Siloxane compounds have been measured using Fourier Transform Infrared (FTIR) spectroscopy, as discussed by Phillips et al., “Method and Apparatus for Siloxane Measurements in a Biogas”, U.S. Pat. No. 8,462,347 B2. However, one disadvantage of this detection technique is that, since there is no separation of the gaseous components, all of the gaseous constituents have to be measured simultaneously by FTIR. This leads to significant errors due to background absorption of unwanted species, such as methane, CO2, ethane and propane. In addition, since the various siloxane species have very similar infrared (IR) absorption features, it is impossible to effectively analyze each component separately via classical least squares and present a valid analytical number for each.
Phillips et al. proposed a surrogate analysis technique, where classes of siloxanes (linear or ring structures) were characterized by one or two members of each class. Even so, the detection limit was only about 200 parts-per-billion (ppb) due to signal-to-background limitations from imperfect fitting of the classical least squared spectral signatures of the background gases.
A need exists, therefore, for improved techniques that address and solve problems associated with existing approaches. In particular, a need exists for identifying and quantifying siloxane species in gaseous streams.
In general, aspects of the invention feature a method and system for detecting siloxanes using thermal desorption tubes and FTIR spectrometers with possibly intervening gas chromatography systems.
In one embodiment, for example, a method for detecting siloxanes comprises: collecting a sample in a thermal desorption tube; desorbing siloxanes from the thermal desorption tube; optionally separating the siloxanes by gas chromatography; and analyzing the desorbed siloxanes or the siloxanes separated by gas chromatography with a Fourier Transform Infrared Spectrometry system.
In another embodiment, a system for detecting siloxanes includes: a thermal desorption tube connected to a gas stream that contains siloxanes; a gas chromatography system for separating siloxanes desorbed from the thermal desorption tube; and a Fourier Transform Infrared Spectrometry system for identifying and quantifying the siloxanes separated by the gas chromatography system.
The above and other features of the invention including various novel details of construction and combinations of parts, and other advantages, will now be more particularly described with reference to the accompanying drawings and pointed out in the claims. It will be understood that the particular method and device embodying the invention are shown by way of illustration and not as a limitation of the invention. The principles and features of this invention may be employed in various and numerous embodiments without departing from the scope of the invention.
In the accompanying drawings, reference characters refer to the same parts throughout the different views. The drawings are not necessarily to scale; emphasis has instead been placed upon illustrating the principles of the invention. Of the drawings:
Embodiments of the present invention are designed to analyze a siloxane-containing sample by pre-concentrating the sample via sorption and thermal desorption, optionally separating the components in the desorbed sample via gas chromatography, and detecting individual siloxane components via FTIR. The siloxane-containing sample can be obtained from a gaseous stream by a sampling pump or other suitable means. In general, siloxanes are thought of as compounds having a molecular structure based on a chain of alternate silicon and oxygen atoms, having, for example, organic groups attached to the silicon atoms. Linear or cyclic, siloxanes often are present as an impurity in industrial or other fluid streams.
In specific aspects of the present invention, a gas chromatograph (GC) is used to separate a sample containing one or more siloxane compounds into different components, and Fourier Transform Infrared (FTIR) spectrometry is used for detecting the individual components. The GC/FTIR process and system have been discussed in detail by Spartz et al., “Process and System for Rapid Sample Analysis”, in US published patent application, US2015/0260695 A1, now U.S. Pat. No. 9,606,088, issued Mar. 28, 2017, both of which are incorporated herein by this reference in their entirety. The on-site monitoring of siloxanes has also been described in “On-site Monitoring of Siloxanes in Wastewater Digester and Landfill Gas”, MAX Technology Application Note 704, from Prism Analytical Technologies, Inc., May 2015.
In many cases, the FTIR system includes a sample or gas cell, provided, for example, with windows made of BaF2, CaF2, or another suitable material. The cell can be configured for multiple-path (also known as multiple-pass or long path) absorption. By increasing the path length traveled, multiple-pass arrangements can be used to measure low concentration components or to observe weak absorption spectral features without increasing the physical length or volume of the cell itself. Since the detection limit of the system is directly related to the volume/path length ratio, decreasing the volume or increasing the path length lowers the concentrations that can be detected. Assuming no signal losses, doubling the path length or reducing the volume in half will lower the detection limit by a factor of 2.
