The present invention belongs to the field of methods and devices for analysing materials by determining their chemical or physical properties by the use of thermos-optical means, more precisely to the systems especially adapted for detection and quantification of carbonaceous aerosol. The invention relates to an improved heating chamber for a device for measuring carbonaceous aerosol and a device comprising the said chamber.
Carbonaceous aerosols are extremely diverse and are frequently the largest and most important fraction of fine particulate matter mass (PM2.5) (Turpin et al., 2001, doi:10.1080/02786820119445; Solomon et al., 2008, J. Air & Waste Mgmt. Assn., 58, S3-S92). They impact air quality, visibility, climate forcing, cloud nucleation, the planetary radiation balance, and public health. The carbonaceous fractions are frequently separated into organic carbon (OC) and elemental carbon (EC) based on their volatility using thermal-optical methods. Although the combined measurement of total carbon (TC) concentration is usually reliable, (Karanasiou et al., 2015, doi:10.5194/amtd-8-9649-2015), the results for the separation of OC and especially EC fractions vary significantly for different thermal analysis methods (Schmid et al., 2001, Atmos. Environ., 35, 2111-2121; tenBrink et al., 2004, doi.org/10.1016/j.atmosenv.2004.08.027; Bae et al., 2009, doi:10.1016/j.scitotenv.2009.05.035). ‘Organic’ (OC) compounds usually comprise the largest carbon-containing fraction of ambient aerosols: often more than 50% of the PM2.5 mass. A smaller fraction is categorized as Light-Absorbing Carbon (“LAC”), often described in terms of Black (“BC”) and Brown (“BrC”) Carbon (Petzold, 2013); or ‘Elemental’ Carbon (‘EC’), which is defined instrumentally by thermal analysis methods.
Accurate, continuous and high time resolved data relating to TC are needed in order to assess the severity of the problem and to identify and investigate the main sources which require attention; and to quantitate the improvements following the application of controls and regulations. Devices for measuring carbonaceous aerosol, also called Total carbon analysers (TCA), have thus been developed, however their heaters used for combustion of sampled air heat the sample slowly. Therefore, it is the aim of the present invention to provide an improved chamber with heaters for a total carbon analyser device that will quickly reach temperatures around 1000° C. needed for reliable, repeatable and complete combustion. It is further desired that the chamber is robust and suitable for use in field measurements and experiments.
Conventional thermal analysis for the ‘EC/OC’ content of aerosols gives data that is highly dependent on the thermal analysis protocol that is used: ‘NIOSH’ vs. ‘IMPROVE’ vs. ‘EUSAAR_2’. Commercially available OC/EC analysers have a quartz glass chamber, which is inert and resistant to high temperatures around 1000° C. Heating of the sample is slow, as a hot catalyst MnO2 is used for transformation of organic vapours into carbon dioxide, the quantity of which is then measured with suitable detectors, usually non-dispersive infrared detector (NDIR). One such analyser is described in patent application CN101963606 that discloses a combustion furnace for a total organic carbon automatic analyser, which comprises a glass component, a heating coil, a temperature sensor, a sample outlet, a gas outlet, a protective tube, a catalyst, a combustion furnace shell and heat-preservation cotton. The catalyst is arranged at the bottom of the glass component; the heating coil heats the sample to 900° C. under the catalysis of the catalyst; organic matters in the sample are combusted to generate carbon dioxide.
Solutions used in devices sold by companies Skalar, Eltra and Uic Inc. use different heater, where the heating wire is installed at a different location if compared to the present invention. Moreover, combustion is enabled by presence of a catalyst similarly as in commercially available OC/EC analysers. Hence, heating and consequently combustion of the analysed sample is not as efficient as in the present invention.
Patent application US 2019/277819 discloses a device for measuring particulate carbon in real time, wherein the heating chamber has two separate filters on which air samples are collected. Each filter is provided with a heater located below the filter in the direction of air flow in order to heat the filter and consequently the sample, so that organic matter is transformed into CO2, which can be detected with a CO2 detector. The chamber is also provided with a catalyst, which increases combustion efficiency. This construction differs from the present invention and it is questionable whether such position of the filters, heaters and catalysts can prevent condensation of organic vapour on the walls prior to reaching the CO2 detector.
