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Tedlar

Tedlar is a type of polyvinyl fluoride film that is widely used in various applications due to its exceptional durability, chemical resistance, and weatherability.
It is commonly employed in the construction industry, photovoltaic systems, and as a protective coating for a variety of products.
Tedlar's unique properties make it an ideal choice for outdoor applications, where it can withstand exposure to ultraviolet light, extreme temperatures, and harsh environmental conditions.
This versatile material has also found uses in the medical and electronics industries, showcasing its adaptability across multiple sectors.

Most cited protocols related to «Tedlar»

Isotopically enriched 129Xe (85%) was polarized to 10–15% by rubidium-vapor spin-exchange optical pumping (21 ) using a commercially available polarizer (Model 9800, Polarean, Inc., Durham, NC). Xenon was cryogenically accumulated and thawed into a Tedlar bag and polarization was determined using a polarization measurement station (Model 2881, Polarean, Inc.). Prior to gas inhalation, the subjects were instructed to inhale to total lung capacity and exhale to functional residual capacity twice. Subsequently, the contents of the bag were inhaled via a mouthpiece connected to the bag through a 6-mm ID Tygon tube, and the subjects held their breath for the duration of the scans (13–15 s). As explained below, to establish the correct TE for Dixon imaging, subjects first underwent a calibration scan, where they received a mixture of 400 ml of HP 129Xe and 600 ml of ultra-high-purity N2. For the subsequent gas-transfer image, subjects received a 1-L dose of HP 129Xe. The subject’s heart rate and oxygen saturation were monitored using an MR-compatible monitoring system (GE Healthcare, Helsinki Finland).
Publication 2015
ARID1A protein, human Oxygen Saturation Radionuclide Imaging Rate, Heart Rubidium Tedlar Vision Xenon
The subjects involved in the study breathed through a facemask connected to a valve of a resistance-free 1L plastic bag (Tedlar bag, SKC Ltd, Dorset, UK). One hour before sampling, eating and exercise were not allowed. The use of inhaled corticosteroids was stopped four weeks before the measurements except in 7 patients due to severe asthma symptoms. Children participated in the study were sampled randomly without division on healthy controls and children with wheezing. All samples from subjects taking part in this study were collected in the same room in order to prevent the appearance of a background bias. The plastic bags were emptied via pump with constant flow over a stainless-steel two-bed sorption tube, filled with carbograph 1TD/Carbopack X (Markes International, Llantrisant, Wales, UK) within 1 h after collection. The air-tight capped tubes were kept at room temperature until analysis (in average for three weeks). The capped tubes can be kept at room temperature up to six months without significant changes of VOCs profile. The bags were cleaned by filling and empting 2 times with nitrogen and reused for next measurements. In this study 1L of mixed breath (end-tidal and dead space air) was collected. Dead-space air comprises only a small part (30 ml) of the total sample of exhaled air collected and we have shown that the contribution of dead-space air to the total volume of whole breath does not lead to sensitivity issues in measuring VOCs by GC-tof-MS [28] (link).
The exhaled air samples were measured by means of GC-tof-MS [35] . All collected samples were measured randomly, i.e. the batch of 26 samples a random set of breath samples obtained from healthy controls and children with wheezing. The GC-tof-MS method applied here is a non-targeted GC-tof-MS method, i.e. no prior identification of the compounds was performed. All chromatographic conditions were optimized by us previously [28] (link) and consequently in consultation with the producer of our instrument and based on common chromatographic experience we chose a column and the temperature programming that were suitable to detect many different classes of volatile compounds and at the same time keep the best possible separation of the compounds at a high sensitivity and a high dynamic range. The detailed parameters of GC-tof-MS measurements are listed in Table 2.
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Publication 2014
Adrenal Cortex Hormones Asthma Child Chromatography Gas Chromatography-Mass Spectrometry Hypersensitivity Nitrogen Patients Specimen Collection Stainless Steel Tedlar
Within this study, three types of sampling bags were compared with respect to the stability of breath constituents:

3 l in volume transparent Tedlar (PVF – polyvinyl fluoride) bags (SKC Inc., USA) equipped with a single polypropylene valve (dimensions when deflated: 26 cm × 24.5 cm, film thickness: 50 μm).