In certain embodiments, longer path lengths are used in combination with higher reflective coatings like enhanced silver, yielding a reflectivity in the 0.992 to 0.995 range or greater. Coating optimizations, in the IR region, for example, could further improve reflectivity. This allows for pathlengths that are longer by a factor or 4 to 8 or even more.
In specific implementations, the sample cell is configured as a “White cell” type. The principles of a traditional White cell arrangement employ three spherical concave mirrors having the same radius of curvature. These principles can be modified, to improve image quality and optical throughput, as described, for instance, by Spartz et al. in U.S. Patent Application Publication No. 2015/0260695 A1 (now U.S. Pat. No. 9,606,088). In one example, the White cell type employed uses non-spherical concave mirrors cut onto a single metal or a glass blank, providing a fixed path length; the mirrors can be the solid end caps of the sample cell, allowing for smaller sample cells that are easier to align.
Other multiple pass cell designs that can be utilized include but are not limited to Herriott cells, Pfund cells, cavity-ring down cells, and integrating spheres.
In other embodiments, a lightpipe flow sample cell is used.
A gaseous sample from a source 110 is introduced (e.g., impelled) into the TDT 102, where the constituents are adsorbed onto the sorption media and held for a period of time (the sampling time). During this sampling time, the concentrations of individual components build up as more gas is passed over the sorption media. After the sampling is ended, the TDT 102 is sealed with the adsorbed sample inside.
To analyze the individual components by GC/FTIR, a fast thermal ramp is applied to the sorption media in the TDT 102 to release the adsorbed contents. These contents are introduced into the GC 104, where they are chromatographically separated in a GC column. The separated components exit the GC 104 and are directed to the sample cell 108 for detection by the FTIR spectrometer 106. Using the algorithmic technique described in Spartz et al., “Process and System for Rapid Sample Analysis”, US2015/0260695 A1, now U.S. Pat. No. 9,606,088, each individual siloxane component can be identified and quantified using FTIR.
This technique can be applied to measuring siloxanes in biogas streams, such that wastewater and landfill operators can get near-real time concentration profiles of siloxanes which may be coming through their filter media. This will allow the filter process to be stopped, saving any unwanted siloxanes from being burnt in the cogeneration engines or turbines, which could destroy either by abrasion of moving parts from the resultant silicates (“sand”). The detection of siloxanes is critical to the wastewater and landfill biogas operations, since excess siloxanes that are burnt during the combustion process to generate electricity through either reciprocation internal combustion engines (RICE) or microturbines can easily penetrate the pistons, bearings and oils used in these machines and abrade these parts, causing irreparable harm and requiring complete overhaul—leading to downtime. Examples of siloxanes that can be encountered in biogas streams include but are not limited to: hexamethyldisiloxane (L2); octamethyltrisiloxane (L3); decamethyltetrasiloxane (L4); hexamethylcyclotrisiloxane (D3); octamethylcyclotetrasiloxane (D4); decamethylcyclopentasiloxane (D5); dodecamethylcyclohexasiloxane (D6).
When a collected sample is ready for analysis, desorption was carried out by unsealing a TDT, and flowing a room temperature stream of nitrogen through the TDT to remove any bulk gases, such as CO2, CH4 and adsorbed water. Although other inert gases can be used as a purge gas, the use of nitrogen is more convenient and less costly than other inert gases such as argon or helium, among others. For example, the TDT can be purged with nitrogen at a flow rate range of about 10 mL/min to 200 mL/min and a temperature range of about 20° C. to 40° C. for a time period sufficient to remove most adsorbed species that may interfere with the separation and/or detection of siloxanes. In one example, a flow rate of about 100 mL/min at a temperature of about 25° C. for 5 min is typically used.
The temperature of the TDT was then raised to over 200° C., preferably about 280° C., to flash desorb the contents off the TDT and onto the GC column.
Various factors have to be considered in determining a suitable temperature ramp (or heating rate) for desorbing the siloxanes from the TDT into the GC. If the temperature ramp is too slow, the chromatographic separation is not as efficient because there will not be a sharp release of the materials into the GC column. As an example, a 35° C. to 280° C. ramp can be applied to the TDT from about 1 to 3 minutes in duration (corresponding to a range of about 245° C./min to 85° C./min). Furthermore, the final temperature level can be used as another parameter for optimizing the process for siloxanes separation and detection. For example, temperature ramping has been investigated at a final temperature range from about 230° C. to 280° C., and a nominal final temperature of about 260° C. Prior to applying the temperature ramp, however, water should be purged effectively from the TDT, so that water background in the GC can be minimized, while still providing reasonable chromatographic resolution.
