Provided is a centrifugal field-flow fractionation device that can stably press a fixing member toward an inner peripheral surface of a rotor by a wedge-shaped member, even when a relatively large centrifugal force acts on the wedge-shaped member. An arc-shaped (C-shaped) fixing member 17 is provided along an inner peripheral surface of a channel member 16 on a side of a rotation axis of the channel member 16. A wedge-shaped member 18 is attached between opposite ends of the fixing member 17 and applies a force in a direction of spreading the opposite ends apart, to thereby press the fixing member 17 toward the inner peripheral surface of the rotor 14. The wedge-shaped member 18 has a pair of contact surfaces 184 that respectively come into contact with the opposite ends of the fixing member 17. The pair of contact surfaces 184 include tapered surfaces that gradually taper down toward the rotor 14, so that the distance between the contact surfaces 184 gradually shortens as the contact surfaces 184 come close to the rotor 14.

An apparatus for determining the mean corpuscular haemoglobin concentration (MCHC) in a whole blood sample includes a sample holder including an elongate sample chamber having an open end and a closed end. A holding member is adapted to receive and retain the sample holder. The holding member rotates may rotate about an axis of rotation. When the sample holder is received and retained by the holding member the sample chamber is substantially perpendicular to the axis of rotation. First and second light sources are positioned on one side of the sample holder and are configured to emit light in respective different frequencies. At least one light sensor is positioned on a second side of the sample holder, opposite from the first side, so that light from the light source may pass through the sample chamber, in at least one rotational position of the sample holder, and impinge on the light sensor.

A method is disclosed for monitoring deposit formation in an aqueous process. The method includes providing a feed flow of aqueous liquid onto a receiving surface of a monitoring cell. At least part of the receiving surface is illuminated with a light source. Visual data is collected at a multitude of positions across the receiving surface, and the collected visual data is analysed. A quantitative scaling and/or fouling indication is computed for the receiving surface. The monitoring cell has an inlet for the aqueous feed flow and an outlet for a reject flow from the monitoring cell. The receiving surface includes a selective barrier membrane. The feed flow is directed to the receiving surface at an elevated pressure to produce a permeate part that passes through the selective barrier membrane, and a concentrate part that forms the reject flow.

Provided is a biological sample imaging device and a biological sample imaging method that are capable of disposing a sufficient number of large-sized particles in a biological sample so as to be moderately dispersed within an imaging range. The biological sample imaging method includes: a first step of introducing a biological sample containing particles into a liquid flow channel; a second step of causing the biological sample introduced into the liquid flow channel to flow in a forward direction; a third step of causing the biological sample to flow in a reverse direction after the second step; and an imaging step of taking, in an imaging cell, images of the particles contained in the biological sample that remains in the liquid flow channel after the third step.

The present invention relates to a testing method for testing a state of an aeration tank in a wastewater treatment facility that uses activated sludge. The testing method comprises obtaining a difference between: a sedimentation amount when a given period of time has elapsed after an activated sludge mixed liquid collected from the aeration tank and water having a higher dissolved oxygen concentration than the activated sludge mixed liquid are poured into the same container and mixed together; and a sedimentation amount when a period of time equal to the given period of time has elapsed after the activated sludge mixed liquid collected from the aeration tank and water having a lower dissolved oxygen concentration than the activated sludge mixed liquid are poured into the same container and mixed together.

Disclosed herein are devices and methods for the real-time detection of aeropathogens. The device includes an aerosampler having an air inlet and at least one collector tube, a microfluidic system which includes a container, piping, a micro-pump for flowing a liquid, and a viral detection chamber. The viral detection chamber has an electrode which may be equipped with functionalized biosensors, a counter electrode, an electronic detection system connectable to the electrodes of the viral detection chamber, and an embedded electronic processing system for processing data from the electronic detection system.

A method for measuring a concentration of molecules, characterized in that the method measures the concentration of molecules dissolved in a continuous phase of a colloid and includes obtaining a test sample by mixing a number of molecules with a volume of colloid, obtaining a control sample by mixing a number of molecules with a volume of a composition comprising a particle-free solution extracted from a fraction of the continuous phase of same colloid used in the obtaining the test sample, so that a value of the concentration of molecules in the mixture is equal to the value of the concentration of molecules in the test sample obtained in the obtaining the test sample, and submitting the test and the control samples obtained in the obtaining the test sample and obtaining the control sample to a process in order to concentrate the particles of the test sample.

Disclosed herein are devices and methods for the real-time detection of aeropathogens. The device includes an aerosampler having an air inlet and at least one collector tube, a microfluidic system which includes a container, piping, a micro-pump for flowing a liquid, and a viral detection chamber. The viral detection chamber has an electrode which may be equipped with functionalized biosensors, a counter electrode, an electronic detection system connectable to the electrodes of the viral detection chamber, and an embedded electronic processing system for processing data from the electronic detection system.

Systems and methods related to centrifuge energy harvesting chambers (CEHCs) for gas production simulation are provided. Certain CEHCs may include a high-pressure chamber, high-pressure syringe pumps, cooling systems, an actuator and surcharge, backpressure control inside the wellbore, a heating element on the wellbore, water gas separation systems, and flow measurement systems. Certain CEHCs may also provide software operably connected to sensors and instrumentation, comprising a module to continuously, in real-time, periodically, or asynchronously, measure and monitor simulation variables.

Sag propensity of a fluid can be determined by applying an oscillatory strain at an amplitude in excess of a linear region and below a yield strain of the drilling fluid. This may include use of medium amplitude oscillatory shear (MAOS), from which an elastic modulus of the fluid is determined. The elastic modulus may be determined over time, from which a time to reach maximum elastic modulus can be determined. The time to reach maximum elastic modulus is then converted or correlated to a drilling fluid sag propensity for the drilling fluid either in absolute terms or in relation to base or comparison fluids. Such an evaluation can be performed using a torsional resonance device in which the oscillatory strain is controllable so as to be maintained relatively constant during the measurement.