🎤Francis Femi OloyIn this episode of Concentrating on Chromatography, David speaks with Francis Femi Oloy about using chromatography to uncover hidden pollutants in real-world water systems.Femi’s team analyzed polychlorinated biphenyls (PCBs) in six major rivers in southwestern Nigeria — compounds that were banned decades ago but still persist in the environment. Using a workflow that many analytical labs will recognize — liquid–liquid extraction, cleanup, rotary evaporation, nitrogen blowdown, and GC-ECD detection — they quantified 25 PCB congeners at trace levels and linked the results to ecological and human health risk.<h4>In this conversation, we cover:</h4><ul><li>Why legacy pollutants like PCBs still show up today</li><li>Choosing GC-ECD vs LC-MS for halogenated compounds</li><li>Liquid–liquid extraction and matrix cleanup strategies</li><li>Why sample concentration is critical for dilute environmental samples</li><li>How rotovap + nitrogen blowdown work together without losing volatile analytes</li><li>Seasonal trends (why wet season levels were higher)</li><li>Translating concentration data into meaningful risk assessments</li></ul><h3>Video Transcription</h3><section><div><div><div><div><div><div>Persistent organic pollutants such as polychlorinated biphenyls (PCBs) remain a significant environmental concern despite decades of regulatory restrictions. In this interview, Francais Femi Oloy discusses the environmental and analytical challenges associated with monitoring PCB contamination in rivers of southwestern Nigeria, a rapidly industrializing region where urban growth, industrial activity, agriculture, and dense populations intersect with extensive aquatic systems.Oloy explains that his interest in environmental contaminant analysis emerged from observing unexplained health problems and environmental degradation while growing up in Nigeria. This motivated his transition into organic and environmental chemistry, with a focus on identifying pollutants present in drinking water, agricultural soils, and food systems. Southwestern Nigeria, particularly the Lagos region, represents a critical environmental monitoring area due to intense industrial development, shipping activity, and widespread human dependence on rivers for domestic use, agriculture, and fishing.Although PCBs are considered “legacy pollutants” and are no longer intentionally produced, the interview highlights why they continue to persist in aquatic environments. Old electrical transformers and aging industrial equipment still contain PCB residues, while historical contamination stored in river sediments can become remobilized during flooding, dredging, or sediment disturbance. Because PCBs are hydrophobic and resistant to degradation, they preferentially accumulate in sediments and bioaccumulate through aquatic food chains, creating long-term environmental and human exposure risks.A major focus of the discussion centers on the analytical workflow used for PCB determination in environmental water samples. Composite river water samples were collected in amber glass bottles to avoid contamination and photodegradation, preserved with sodium azide to minimize microbial activity, and stored under cooled conditions prior to extraction. The analytical protocol employed liquid–liquid extraction using dichloromethane (DCM) and hexane to recover both polar and nonpolar PCB congeners. Oloy emphasizes that liquid–liquid extraction was selected over solid-phase extraction (SPE) because of concerns about congener retention within sorbent materials and clogging issues associated with large-volume environmental samples.Following extraction, concentration and cleanup represented critical analytical stages due to the trace-level occurrence and volatility of PCBs. Silica and alumina cleanup procedures were used to remove matrix interferences prior to instrumental analysis. The concentration workflow combined rotary evaporation for bulk solvent reduction with nitrogen blowdown for final volume reduction to less than 1 mL, while carefully avoiding excessive temperature or complete dryness to minimize analyte loss. Oloy repeatedly stresses that improper concentration procedures are among the most common causes of analytical failure in PCB analysis.For instrumental determination, the study utilized gas chromatography coupled with electron capture detection (GC-ECD) rather than LC-MS or GC-MS. According to Oloy, GC was preferred because PCBs are sufficiently volatile for gas chromatographic separation, while ECD provided superior sensitivity and selectivity