolution | 0.01 mg/L |
| Hardness, Magnesium Accuracy | ±0.11 mg/L ±5% of reading |
| Hardness, Magnesium Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, EDTA Colorimetric method |
| Hydrazine Range | 0 to 400 μg/L (as N2H4) |
| Hydrazine Resolution | 1 μg/L |
| Hydrazine Accuracy | ±4% of full scale reading |
| Hydrazine Method | Adaptation of the ASTM Manual of Water and Environmental Technology, method D1385-88, p-Dimethylaminobenzaldehyde method |
| Iodine Range | 0.0 to 12.5 mg/L (as I2) |
| Iodine Resolution | 0.1 mg/L |
| Iodine Accuracy | ±0.1 mg/L ±5% of reading |
| Iodine Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, DPD method |
| Iron Range | Low Range |
| Iron Resolution | 0.001 mg/L; 0.01 mg/L |
| Iron Accuracy | Low Range |
| Iron Method | Low Range |
| Magnesium Range | 0 to 150 mg/L (as Mg2+) |
| Magnesium Resolution | 1 mg/L |
| Magnesium Accuracy | ±5 mg/L ±3% of reading |
| Magnesium Method | Adaptation of the Calmagite method |
| Manganese Range | Low Range |
| Manganese Resolution | 1 μg/L; 0.1 mg/L |
| Manganese Accuracy | Low Range |
| Manganese Method | Low Range |
| Molybdenum Range | 0.0 to 40.0 mg/L (as Mo6+) |
| Molybdenum Resolution | 0.1 mg/L |
| Molybdenum Accuracy | ±0.3 mg/L ±5% of reading |
| Molybdenum Method | Adaptation of the mercaptoacetic acid method |
| Nickel Range | Low Range |
| Nickel Resolution | 0.001 mg/L; 0.01 g/L |
| Nickel Accuracy | Low range |
| Nickel Method | Low Range |
| Nitrate Range | 0.0 to 30.0 mg/L (as NO3-- N) 16 mm vial |
| Nitrate Resolution | 0.1 mg/L |
| Nitrate Accuracy | ±0.5 mg/L ±10% of reading 16 mm vial |
| Nitrate Method | Adaptation of the cadmium reduction method 16 mm vial |
| Nitrite Range | Freshwater Low Range |
| Nitrite Resolution | Freshwater |
| Nitrite Accuracy | Freshwater Low Range |
| Nitrite Method | Low Range and Seawater |
| Nitrogen, Total Range | Low Range |
| Nitrogen, Total Resolution | 0.1 mg/L; 1 mg/L |
| Nitrogen, Total Accuracy | Low Range |
| Nitrogen, Total Method | Chromotropic acid method |
| Oxygen, Scavenger Range | 0 to 1000 μg/L (as DEHA) 0.00 to 1.50 mg/L (as Carbohydrazide) 0.00 to 2.50 mg/L (as Hydroquinone) 0.00 to 4.50 mg/L (as ISO-ascorbic acid) |
| Oxygen, Scavenger Resolution | 1 μg/L (DEHA); 0.01 mg/L |
| Oxygen, Scavenger Accuracy | ±5 μg/L ±5% of reading |
| Oxygen, Scavenger Method | Adaptation of the iron reduction method |
| Ozone Range | 0.00 to 2.00 mg/L (as O3) |
| Ozone Resolution | 0.01 mg/L |
| Ozone Accuracy | ±0.02 mg/L ±3% of reading |
| Ozone Method | Colorimetric DPD Method |
| Phosphate Range | Freshwater Low Range |
| Phosphate Resolution | Freshwater |
| Phosphate Accuracy | Freshwater Low Range |
| Phosphate Method | Freshwater Low Range |
| Phosphorous, Acid Hydrolyzable Range | 0.00 to 1.60 mg/L (as P) |
| Phosphorous, Acid Hydrolyzable Resolution | 0.01 mg/L |
| Phosphorous, Acid Hydrolyzable Accuracy | ±0.05 mg/L or ±5% of reading |
| Phosphorous, Acid Hydrolyzable Method | Adaptation of the EPA method 365.2 and Standard Methods for the Examination of Water and Wastewater, 20th edition, 4500-P E, ascorbic acid method |