The GC column was a standard MTX624 30 meter column that was temperature ramped from 35° C. to 250° C. for a period of about 50 minutes at a flow rate of approximately 2 mL/min. This was sufficient to separate the siloxanes into individual species. The MTX624 column is commercially available from Restek Corporation, Bellefonte, Pa., USA. Other 624-type of GC columns with an appropriate stationary phase (e.g., from other suppliers) can also be used.
The separated siloxanes were directed from the exit of the GC 104 to the sample cell 108 for detection by the FTIR spectrometer 106. IR absorption bands were monitored in the region from about 750 cm−1 to 1300 cm−1, which covers the Si—O stretches for the siloxanes.
Since this GC/FTIR technique chromatographically separates and individually analyzes each siloxane separated from the background, the detection limits are about 100 times better than conventional techniques. In addition, there is no need for surrogate methods of analysis to be used as in previous known techniques such as that discussed in Phillips et al., U.S. Pat. No. 8,462,347 B2. Instead, each siloxane can be characterized completely by itself.
The method of the present invention can also be used for monitoring or measuring siloxane levels in other applications or environments, e.g., during a lithographic laser ablation process for semiconductor manufacturing. For photolithographic tools in a semiconductor FAB (fabrication facility or cleanroom), extremely deep UV lasers are used to photo-etch microscopically small channels on the photoresist applied to silicon wafers. These channels will act as wires and electron transports in the chip being formed. Since the laser wavelengths used are almost ubiquitously absorbed by any material, extremely pure quartz lenses are used to focus the laser beam onto the photomasks. If any contaminant adsorbs onto the lens, it can be photo-burnt onto the lens, rendering the lens useless. The most common contaminant are siloxanes, which can emanate from silicone rubber materials (commonly used as thermal and electrical insulators) within the FAB.
If siloxanes enter into this laser ablation process, they could coat the precision lens materials and be ablated onto the surface of these lenses, destroying them and costing the manufacturer tens of millions of dollars. The method of the present invention is well-suited for monitoring or detection of siloxanes to avoid potential contaminations in the lithographic laser ablation process environment.
The gaseous components from the TDT are then introduced into a GC for separating into different components, as illustrated in step 208. In step 210, one of the separated components from the GC is allowed to enter a previously-evacuated sample cell, and allowed to accumulate for a certain time period. In step 212, the component collected in the sample cell after the given time period is subjected to FTIR detection and analysis. By increasing the amount of the component in the cell before performing FTIR, the absorption signal for the component can be improved (compared to using a flow cell configuration). Steps 210 and 212 are repeated for each of the GC-separated components, as appropriate.
Other details of the apparatus and method for sample analyzing using GC/FTIR can be found in Spartz et al., US published patent application US2015/0260695 A1 and U.S. Pat. No. 9,606,088.
Aspects of the invention are further illustrated in the following non-limiting example.
Samples of pre- and post-filtered biogas were acquired from a wastewater treatment facility. Adsorption tubes were exposed for 5 minute to each stream at a flow rate of about 150 mL/min, or an equivalent volume of 0.75 L. The tube's contents were processed and introduced into a MAX™ analyzer, insuring that the light hydrocarbons, CO2 and H2O would be flushed before they could reach the column. The column was operated and the GC separation was spectroscopically analyzed by the FTIR. A representative “chromatogram” and its associated infrared spectrum (
While this invention has been particularly shown and described with references to preferred embodiments thereof, it will be understood by those skilled in the art that various changes in form and details may be made therein without departing from the scope of the invention encompassed by the appended claims.
This application is a § 371 National Phase Application of International Application No, PCT/US2017/026631, filed on Apr. 7, 2017, which claims the benefit under 35 USC 119(e) of U.S. Provisional Application No. 62/319,925, filed on Apr. 8, 2016, both of which are incorporated herein by reference in their entirety.