3 l in volume SamplePro Flexfilm bags (unknown polymer – trade secret of SKC Inc., USA) equipped with a single polypropylene valve (dimensions when deflated: 21 cm × 41.5 cm, film thickness: 76 μm).

3 l in volume Kynar (PVDF – polyvinylidene difluoride) bags (SKC Inc., USA) equipped with a single polypropylene valve (dimensions when deflated: 26 cm × 28.5 cm, film thickness: 50.8 μm).

All bags were new and flushed five times with high-purity nitrogen (type 6.0 – 99.9999%) directly before their use.
Publication 2013
Nitrogen Polymers Polypropylenes polyvinyl fluoride polyvinylidene fluoride Tedlar

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Publication 2010
ARID1A protein, human Chromatography Electrons Gas Chromatography Gas Chromatography-Mass Spectrometry n-hexane Odorants Odors Syringes Tedlar
Samples of mixed breath gas were collected in Tedlar bags (SKC Inc, Eighty Four, PA) with parallel collection of ambient air (also in Tedlar bags). Breath gas samples were obtained after a ~5 minutes sitting of a volunteer. Each subject provided 1 or 2 breath samples by use of a straw. All samples were processed within 3-6 hours. We collected mixed alveolar breath (instead of alveolar breath) in order to find also compounds directly released from the lungs.
Before collection of breath, all bags were thoroughly cleaned to remove any residual contaminants by flushing with nitrogen gas (purity of 99.9999%), and then finally filled with nitrogen and heated at 85°C for more than 8 hours with a complete evacuation at the end.
All compounds detected in breath were compared to the ambient air and only compounds with concentrations at least 15% higher than in ambient air concentrations were reported. 18 ml of gas sample has been transferred to 20 ml volume evacuated glass vials, and equilibrated with nitrogen gas.
Here we determined VOCs in exhaled breath of lung cancer patients. We restrict ourselves to compounds which show at least 15% higher concentrations in exhaled breath as compared to inhaled air. In particular, we exclude compounds which show lower concentration in exhaled breath than in inhaled air. Our experience showed that different rooms show quite different indoor air composition, which is particularly pronounced in clinical environments. The threshold of 15% was arbitrarily chosen.
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Publication 2009
Lung Lung Cancer Nitrogen Patients Tedlar Voluntary Workers

Most recents protocols related to «Tedlar»