for chlorinated compounds at environmentally relevant concentrations. The interview also discusses analytical validation strategies, including the use of surrogate standards to assess recoveries, which ranged from approximately 85% to 114%, and signal-to-noise-based determination of detection limits.The study further examined seasonal variations in PCB concentrations, revealing higher levels during the wet season. This observation was attributed to rainfall-driven runoff from contaminated infrastructure, sediment resuspension, and lower temperatures that reduce volatilization losses. To communicate toxicological relevance beyond simple concentration reporting, the researchers also calculated toxic equivalency values (TEQs), converting mixtures of PCB congeners into biologically meaningful toxicity estimates comparable to dioxin toxicity metrics.Beyond environmental monitoring, Oloy highlights broader research interests focused on pollutant remediation and sustainable environmental protection. His group is also involved in developing catalytic materials capable of degrading or removing persistent contaminants from environmental systems. Throughout the discussion, he emphasizes that analytical chemistry plays a central role not only in detecting pollutants, but also in enabling prevention, remediation, and long-term environmental management strategies.</div></div></div></div></div></div></section><blockquote>This text has been automatically transcribed from a video presentation using AI technology. It may contain inaccuracies and is not guaranteed to be 100% correct.</blockquote><blockquote><h4>Concentrating on Chromatography Podcast</h4>Dive into the frontiers of chromatography, mass spectrometry, and sample preparation with host David Oliva. Each episode features candid conversations with leading researchers, industry innovators, and passionate scientists who are shaping the future of analytical chemistry. From decoding PFAS detection challenges to exploring the latest in AI-assisted liquid chromatography, this show uncovers practical workflows, sustainability breakthroughs, and the real-world impact of separation science. Whether you’re a chromatographer, lab professional, or researcher you'll discover inspiring content!You can find Concentrating on Chromatography Podcast in podcast apps:<ul><li><a target="_blank" rel="noopener noreferrer" href="https://open.spotify.com/show/1wZg67rCjoGju4yhqxI3tL">Spotify</a></li><li><a target="_blank" rel="noopener noreferrer" href="https://podcasts.apple.com/tz/podcast/concentrating-on-chromatography/id1788429185">Apple podcast</a></li><li><a target="_blank" rel="noopener noreferrer" href="https://podscan.fm/podcasts/concentrating-on-chromatography">podscan</a></li></ul>and on <a target="_blank" rel="noopener noreferrer" href="https://www.youtube.com/@ChromatographyTalk/videos">YouTube channel</a></blockquote>

Tracking Toxic PCBs in River Water using Gas Chromatography–Electron Capture Detection

This study presents a high-temperature GC-APCI-MS/MS method for detecting large polycyclic aromatic hydrocarbons in pyroplastics and environmental samples. The approach enables sensitive analysis of PAHs with molecular weights from 314–424 Da without extensive cleanup or fractionation.Application to pyroplastics from the M/V X-Press Pearl fire revealed substantially elevated levels of large PAHs compared to unburnt plastics. Several compounds, including 1,3,5-triphenylbenzene, emerged as promising markers for identifying pyroplastic contamination, supporting future monitoring of plastic burning, fires, and microplastic pollution.<blockquote><h4>The original article</h4><h4><a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/10.1021/acsomega.5c11703">Gas Chromatography-Atmospheric Pressure Chemical Ionization (GC-APCI) Expands the Analytical Window for Detection of Large PAHs (≥24 Ringed-Carbons) in Pyroplastics and Other Environmental Matrices</a></h4>Cara Megill, Douglas M. Stevens*, Christopher M. Reddy, Bryan D. James*, Robert K. Nelson, and Frank L. DormanACS Omega 2026, 11, 7, 12321–12329<a target="_blank" rel="noopener noreferrer" href="https://doi.org/10.1021/acsomega.5c11703">https://doi.org/10.1021/acsomega.5c11703</a><h6>licensed under <a target="_blank" rel="noopener noreferrer" href="https://creativecommons.org/licenses/by/4.0/">CC-BY 4.0</a></h6></blockquote>Selected sections from the article follow. Formats and hyperlinks were adapted from the original.