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Tenax ta

Manufactured by Markes International
Sourced in United Kingdom

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.

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15 protocols using tenax ta

1

Comparative Evaluation of Sorbent Packing

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To compare the ST adsorption capacities of the seven phthalates, three types of sorbent packing (QW, GW, and QWTN) were prepared and tested for comparative purposes. Note that for this test, QW and GW were selected for their considerably good sorption capacity for SVOCs like PAHs23 (link). QWTN tubes were also included, as they have been used widely in many previous studies for the collection of SVOCs including phthalates2 9 (link)10 24 (link). To prepare the three types of STs, an empty quartz tube (6.35 mm × 90 mm) was packed individually, containing: (1) 10 mg of QW (Grace, IL, USA), (2) 10 mg of GW (Supelco, PA, USA), and (3) 50 mg of Tenax TA (35–60 mesh, Markes International, UK) and 10 mg of QW (5 mg each at the initial and end of the Tenax TA). After the preparation, all STs were cleaned by supplying pure N2 gas at 100 mL min−1 at 320 °C for 24 h.
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2

Breath Sampling for Postpartum Analysis

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Breath sampling was performed at 3 months after childbirth (follow-up visit 4) following the protocol described by Sola Martínez et al.40 (link). Briefly, exhaled breath was collected in 1 L Tedlar gas sampling bags. Specifically, mixed breath sample (alveolar and dead space) were collected. Then, the exhaled breath contained in the gas sampling bags was immediately transferred to to thermal desorption tubes (Tenax TA, Markes International) to avoid the diffusion through the bag wall. A room air content sample was also collected directly through Tenax tube for each exhaled breath sample using an Easy-VOC syringe (Markes International) to control for environmental conditions at sampling. Almost all samples were analysed on the same day of collection, being a maximum storage period of less than one week. The Tenax tubes were stored at 4 °C for storage periods longer than one day. Tenax tubes were heated to 335ºC for 25 min for reconditioning after each use. The Tedlar bags were cleaned with 10 nitrogen flushes (99.9% nitrogen purity) before use. Thus, the levels of background artefacts (N,N-dimethylacetamide and phenol) in the gas sampling bags were strongly reduced (Supplementary Fig. S12).
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3

Bacterial Volatile Organic Compound Analysis

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Next to the inhibition experiments, bacterial volatiles emitted in monocultures and pairwise combinations were trapped and analyzed. For trapping of VOCs emitted by bacteria a volume of 100 μl of inoculation suspension was spread on 1/10th TSBA (20 mL) in glass Petri dishes designed for headspace volatile trapping (Garbeva et al., 2014b (link)). The Petri dishes were closed by a lid with an outlet connected to a steel trap containing 150 mg Tenax TA and 150 mg Carbopack B (Markes International, Ltd., Llantrisant, UK; Supplementary Figure S1). All treatments were inoculated in triplicate. The volatiles were collected after 48 and 72 h of incubation and the Tenax steel traps were stored at 4°C until GC-Q-TOF analysis.
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4

Profiling Symbiodiniaceae BVOCs

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Biogenic volatile organic compounds (BVOCs) were sampled from live cultures of Symbiodiniaceae as per [44 (link)]. Sample aliquots of 50 mL were sealed in sterile crimp cap vials (100 mL) and maintained under matching growth conditions during sampling. Technical duplicates were collected from each biological replicate (n = 6). BVOCs were collected by purging each vial for 15 min with instrument-grade air at 100 mL/min (BOC Gases, Linde Group, North Ryde, NSW, Australia). The outlet of this purge passed through thermal desorption (TD) tubes (200 mg Tenax TA; Markes International Ltd., Llantrisant, UK). Immediately following sample purging, TD tubes were capped and stored at 4 °C until analysis. Water blanks (n = 6) consisting of culture medium (autoclaved and filter sterilised (0.22 µm) artificial seawater (ASW) and F/2 media) were also run to capture any background BVOCs.
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5