The changes in resistance caused by the influence of CO gas and experimental conditions were measured using a home-made dynamic gas sensing setup. The gas chamber was crafted using a glass of 8-cc volume with inlet and outlet gas ports. Additionally, the calibrated concentration of testing gas kept in Tedlar bags was utilized to inject CO gas, maintaining a flow rate of 200 sccm. A program-controlled script was run using Alicat Mass Flow Controllers (MFCs) to achieve the target concentrations, while dry air was used as reference gas for sensing measurement. The sensors were sustained under the steady flow of dry air for 5 min before the target gas with various concentrations was exposed to the sensor chip for the script duration. Chemisensing measurements were characterized using a Keithley 4200A semiconductor parameter analyzer.
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Publication 2023
DNA Chips Tedlar
Figure 1 shows a schematic diagram
of the three-stage (i) pyrolysis, (ii) catalytic steam reformer, (iii)
and water gas shift reactor system used to produce hydrogen from waste
polypropylene. The first-stage (i) pyrolysis took place in a stainless
steel reactor, 30 cm in length and 2.5 cm in diameter, and heated
externally by a temperature-controlled electrically heated furnace.
The polypropylene (1.00 g) was loaded into a stainless steel crucible,
which was held in place in the center of the pyrolysis reactor. The
pyrolysis heating regime consisted of heating the reactor from 20
to 500 °C at 20 °C min–1 and held at that
temperature for 20 min. The evolved pyrolysis hydrocarbons derived
from the thermal degradation of the polypropylene pyrolysis were passed
directly to the reforming reactor where catalytic steam reforming
took place in the presence of the 10 wt % Ni/Al2O3 catalyst (1.00 g). The reforming reactor was also constructed of
stainless steel (length 30 cm, 2.5 cm diameter) heated with a temperature-controlled
electrical furnace. The steam required for reforming was supplied
to the second-stage reactor via a water syringe pump (WPI SPLG100
syringe pump) to give a controlled input of steam. The temperature
of the second-stage (ii) reforming catalytic reactor was maintained
at 850 °C throughout the experiments.
The product gases from the second-stage (ii) reforming
reactor
were passed directly to the third-stage stainless steel (iii) water
gas shift reactor, of length 14.5 cm and 2 cm diameter, heated by
a temperature-controlled furnace. The product gases from the reforming
reactor consist of mainly hydrogen and carbon monoxide undergoing
catalytic water gas shift reaction in the presence of the metal–alumina
catalysts (0.50 g). Steam was generated from water added via a second
WPI SPLG100 syringe pump. The temperature of the water gas shift catalytic
reactor was an investigated process parameter, and temperatures between
250 and 650 °C were examined using each of the different metal–alumina
(Fe, Zn, Mn, Cu, Co) catalysts. Thermocouples monitored the temperatures
of the pyrolysis, catalytic steam reforming, and catalytic water gas
shift processes throughout the experiments. The three-stage reactor
system was continually purged with nitrogen at 100 mL min–1, producing a nominal gas residence time of 88 s in the second-stage
(ii) reforming reactor and 26 s in the third-stage (iii) water gas
shift reactor. The gases leaving the reactor system were passed through
a series of water and dry-ice-cooled glass condensers to remove condensable
products, which consisted of mostly unreacted water (condensed steam).
The final product gases were collected in a 25 L Tedlar gas sample
bag.
The experimental procedure for the operation of the three-stage
reactor system involved initially heating the (ii) second- and (iii)
third-stage catalytic reactors to the desired temperature, 850 °C
for the (ii) second stage and investigated temperatures between 250
and 650 °C for the (iii) third stage. Once the catalyst reactor
temperature had been stabilized, the pyrolysis reactor was heated
to 500 °C at 20 °C min–1 and held at that
temperature for 20 min. The heating of the first-stage (i) pyrolysis
coincided with the injection of steam into the (ii) reformer reactor
and the third-stage (iii) water gas shift reactor. The reactor system
was tested via many baseline experiments to determine repeatability
and reproducibility, and only negligible differences occurred between
experiments. Data reported here were the average of at least two repeat
experiments.
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Publication 2023
ARID1A protein, human Catalysis Dry Ice Electricity Hydrocarbons Hydrogen Metals Monoxide, Carbon Nitrogen Oxide, Aluminum Polypropylenes Pyrolysis Stainless Steel Steam Steel Syringes Tedlar
A total of 240 volunteer breath samples were collected in this experiment, including 120 diabetic samples and 120 non-diabetic samples. The volunteers' breath samples were taken in the morning when they had not eaten or exercised. Volunteers were asked to take deep breaths through a disposable suction nozzle into a 1 L Tedlar collection bag, with a one-way valve attached to the bag to prevent external air pollution. After the breath sample was collected, the collection bag was immediately sent to the electronic nose equipment for detection. The signals were processed by the electronic nose low-pass filter circuit and then collected by the data acquisition card. Finally, they were digitized and sent to the computer. The specific sample collection process is shown in Fig. 2. For each sample, we obtained a data matrix represented by 32 response curves, and each response curve had 60 s × 100 Hz = 6000 data points.

Gas sample collection process.