<div>The measurement and reporting of polycyclic aromatic hydrocarbons (PAHs) are routine practices in environmental monitoring and risk assessment. <a href="javascript:void(0);">(1−3)</a> However, of the thousands of PAHs, only the 16 designated as Priority Pollutants by the U.S. Environmental Protection Agency (EPA16) are typically reported. <a href="javascript:void(0);">(4,5)</a> These span two to six ringed parent PAHs, ranging in molecular weight from 128 to 278 Da. It is well recognized that this limited analyte list drastically simplifies and misses a significant fraction of PAHs. <a href="javascript:void(0);">(4)</a> For example, the concentration of C1–C4 alkylated PAHs can be greater than or equal to the concentration of the EPA16 in crude oils and fuels. <a href="javascript:void(0);">(6)</a> Expanding the analytical window of PAHs has proven valuable for forensic analysis of oil spills (e.g., alkylated and heterocycle-containing PAHs) and relevant for toxicological evaluation(e.g., oxygen-, nitrogen-, and sulfur-containing PAHs). <a href="javascript:void(0);">(3,7)</a> Moreover, the sources of PAHs have distinct compositions of PAHs, <a href="javascript:void(0);">(1,8)</a> which enables the use of PAHs for source apportionment. <a href="javascript:void(0);">(2,7)</a> Including alkylated and sulfur-containing PAHs (those beyond the EPA16) in the investigation of environmental samples and other matrices provides greater discriminating power between potential sources (using extracted ion chromatograms). <a href="javascript:void(0);">(3,7,9)</a> Additionally, monitoring the compositional changes of PAHs in the environment can inform about the fate and environmental processing of the matrix (e.g., oil weathering). <a href="javascript:void(0);">(2)</a> While these efforts have made strides in considering other PAHs, an environmentally relevant fraction of PAHs remains underutilized.PAHs with more than six rings have been reported in diverse environmental matrices. <a href="javascript:void(0);">(10,11)</a> These large PAHs (≥24 ringed-carbons <a href="javascript:void(0);">(10)</a>) have been found in combustion-derived particulate matter, <a href="javascript:void(0);">(12−19)</a> urban dust, <a href="javascript:void(0);">(20−23)</a> refinery deposits, <a href="javascript:void(0);">(11)</a> coal tars and pitches, <a href="javascript:void(0);">(24−27)</a> cokes, <a href="javascript:void(0);">(28)</a> soils, <a href="javascript:void(0);">(20,22)</a> sediments, <a href="javascript:void(0);">(20−23)</a> and deep-sea hydrothermal vent bitumen. <a href="javascript:void(0);">(29)</a> Most reports of large PAHs in environmental matrices have been from analyses of U.S. National Institute of Standards and Technology (NIST) standard reference materials (SRMs); <a href="javascript:void(0);">(18,21−23,25,26,30)</a> a few 302 Da isomers have been certified in three SRM. <a href="javascript:void(0);">(31)</a> Nonetheless, isomers ranging from 326 to 374 Da have been reported in SRMs for urban dust (1649a/b), diesel particulate (1650b and 2975), coal tar (1597a), and marine sediment (1941b), displaying qualitative differences between the sources in their large PAH compositions; <a href="javascript:void(0);">(18,20,22,23,27)</a> thus, large PAHs should offer forensic utility.Recent advances in soft ionization within an atmospheric pressure chemical ionization source for gas chromatography–mass spectrometry (GC-APCI) are well-suited for the analysis of large PAHs. Two contributing factors for this are the tolerance for high carrier gas flow rates by GC-APCI and the sensitivity of charge exchange APCI for aromatic species. <a href="javascript:void(0);">(48)</a> Increasing the carrier gas flow rate reduces the elution temperature of analytes, making many higher mass analytes accessible using a conventional GC and column, although poor thermal stability may still pose challenges for some analytes. <a href="javascript:void(0);">(49)</a> Classic vacuum-source GC/MS systems using electron ionization (EI) restrict the upper carrier gas flow allowed from the GC, and therefore, cannot fully utilize high GC carrier gas flows. The sensitivity of GC-APCI for components of petroleum, such as PAHs, has been previously reported. <a href="javascript:void(0);">(48)</a> Furthermore, unlike LC-APCI, which commonly exhibits protonation of analytes in positive ion mode, <a href="javascript:void(0);">(50)</a> GC-APCI+ can operate with dry source conditions. These conditions result in nitrogen-mediated charge exchange ionization and ions of the form M+•, the same form of molecular ion created using EI. As a result, because the charge site location on an ion dictates which product ions will be stable, the same multiple reaction monitoring (MRM) transitions can be used for both GC-APCI MS/MS and EI MS/MS. <a href="javascript:void(0);">(51)</a>Herein, a GC-APCI method was developed for the detection of large PAHs. Due to the limited availability of pure standards, previously characterized NIST SRMs were used in method development as sources of large PAHs. The values of the method and detection of large PAHs were demonstrated by analyzing environmental plastic samples collected after the M/V X-Press Pearl ship fire and plastic spill.