A measuring method of bromate ion concentration includes a first fluorescence intensity measuring process including a process of passing hydrochloric acid through an anion exchanger to elute bromate ions adsorbed to the anion exchanger into the hydrochloric acid and a process of measuring the fluorescence intensity of the hydrochloric acid passed through the anion exchanger, a second fluorescence intensity measuring process including a process of passing a hydrochloric acid solution containing a fluorescent substance whose fluorescence intensity changes due to coexistence of bromate ions through an anion exchanger to elute bromate ions adsorbed to the anion exchanger into the hydrochloric acid solution and a process of measuring the fluorescence intensity of the hydrochloric acid solution passed through the anion exchanger, and a calculation process determining the bromate ion concentration in the water sample by using the difference between the fluorescence intensities of the hydrochloric acid solution and the hydrochloric acid.

The present invention discloses a method for measuring the concentration of a photoresist in a stripping liquid. In the method for measuring the concentration of a photoresist in a stripping liquid, a plurality of standard photoresist samples are prepared at first, then the spectrum of the standard photoresist samples and the spectrum of the test photoresist sample are collected, and the nth derivative of the spectrum of the standard photoresist samples and the spectrum of the test photoresist sample are taken, wherein n is an integer equal to or greater than 1, a standard curve based on the nth derivative curves and calculating the concentration of the test photoresist sample is established, the concentration of a photoresist in a stripping liquid can be measured accurately according to the standard curve.

A method is provided of using morphologically specific free-floating structures as Standards in the pharmaceutical industry to test objects in drug containers. These structures are micropatterned according to a desired pattern. A container is filled with a defined number of the standards, which then can be used as a standard reference for testing other drug products held in a drug container. The testing pertains to optically identifying structures in the drug container that can be similar in size and shape as the standards, or that can be different in size and shape as the standards. The advantage of the method is that imaging systems with tracking algorithms that count and track sub-visible and visible particles in solution can be used to identify e.g. glass flakes and other foreign particles by comparing them to the shape and size of the standard reference particles.

The present invention relates to a method for monitoring a control parameter of a polymerization reaction mixture in heterogeneous phase comprising the following steps: (a) acquiring at least one NIR reflectance spectrum of said mixture; (b) calculating a value of said control parameter by means of a calibration curve which correlates the NIR reflectance spectrum with the values of said control parameter measured with a reference measurement method. The present invention also relates to an apparatus for implementing said method.

The invention discloses a calibration attachment for adjustment, calibration and/or for carrying out a functional check of an optical sensor, which is configured for measuring at least one measurement variable in a medium using light. The sensor is configured for emitting emission light of at least a wavelength in the range of 200-450 nm, comprising a housing and a body arranged in the housing wherein the body comprises praseodymium, and after excitation with the emission light, the body emits light with a longer wavelength. The invention also discloses a sensor arrangement comprising such a calibration attachment, and a use of same.

An oxygen number density or concentration sensor including a sampling luminescent oxygen probe located in a fluid environment, and a gas impermeable enclosure located in the fluid environment and a reference luminescent oxygen probe located within the gas impermeable enclosure, wherein the sampling and reference luminescent oxygen probes are formed by an ideal PSP. A predetermined fixed oxygen number density or concentration is provided within a medium contained in the gas impermeable enclosure. A detector receives signals corresponding to luminescent emissions of the sampling and reference probes. A processor determines a number density or concentration of oxygen in the fluid environment from a signal generated at the sampling probe with reference to an oxygen number density or concentration dependent signal generated at the reference probe.

A borescope calibration device is provided that includes a base having a planar surface and a plurality of reference surfaces on a side of the base opposing the planar surface, each of the plurality of reference surfaces having a height that decreases along a length of the base, a fixture that positions an optical head along a reference line that is parallel to the planar surface and providing a fixed distance between the reference surfaces and the optical head, the fixture being movable along a length of the base, and a target pattern formed on each of the reference surfaces.

A method is used for selecting a boundary sample. The method includes acquiring a deterioration trend of a new device by performing a deterioration acceleration treatment to the new device, acquiring deterioration trends of a plurality of repaired devices which have been repaired after long-term use by performing a deterioration acceleration treatment to the plurality of repaired devices, calculating an upper limit of deterioration of the repaired device based on the deterioration trend of the new device, and selecting a boundary sample indicating a limit state in which the device can be reused as a standard of reuse of the device by specifying a repaired device having the largest deterioration among the repaired devices having a deterioration not larger than the upper limit.

The present inventive concept relates to a method (100) for identifying a set of candidate substances of a sample (10) using a Raman spectroscopy device (200). The method (100) comprises recording (120) a Raman spectrum using an exposure time, and recording (162) a further Raman spectrum using a further exposure time. The further Raman spectrum may exhibit Raman peaks not recorded/detected in the Raman spectrum which possibly reduces the set of candidate substances. If necessary, one or more additional Raman spectra are recorded to further reduce the set of candidate substances, such that a single candidate substance eventually remains, thereby deemed to be a substance of the sample (10). A Raman spectroscopy device (200), a computer program and a non-transitory computer-readable storage medium are also provided

Provided herein are techniques for improved optical absorption measurements in the presence of time-varying etalons. In one aspect, a method for dynamic etalon fitting for adaptive background noise reduction in an optical sensor is provided. The method includes the steps of: obtaining a zero-gas spectrum measured using the optical sensor; obtaining an analyte gas spectrum of a target trace gas measured using the optical sensor; comparing the zero-gas spectrum and the analyte gas spectrum using fit parameters that compensate for drifting etalons in the optical sensor; and dynamically extracting the drifting etalons from the analyte gas spectrum to retrieve concentration of the target trace gas.