Publication 2023
Air Pollution Eating Specimen Collection Suction Drainage Tedlar Voluntary Workers
A 7 L lab-scale
bioreactor with a working volume of 5 L was operated semi-continuously
as an anaerobic sequencing batch reactor (ASBR) for 339 days. The
ASBR was run on a 24 h cycle through four cycles: (1) feeding (8–10
min), (2) react phase with continuous mixing and pH adjustment (22
h 40 min), (3) settling (1 h), and (4) decanting for withdrawal of
effluent equal to the volume of the influent fed (8–10 min).
The bioreactor was temperature controlled at 40 ± 0.5 °C
until Day 73 and at 37 ± 0.5 °C from Days 74 to 339. The
bioreactor pH was maintained at 5.5 ± 0.1 by the automatic addition
of 3 M NaOH with the help of LabVIEW (National Instruments, Austin,
TX). The biogas was collected in a 5 L Tedlar gas bag. Rumen content
(17.1 ± 1.0 g volatile solids (VS) L–1), obtained
from a fistulated cow from a dairy farm at Michigan State University
(East Lansing, MI), was used as an inoculum. The bioreactor was operated
at a hydraulic retention time (HRT) of 2–4 days and an organic
loading rate (OLR) of (10.5 ± 7.0 g soluble chemical oxygen demand
(sCOD) L–1 d–1). The solids retention
time (SRT) was controlled around 9.7 ± 5.8 days from Days 20
to 81 by wasting suspended biomass from the bioreactor (during the
react phase) and effluent (after the decant phase). The volatile suspended
solids concentrations in both suspended biomass and effluent were
considered for SRT calculation. Additional operational details are
described by Shrestha et al.3 (link)A mixture
of waste beer containing ethanol and permeate extracted from an acidogenic
bioreactor20 treating food waste was fed
to the ASBR once a day. The influent was prepared once a week. Waste
beer was obtained from Jolly Pumpkin Brewery (Dexter, MI), where it
represents 2–19% of the total volumetric beer production (Doug
Knox, Sustainability Manager, personal communication). The sodium
salt of 2-BES (Sigma-Aldrich, St. Louis, MO) was added to the ASBR
at the beginning of the react phase roughly every 2 weeks, the first
two times on Days 230 and 246, and every 10 days (equivalent to approximately
three HRTs) after that on Days 259, 269, 278, 287, 296, 305, and 314
to reach a bioreactor concentration of 10 mM (∼10.8 g in 5
L working volume of the bioreactor) immediately after each addition.
The 2-BES dose was selected based on literature values obtained from
anaerobic mixed-culture studies.21 (link),22 (link) The change
in 2-BES concentration over time was estimated using the initial concentration
added, the volume of effluent wasted per day, and the bioreactor working
volume. Thermodynamic calculations were performed to evaluate the
feasibility of different reactions during the period 2-BES was added
(details are given in the Supporting Information [SI]).
Publication 2023
austin BAG5 protein, human Beer Biogas Bioreactors Bos taurus Chemical Oxygen Demand Ethanol Food Pumpkins Retention (Psychology) Rumen Tedlar Therapy, Hormone Replacement
The amount of ammonia supported
on the sensor chip was measured by thermal desorption spectrometry
(TDS). The sensor chip sample was placed in a quartz glass container,
which was filled with helium gas and externally heated from 323 to
773 K. The gas released from the glass container during the temperature
increase was analyzed using a quadrupole mass spectrometer (M-101QA-TDM,
Canon-Anelva, Japan). The amount of ammonia on the sensor was evaluated
using ion currents with a mass-to-charge ratio of 17. The spectrometer
ion current was calibrated to the expected value by subtracting the
current corresponding to the fragments from water. The spectrometer
ion current was obtained at standard temperature and pressure (STP;
273 K, 1 atm). The amount of ammonia supported per unit surface area
in the pores of the porous glass was expressed by converting it into
a gas at STP.
Vanillin (0.1 g) was dissolved in 10 mL of deionized
water to prepare a 1 wt % aqueous solution, which was then mixed with
5 mL of aqueous ammonia (30 wt %, Kanto Chemical, special grade, Kanto
Chemical Co., Inc., Japan). Subsequently, the porous glass was immersed
in 20 μL of the mixed solution using a microdispenser (Dialamatic
3-000-250, Drummond Scientific, USA). The sample was then dried at
298 K for 24 h under vacuum to obtain a sensor chip. The absorption
spectrum and microstructure of the sensor chip were analyzed by UV–Vis
spectroscopy and SEM, respectively.
The nonanal-adsorbing capacity
of the porous glass was also evaluated
using 1 L atmosphere. At first, a 50-L Tedlar bag (1-2711-08, Asone,
Japan) was filled with nitrogen (Industrial Grade, Iwatani, Japan).
Subsequently, 0.125 mL of nonanal was diluted to 50 mL with ethanol;
40 μL of this solution was then placed in the Tedlar bag to
achieve a nonanal atmosphere of 0.28 ppm. Then, 1 L of atmosphere
was adjusted by subdividing 50 L of nonanal atmosphere of 0.28 ppm
as described above, and the porous glass was in a polytetrafluoroethylene
(PTFE) mesh film was hung in the 1 L Tedlar bag. After a predetermined
time (every 30 min), the sensor was removed from the Tedlar bag, and
the nonanal concentration in the bag was measured using a sensor gas
chromatograph (SGVA-P3-A, Nissha FIS Inc., Japan).
Publication 2023
Ammonia Atmosphere BAG1 protein, human DNA Chips Ethanol Fever Gas Chromatography Helium Ion Transport Nitrogen nonanal Polytetrafluoroethylene Pressure Quartz Spectrometry Tedlar Vacuum vanillin

