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Hq40d portable multi meter

Manufactured by HACH
Sourced in United States

The HQ40D Portable Multi Meter is a handheld device designed for measuring various water quality parameters. It can measure pH, conductivity, dissolved oxygen, and other water quality parameters.

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8 protocols using hq40d portable multi meter

1

Marine Environment Water Quality Monitoring

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Water salinity (21.1–29.5‰), pH (7.81–9.18), and temperature (23.7–26°C) were measured (Hach HQ40d Portable Multimeter, Loveland, CO) daily around 11:00 by the animal caretakers and this data are provided in Appendix 1. Air temperature (kept between 24°C and 28°C) was regulated by means of air‐conditioning and ventilation at the top of the roof, while relative humidity (± 70%) was controlled by means of water sprayers.
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2

Automated Seawater Temperature Control

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Automated controls of seawater temperatures were provided by SeaSim via the SCADA (Supervisory Control and Data Acquisition) system. Seawater temperature of each tank was monitored hourly using resistance temperature detector (RTD). To confirm the treatment conditions inside the 6-well plates (i.e., where the larvae were located), seawater that was removed from the wells during water change was collected for measurement of O2 level, salinity, temperature and pH every day at 12:00 using the HACH HQ40D Portable Multi Meter. Salinity measurements were calibrated with IAPSO Standard Seawater. Seawater from several wells of the same tank was combined for measurement due to depth requirement of the measurement probes. Total alkalinity (AT) was measured twice during the 10-day experiment using VINDTA calibrated to Dickson’s Certified Reference Material. Ωarag (aragonite saturation state) and DIC (dissolved inorganic carbon) were calculated using the measured values of seawater AT, pH, temperature and salinity, with the program CO2SYS98 as implemented in Microsoft Excel by Pierrot et al.99 .
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3

Soil Characterization for Ecological Research

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When all samples had been taken, the bulk soil samples were thawed and air dried for 48 h, disaggregated, and allowed to air dry again to reach a constant mass. Each sample was weighed and ground to pass through a 2-mm sieve, with any material not passing through weighed and discarded. The remaining material was then all ground to pass through a 355-μm sieve to improve sample uniformity and amalgamation. SOM was then determined by the Walkley-Black dichromate method (Walkley and Black 1934 ). Plant available P was determined using Olsen’s reagent (Olsen et al. 1954 ) and measured colorimetrically in solution by spectrophotometry using the molybdenum blue method (Murphy and Riley 1962 ). Soil N content was determined as Total Kjeldahl Nitrogen (TKN) using the method 4500-Norg Nitrogen (Organic) (Standard Methods for the Examination of Water and Wastewater 2018 ) with a 50:1 dilution of water/soil, copper catalyst tablets (Fisher Scientific, 1g Na2SO4 and the equivalent of 0.1g CuSO4, Fisher chemical K/0120/80), a Buchi B-435 Digestion Unit, and Buchi B324 Distillation Unit. pH was measured using a 1:2.5 v/v suspension in water (World Agroforestry Centre 2014 ) using a Hach Intellical PHC201 pH electrode and Hach HQ40D portable multimeter.
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4

Viscosity and Conductivity of EE100 Solution

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The viscosity of EE100 solution in the OEE was measured by a rotational viscometer Alpha series (Fungilab, Barcelona, Spain) equipped with L1 spindles at 25 °C and a 10 rpm shear rate. The measurement was taken after 10 s. The conductivity of EE100 solution in the OEE was measured by the HQ40d portable multi meter (Hach, Loveland, CO, USA) at room temperature (25 ± 1 °C).
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5

Comprehensive Water Quality Monitoring

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All localities were also sampled for basic water physicochemical and chemical analysis once a month throughout the year. Water temperature, electrical conductivity, pH and dissolved oxygen were measured in situ with a Hach HQ40D Portable Multi Meter under standard conditions. Furthermore, water samples were collected and analyzed in an accredited laboratory (Central Water Management Laboratory, Zagreb) for total alkalinity, total suspended solids, biochemical oxygen demand and chemical oxygen demand, as well as for nitrogen and phosphorus compounds (ammonium, nitrites, nitrates, total nitrogen, orthophosphates and total phosphorus) (Table 1). The land use in the catchment area of each sampling site was obtained from the database of Hrvatske vode—the legal entity for water management. Here, four distinct categories are recognized and calculated from the CORINE land cover dataset [81 ]—natural area, urban area, and intensive and extensive agricultural land (Table 1).
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6

Anaerobic P. aeruginosa Biofilm Cultivation

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P. aeruginosa biofilms were grown and treated under anoxic conditions in an anaerobic growth chamber (Concept 400 Anaerobic Workstation, Ruskinn Technology Ltd., UK). The gas atmosphere consisted of N2/H2/CO2 (ratio, 80:10:10). Anoxia was confirmed with an optical O2 sensor (HQ40d Portable multi meter; HACH Company, CO, USA) placed in the growth chamber. To remove traces of O2, all media and chemical solutions applied for anaerobic work were equilibrated in the anaerobic chamber 3 days prior to experiment.
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7

Multidimensional Assessment of Aquatic Ecosystems

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All localities were also sampled for basic water physicochemical and chemical parameters once a month throughout the year. Conductivity, pH, water temperature and dissolved oxygen were measured in situ with a Hach HQ40D Portable Multi Meter under standard conditions. Water samples were collected and analysed in an accredited laboratory (Central Water Management Laboratory, Zagreb, Croatia) for nine additional water chemistry parameters (Table 5).
Furthermore, physiographic and climatic environmental variables were obtained from several data sets using ArcGIS 10.5 software. Altitude was obtained from the digital elevation model EU-DEM v1.0 [70 ], distance from the source from topographic maps 1:25,000 [71 ], catchment area from the database of Hrvatske vode—the legal entity for water management and bioclimatic variables from CHELSA climatological datasets [72 (link)] (Table 5).
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8

Methane Removal Monitoring Protocol

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To monitor methane removal, 3 mL water samples were collected weekly from the influent and effluent ports. Influent ports were placed approximately 7 cm before the water/methane mixture entry to the reactors while effluent samples were collected by inserting the tip of a gas-tight syringe directly into the effluent tubing. To avoid loss of dissolved methane during sample collection from the influent port, samples were collected with a 5 cm long needle with a gas tight syringe inserted into the tube from the sampling port. Dissolved oxygen (DO) in the effluents from the reactors was measured in a flow-through set-up with a DO probe (HQ40d portable multi meter with a LDO101 probe, HACH, Loveland, Colorado, USA).
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