| Phosphorous, Reactive Range | Low Range |
| Phosphorous, Reactive Resolution | 0.01 mg/L; 0.1 mg/L |
| Phosphorous, Reactive Accuracy | Low Range |
| Phosphorous, Reactive Method | Low Range |
| Phosphorous, Total Range | Low Range |
| Phosphorous, Total Accuracy | Low Range |
| Phosphorous, Total Resolution | Low Range |
| Phosphorous, Total Method | Low Range |
| Potassium Range | 0.0 to 20.0 mg/L (as K) |
| Potassium Resolution | 0.1 mg/L |
| Potassium Accuracy | ±3.0 mg/L ±7% of reading |
| Potassium Method | Adaptation of the Turbidimetric Tetraphenylborate method |
| Silica Range | Low Range |
| Silica Resolution | 0.01 mg/L; 1 mg/L |
| Silica Accuracy | Low Range |
| Silica Method | Low Range |
| Silver Range | 0.000 to 1.000 mg/L (as Ag) |
| Silver Resolution | 0.001 mg/L |
| Silver Accuracy | ±0.020 mg/L ±5% of reading |
| Silver Method | Adaptation of the PAN method |
| Sulfate Range | 0 to 150 mg/L (as SO42-) |
| Sulfate Resolution | 1 mg/L |
| Sulfate Accuracy | ±5 mg/L ±3% of reading |
| Sulfate Method | Turbidimetric - Sulfate is precipitated with barium chloride crystals |
| Zinc Range | 0.00 to 3.00 mg/L (as Zn) |
| Zinc Resolution | 0.01 mg/L |
| Zinc Accuracy | ±0.03 mg/L ±3% of reading |
| Zinc Method | Adaptation of the Standard Methods for the Examination of Water and Wastewater, 18th edition, Zincon method |
| Input Channels | 1 pH electrode input and 5 photometer wavelengths |
| pH Electrode | digital pH electrode (not included) |
| Photometer/Colorimeter Light Source | 5 LEDs with 420 nm, 466 nm, 525 nm, 575 nm, and 610 nm narrow band interference filters |
| Photometer/Colorimeter Light Detector | silicon photodetector |
| Bandpass Filter Bandwidth | 8 nm |
| Bandpass Filter Wavelength Accuracy | ±1 nm |
| Cuvette Type | round, 24.6 mm |
| Number of Methods | 128 max. |
| GLP | calibration data for connected pH electrode |
| Display | 128 x 64 pixel LCD with backlight |
| Logging Type | log on demand with user name and sample ID optional input |
| Logging Memory | 1000 readings |
| Connectivity | USB-A host for flash drive; micro-USB-B for power and computer connectivity |
| Power Supply | 5 VDC USB 2.0 power adapter with USB-A to micro-USB-B cable (included) |
| Battery Type/Life | 3.7 VDC Li-polymer rechargeable battery / >500 photometric measurements or 50 hours of continuous pH measurement |
| Environment | 0 to 50.0 oC (32 to 122.0 oF); 0 to 95% RH, non-condensing |
| Weight | 1.0 kg (2.2 lbs.) |
| Dimensions | 206 x 177 x 97 mm (8.1 x 7.0 x 3.8") |
| Ordering Information | HI83399 is supplied with sample cuvettes and caps (4 ea.), cloth for wiping cuvettes, USB to micro USB cable connector, power adapter and instruction manual. |
Casos de servicio
Tratamiento de Aguas Residuales Municipales — Hanna: caso de configuración desde stock
Resumen del proyecto
La instalación está en las etapas de entrada, biológica y salida de una planta municipal. El cliente quería configurar bien Hanna en la planta existente, con el objetivo de análisis portátil y de laboratorio con instrumentos Hanna.