Filing Document | Filing Date | Country | Kind |
---|---|---|---|
PCT/US2017/026631 | 4/7/2017 | WO | 00 |
Publishing Document | Publishing Date | Country | Kind |
---|---|---|---|
WO2017/177154 | 10/12/2017 | WO | A |
Number | Name | Date | Kind |
---|---|---|---|
3287557 | Bartz | Nov 1966 | A |
4183670 | Russell | Jan 1980 | A |
4538910 | Doyle | Sep 1985 | A |
5200543 | Inomata | Apr 1993 | A |
5341207 | Tank | Aug 1994 | A |
5440143 | Carangelo | Aug 1995 | A |
5457316 | Cohen | Oct 1995 | A |
5479815 | White | Jan 1996 | A |
5541728 | Dierking | Jul 1996 | A |
5720798 | Nickerson | Feb 1998 | A |
5777735 | Reagen | Jul 1998 | A |
7092077 | Kishkovich | Aug 2006 | B2 |
7552617 | Danilchik | Jun 2009 | B2 |
8462347 | Phillips et al. | Jun 2013 | B2 |
9606088 | Spartz et al. | Mar 2017 | B2 |
20030184733 | Kameoka | Oct 2003 | A1 |
20030222413 | Hatanaka | Dec 2003 | A1 |
20060066824 | Knappe | Mar 2006 | A1 |
20060137432 | Kin | Jun 2006 | A1 |
20060225571 | Higgins | Oct 2006 | A1 |
20070182965 | Kamlet | Aug 2007 | A1 |
20070242275 | Spartz | Oct 2007 | A1 |
20100107731 | Kippeny | May 2010 | A1 |
20100223015 | Phillips | Sep 2010 | A1 |
20100307335 | Hayward | Dec 2010 | A1 |
20110171447 | Krishnamoorthy | Jul 2011 | A1 |
20120108450 | Jaworski | May 2012 | A1 |
20130193325 | Phillips | Aug 2013 | A1 |
20130256583 | Schlenoff | Oct 2013 | A1 |
20140318217 | Li | Oct 2014 | A1 |
20150209717 | Ballantyne | Jul 2015 | A1 |
20150260695 | Spartz et al. | Sep 2015 | A1 |
20160206990 | Bossan | Jul 2016 | A1 |
20170122888 | Heckner | May 2017 | A1 |
20170226437 | Jurng | Aug 2017 | A1 |
20170299559 | Wyatt | Oct 2017 | A1 |
20170341056 | Spartz | Nov 2017 | A1 |
20180045693 | Wyatt | Feb 2018 | A1 |
20180045694 | Wyatt | Feb 2018 | A1 |
20180180579 | Spartz | Jun 2018 | A1 |
20180250896 | Matsumoto | Sep 2018 | A1 |
20180252639 | Spartz | Sep 2018 | A1 |
20190064127 | McPartland | Feb 2019 | A1 |
20190064131 | Wyatt | Feb 2019 | A1 |
20190265205 | Spartz | Aug 2019 | A1 |
Entry |
---|
McGoldrick et. al., Concentrations and trophic magnification of cyclic siloxanes in aquatic biota from the Western Basin of Lake Erie, Canada, Environmental Pollution 186 (2014), 141-148 (Year: 2014). |
Gallego, E. et al., “Development of a method for determination of VOCs (including methylsiloxanes) in biogas by TD-GC/MS analysis using Supel™ Inert Film bags and multisorbent bed tubes,” Intern. J. Environ. Anal. Chem., 95(4):291-311 (2015). |
International Search Report and Written Opinion of the International Searching Authority, dated Jul. 5, 2017, from International Application No. PCT/US2017/026631, filed on Apr. 7, 2017. 17 pages. |
International Preliminary Report on Patentability of the International Searching Authority, dated Oct. 18, 2018, from International Application No. PCT/US2017/026631, filed on Apr. 7, 2017. 9 pages. |
Kim, K-H et al., “Conditions for the optimal analysis of volatile organic compounds in air with sorbent tube sampling and liquid standard calibration: demonstratin of solvent effect,” Anal Bioanal Chem 405:8397-8408 (2013). |
“On-site Monitoring of Siloxanes in Wastewater Digester and Landfill Gas”, MAX Technology Application Note 704, from Prism Analytical Technologies, Inc., May 2015. |
Number | Date | Country | |
---|---|---|---|
20190137460 A1 | May 2019 | US |
Number | Date | Country | |
---|---|---|---|
62319925 | Apr 2016 | US |