Volatile Organic Compound Analysis Protocol

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For analysis of volatile organic compounds, glass Petri dishes were used (Garbeva et al., 2014a). The Petri dishes were closed by a lid with an outlet connected to a steel trap containing 150 mg Tenax TA and 150 mg Carbopack B (Markes International, Llantrisant, UK). The Tenax steel traps were collected after 72 h of incubation and stored at 4°C until GC‐Q‐TOF analysis. As controls glass Petri dishes containing 1/10th TSBA media without inoculated bacteria were used.
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6

Volatile Compound Extraction Protocol

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Samples were thawed overnight in the fridge (−4 °C). For each time point, 20 mL of each replica was transferred to a 100 mL gas washing flask and closed with a purge head. The samples were equilibrated to 37 °C in a circulating water bath and then purged with nitrogen (150 mL/min) for 60 min under magnetic stirring (200 rpm). The volatile compounds were collected on traps containing 200 mg of Tenax-TA with mesh size 60/80 (Markes International, Llantrisant, UK). Water was removed from the traps by dry-purging with nitrogen (100 mL/min) for 20 min.
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7

Volatile Organic Compound Sampling from Decomposing Cadaver

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VOC samples were collected from the headspace of the decomposing cadaver by placing an aluminum hood measuring 800 mm (H) x 1900 mm (L) x 1200 mm (W) over the donor. VOCs were allowed to accumulate for 15 min before being drawn into sorbent tubes (n = 3 per sampling event), packed with Carbograph 5TD and Tenax TA (Markes International Ltd., Llantrisant, UK), for 10 min at 100 mL/min using an ACTI-VOCTM low-flow sampling pump (Markes International Ltd., Australia). The sorbent tubes were attached to the sampling hood via a brass Swagelok fitting (Swagelok Company, Caringbah, Australia). Each tube was then wrapped in aluminum foil and transported to the laboratory for analysis in glass jars. Prior to sample analysis, each sorbent tube was injected with an internal standard of 0.2 μL of 10 ppm bromobenzene (CAS#: 108-86-1, HPLC grade, Sigma-Aldrich, Castle HIL, Australia) diluted in methanol (HPLC grade, Sigma-Aldrich, Australia) using an eVol XR hand-held automated analytical syringe (SGE Analytical Science, Sydney, Australia).
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8

Breath Sampling for Volatile Analysis

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Details on the sample collection and storage method have been previously described.8 The participants were asked to breathe into a 3L Tedlar® bag (SKC Inc. 231-03). The exhaled breath (3L) in the Tedlar® bag was immediately pumped onto an adsorbent thermal desorption (TD) tube (Tenax® TA and Carbograph-1TD; Markes International, C2AAXX-5032) which was capped immediately with brass storage caps (Markes International, C-CF010) A 0.5L environmental air sample was collected at a flow of 500 mL min−1 directly onto a TD tube using an ESCORT ELF® (Zefon International, 805558) pump adjacent to the participants.
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9

Volatilome Trapping of Nest Microbiome

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The volatilomes of the five nest microbiome members were trapped. The strains were prepared as described above (chapter 2.2.) and preincubated for 3-5 days. The trapping was performed for 24 h using steel traps filled with 300 mg Tenax TA (Markes International, Llantrisant, United Kingdom) connected to special Petri dishes (based on Garbeva et al. 2014) . Sterile media were used as controls. The procedure was replicated six times.
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10

Headspace Sampling of Carrion VOCs

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Prior to VOC sample collection, a stainless steel hood was placed over the carrion or control sites and the headspace (gas phase) was allowed to accumulate within the hood for 15 min. A sorbent tube containing Tenax TA and Carbograph 5TD (Markes International Ltd., UK) was connected to the hood via a Swagelok bulkhead connector and the headspace drawn onto the tube at a rate of 100 mL/min for 10 min using an ACTI-VOC low flow sampling pump (Markes International Ltd., UK) (see [34] (link) for diagram of experimental design). The tubes were sealed with brass storage caps, wrapped in foil, and placed in an airtight glass container for transport to the laboratory. Two field blank samples were also collected; one prior to the first sample collection and one at the completion of sample collection on each sampling day, to monitor the natural change in the atmospheric VOC profile at the site. Field blank tubes were transported and stored with sample tubes to account for any contamination and artifacts.
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