Retos técnicos
Lo que realmente da problemas es alto contenido de sólidos y componentes corrosivos, con grandes variaciones diarias de caudal, y los parámetros del efluente oscilan y las sondas se ensucian con lodos y biopelícula. Todo ello implica que la configuración de Hanna deba incluir selección por parámetros, precisión y portabilidad.
Configuración
El suministro y la instalación se organizaron por la vía de stock: configurar desde stock y entregado con rapidez. En planta esto supuso selección por parámetros, precisión y portabilidad; se revisó línea a línea: cumplimiento estable del nivel 1A y reporte de datos en línea.
Comportamiento
Tras la puesta en marcha el resultado es resultados in situ, con menos verificaciones de laboratorio, y las lecturas se usan ya para ajustar el proceso.
Alimentación y Bebidas — Hanna: caso de configuración desde stock
Situación en planta
Se trata de un cliente del sector Alimentación y Bebidas cuya planta está en las etapas de dosificación, pasteurización, llenado y limpieza CIP. La tarea principal era análisis portátil y de laboratorio con instrumentos Hanna.
El problema
La dificultad está en jarabes, lácteos y bebidas proclives a incrustaciones, con estrictos requisitos higiénicos; a la vez, las limpiezas frecuentes exigen instrumentos resistentes a ciclos CIP/SIP con sosa caliente. Por eso la especificación implica selección por parámetros, precisión y portabilidad.
Qué hicimos
Adoptamos un enfoque de stock: configurar desde stock y entregado con rapidez. La entrega se construyó en torno a selección por parámetros, precisión y portabilidad; se verificó punto por punto: requisitos de seguridad alimentaria y diseño higiénico 3-A / EHEDG.
Resultado operativo
En servicio el sistema responde a lo previsto: resultados in situ, con menos verificaciones de laboratorio, con un mantenimiento rutinario notablemente menor.
Química y Farmacéutica — Hanna: caso de configuración desde stock
Contexto de aplicación
reactores, vasijas de dosificación y tanques de producto terminado es un servicio típico de Química y Farmacéutica. El proyecto partió de Hanna, centrándose en análisis portátil y de laboratorio con instrumentos Hanna.
Limitaciones del proceso
la corrosión y la protección Ex acortan la vida útil y encarecen las paradas, y medios muy corrosivos con disolventes y cristalización, en parte en atmósferas explosivas no hace sino acentuarlo. Por eso la especificación de Hanna debe cubrir selección por parámetros, precisión y portabilidad.
Enfoque de suministro
La entrega se gestionó como stock: configurar desde stock y entregado con rapidez. La ejecución se centró en selección por parámetros, precisión y portabilidad, junto con certificación Ex y trazabilidad de datos según GMP.
Resultados en campo
La operación evidencia el beneficio: resultados in situ, con menos verificaciones de laboratorio, con una confianza claramente mayor en este punto de medición.
Energía y Electricidad — Hanna: caso de configuración desde stock
Perfil del cliente
El entorno típico en Energía y Electricidad es agua de alimentación, condensado de turbina y sistemas de desulfuración/DeNOx. El punto de medición es Hanna; el foco es análisis portátil y de laboratorio con instrumentos Hanna.
Dificultades clave
Las condiciones son alta temperatura y presión, con vapor y agua salina y, encima, deriva a alta temperatura y presión, con paradas no programadas muy costosas, algo que una configuración estándar no soporta mucho tiempo. El diseño parte de selección por parámetros, precisión y portabilidad.
Implementación
El alcance se canalizó por la vía de stock: configurar desde stock y entregado con rapidez. Técnicamente se apoya en selección por parámetros, precisión y portabilidad, y en estos requisitos: cumplimiento de normativas del sector y objetivos de disponibilidad.
Beneficio para el cliente
En la práctica esto significa resultados in situ, con menos verificaciones de laboratorio, lo que redujo la carga del equipo de mantenimiento.
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