Top products related to «Tedlar»

Sourced in United States, United Kingdom
Tedlar bags are airtight, flexible containers designed for the collection and storage of gas samples. They are made of a chemically inert polymer material that helps preserve the integrity of the sample. The bags are available in various sizes to accommodate different sampling needs.
Sourced in Panama
Tedlar bags are a type of laboratory equipment used for sample collection and storage. They are made of a durable, inert polyvinyl fluoride (PVF) material, which helps to preserve the integrity of the samples. Tedlar bags are designed to be airtight and resistant to various chemicals, making them suitable for a wide range of applications in the laboratory setting.
Sourced in United States, Germany
The GC 7890A is a gas chromatograph (GC) instrument manufactured by Agilent Technologies. It is designed to separate and analyze complex mixtures of volatile and semi-volatile organic compounds. The GC 7890A features an oven, injector, and detector, which work together to facilitate the separation and detection of the individual components in a sample.
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The Rtx-5 column is a gas chromatography (GC) column designed for the separation and analysis of a wide range of organic compounds. It features a 5% diphenyl-95% dimethyl polysiloxane stationary phase, which provides good peak shape and resolution for a variety of analytes. The Rtx-5 column is suitable for a wide range of applications, including environmental, food, and pharmaceutical analyses.
Sourced in United States, United Kingdom
The 1-L Tedlar bag is a laboratory equipment used for sample collection and storage. It is designed to hold and contain gas or liquid samples. The bag is made of Tedlar, a specialized material known for its inertness and resistance to chemical interactions, ensuring the integrity of the samples. The bag has a capacity of 1 liter and can be used for a variety of applications in laboratory settings.
Sourced in Canada
The 1 L glass bulbs are laboratory equipment used for various scientific applications. These bulbs have a capacity of 1 liter and are made of glass, providing a durable and transparent container for conducting experiments or storing materials. The core function of these bulbs is to serve as a general-purpose container for liquids, gases, or other substances in a laboratory setting.
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The HP-PLOT/Q column is a gas chromatography (GC) column designed for the separation and analysis of permanent gases and low molecular weight hydrocarbons. It features a porous polymer stationary phase that provides effective separation of these analytes. The column is suitable for a wide range of applications where the analysis of permanent gases and light hydrocarbons is required.
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Tenax TA is an adsorbent material designed for the collection and analysis of volatile organic compounds (VOCs) in air, water, and soil samples. It is a porous polymer with a high surface area, providing efficient trapping and subsequent desorption of a wide range of organic compounds.

More about "Tedlar"

Tedlar, a versatile and durable polyvinyl fluoride (PVF) film, has found widespread applications across various industries.
This exceptional material is renowned for its exceptional resistance to UV light, extreme temperatures, and harsh environmental conditions, making it an ideal choice for outdoor applications.
In the construction industry, Tedlar is commonly used as a protective coating, enhancing the longevity and weatherability of buildings and structures.
Its chemical resistance also makes it a popular choice for photovoltaic systems, where it safeguards solar panels and other components from the elements.
Beyond construction, Tedlar has found applications in the medical and electronics sectors, showcasing its adaptability across multiple industries.
Tedlar bags, for instance, are often used in the collection and storage of gas samples, ensuring sample integrity and preserving the sample's chemical composition.
These bags can be used in conjunction with analytical instruments like the GC 7890A and Rtx-5 column to facilitate reliable gas chromatography (GC) analysis.
The versatility of Tedlar extends to the field of environmental monitoring as well. 1-L Tedlar bags and 1 L glass bulbs are commonly employed for the collection and storage of air samples, which can then be analyzed using techniques like Methanol or Acetone extraction and HP-PLOT/Q column GC analysis to detect and quantify various volatile organic compounds (VOCs) and other air pollutants.
Tedlar's exceptional properties, including its durability, chemical resistance, and weatherability, have made it an indispensable material in numerous applications, from construction and renewable energy to medical and environmental analysis.
As researchers and professionals continue to explore the capabilities of this versatile film, its impact across various industries is sure to grow.