The essence of the improved chamber for an instrument for measuring carbonaceous aerosol is in that the airtight chamber comprises two heaters encasing a filter, wherein the chamber and the heaters are made of stainless steel, wherein the heaters are controlled by suitable electronics. Stainless steel is inert as the commercially available quartz chambers, but does not release any carbon at high temperatures, which could affect the measurements. Further, stainless steel is more robust than the fragile quartz glass, thus making the chamber resistant to impacts and suitable for field measurements and experiments. Both heaters comprise a housing and a heating wire, both made of material that does not release carbon upon heating, the preferred option being stainless steel. The material from which the heating wire is made should enable fast heating and should endure frequent heating and cooling. A preferred choice for the heating wire is material APM produced and sold by the company Kanthal. APM is an advanced powder-metallurgical, dispersion-strengthened, ferritic iron-chromium-aluminium alloy (FeCrAl alloy) for use at temperatures up to 1425° C. The alloy is characterized by excellent stability and oxidation resistance, has low tendency to ageing and low resistance change. Any material similar to the APM is suitable to be used for the heating wire of the heaters in the chamber according to the invention. The filter used in the chamber is preferably a quartz fibre filter. Suitable filters are all filter stable at temperatures up to 1100° C. It would also be possible to use steel mesh filters with suitably small pores, however their collection efficiency is lower than with quartz filters. One of the said heaters is placed above the filter, while the other heater is placed below the filter, wherein the distance of the heaters from the filter is from 1 to 10 mm, preferably 1 to 5 mm. Such placement of heaters allows uniform and fast heating of the filter with the sample, which leads to efficient combustion of organic vapour into CO2. The filter reaches its final temperature around 940° C. in approximately 10 seconds. The chamber is preferably equipped with a temperature sensor for measuring temperature below the filter, wherein the said sensor is usually placed in the lower part of the chamber. When the organic vapours evaporate from the filter, they reach the heating wires with temperatures around 900° C. almost immediately, meaning that they do not condense on the walls of the chamber before combustion. In case the organic vapours condense on the walls, they become unavailable for detection with a suitable CO2 sensor such as an NDIR sensor.
The stainless-steel chamber comprises at least the following:
The preferred embodiment of each heater comprises the steel housing also serving as the holder of the filter, wherein the following components are housed within the housing:
Said heaters are controlled by electronics, the main component of the latter being a voltage driver, one for each of the heaters. The voltage driver through suitable contact and ceramic pins regulates the voltage on the heating wire with 0.1 V precision, wherein the power of the heaters is measured with a voltage clamp. Said electronics are used to control operation of the heaters, wherein the lower heater is preferably turned on before the upper heater. As the sampled air travels downwards, the lower heater is turned on, thereby allowing the organic vapour to pass through an already hot heater, consequently turning them to CO2. This allows efficient combustion and also enables abandonment of catalysts in the chamber. In case the upper heater would be turned on first, a portion of the organic vapour could escape through the lower heater having a temperature lower than required; hence this portion of vapour could not be detected with the CO2 sensor. The heaters and consequently the filter heat to temperatures up to 1000° C., wherein the chamber itself heats to temperatures up to 300° C.
The chamber according to the invention is suitable for use in a device for quantification of carbonaceous aerosols, such as a Total Carbon Analyzer (TCA) instrument that uses a thermal method for total carbon (TC) determination. The TCA comprises at least one, preferably two parallel flow channels with two sampling-analytical heating chambers according to the invention, which alternate between sample collection and thermal analysis. While one channel is collecting its sample for the next time-base period, the other channel is analysing the sample collected during the previous period. This sequential feature offers the great advantage of a continuous measurement of TC. The sampling time may be pre-set from 20 minutes to 24 hours. At the end of the collection period, the sample flow is switched from one channel to the other.
The method of operation of the device with the chamber according to the invention comprises the following steps:
A preferred embodiment of the step b) in the method of operation of the device with the chamber according to the invention is as follows:
Step iii) may also be performed immediately after step i) or at the same time as step ii).
Even more preferred embodiment repeats the above sequence of steps i) to vi). Such heating has an advantage that artefacts such as increased concentration of CO2 as a result of an NDIR detector artifact due to rapid change in the air temperature in the chamber are eliminated. The amount of CO2 attributed to the carbonaceous aerosols collected on the filter is thus calculated as:
CO2(Carbonaceous Aerosols)=CO2(first heating cycle)−CO2(second heating cycle).
The device with the chamber according to the invention can be used in online mode for continuous, real-time analysis and offline mode to analyse previously-collected samples. In case the device is linked to another device for measurement of black carbon (BC) such as Aethalometer AE33 (Aerosol, Slovenia), OC can be calculated as OC=TC (measured by the device)−EC (i.e. BC measured by AE33).
In the sequence of steps the CO2 signal increases in the first heating cycle, wherein CO2 signal could also be present in the second cycle. C5 and C10 cycle stages are longer as the heaters take longer to cool than to heat to the required temperature.
The filter reaches its final temperature around 940° C. in approximately 10 seconds, wherein the temperature rise is shown in
The newly developed chamber and the device for measuring carbonaceous aerosols according to the invention enables measurement of the concentrations of total aerosol carbon continuously with high time resolution as rapid as 20 min. Two parallel flow channels provided with the improved chamber allow continuous operation: while one channel analyzes, the other collects the next sample. Thermal analysis by flash-heating of the sample collected on a quartz fiber filter inside the chamber efficiently converts all the particulate carbon to CO2. The increase in CO2 concentration above baseline in a flow of analytic air is measured by an integrated NDIR detector. When the device according to the invention is combined with an AE33 Aethalometer, the TC-BC method yields OC-EC data with much greater time resolution than that offered by the analysis of offline filter-based samples.
Number | Date | Country | Kind |
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19213028.4 | Dec 2019 | EP | regional |