<h4>Materials and Methods</h4><h5>GC-APCI</h5>The solvent extracts and dilutions were analyzed by GC-APCI on a <a target="_blank" rel="noopener noreferrer" href="https://lcms.labrulez.com/products/554">Xevo TQ Absolute</a> (Waters Corporation) tandem quadrupole mass spectrometer (TQ-MS/MS). The atmospheric pressure gas chromatography (APGC) ionization source was operated in charge transfer mode using dry N2 as the reagent gas. Dry N2 reagent gas creates molecular ions of the form M+• with no significant adduct formation for large PAHs. The high reagent gas flow rate of 350 mL/min into the ionization chamber, combined with low energies applied to the transfer optics from the atmospheric pressure region to the first quadrupole, leads to a high molecular ion survival rate. Furthermore, the use of MS/MS with quadrupoles operating at unit mass resolution prevents potential effects on response caused by adduct formation. Acquisitions were performed in positive ion, MRM mode. Two MRM transitions were used for each of the 16 precursor masses, ranging from 314 to 424 Da (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/suppl/10.1021/acsomega.5c11703/suppl_file/ao5c11703_si_001.pdf">Table S1</a>). No optimization of source conditions specific to the analysis of large PAHs was required. The list of 16 specific precursor masses targeted in this range was developed using multiple sources reporting large PAHs in NIST SRMs and samples from deep-sea hydrothermal vents. <a href="javascript:void(0);">(18,29,30)</a> The two transitions represented constant neutral losses of 2 and 4 Da at high collision energies of 60–100 eV, using N2 as the collision gas.For 1,3,5-TPB analysis, the APGC ionization source was operated in charge transfer mode using N2 as the collision gas. Acquisitions were performed in positive ion, MRM mode, yielding six MRM transitions for analysis (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/suppl/10.1021/acsomega.5c11703/suppl_file/ao5c11703_si_001.pdf">Table S2</a>). Similar to the large PAHs, this analyte also shows neutral losses of 2 and 4 Da, reflecting behavior like that of the more condensed structures.The <a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/library?mainauthorItems=10&amp;search=8890+GC">8890 GC (Agilent Technologies)</a> was configured with N2 as the carrier gas and an <a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/library?mainauthorItems=7&amp;search=Rxi-5HT">Rxi-5HT column (Restek)</a> of 15 m in length, 0.25 mm inner diameter, and 0.10 μm film thickness. The split/splitless (SSL) injection port was operated at a 10:1 split ratio with a temperature of 380 °C. A 1 μL injection volume was used for all analyses. The temperature program was 30.8 min; it started by holding at 40 °C for 0.5 min, then ramped to 160 °C at 14 °C/min, followed by a ramp to 395 °C at 22 °C/min and a hold at the temperature for 11 min. The flow rate of the N2 carrier gas was initially 0.60 mL/min, then ramped at 0.015 mL/min2 to 0.90 mL/min, followed by a ramp at 0.150 mL/min2 to 3.0 mL/min. To adapt the system for high-temperature work, the SSL was configured with a high-temperature septum (400 °C maximum), a 100% graphite liner O-ring, and a straight 4 mm inner diameter, wool-packed liner (450 °C maximum). Additional instrument and method details are included in the <a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/suppl/10.1021/acsomega.5c11703/suppl_file/ao5c11703_si_001.pdf">Supporting Information</a>.<h4>Results</h4><h5>Analysis of Large PAHs in Pyroplastic Samples by GC-APCI</h5>Macroplastic and microplastic debris from the M/V X-Press Pearl ship fire and plastic spill were investigated for the presence and distribution of large PAHs. The field samples included white, unburnt polyethylene nurdles and two types of pyroplastic, termed burnt plastic and combustion remnant (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/10.1021/acsomega.5c11703#fig1">Figure 1</a>), both of which were polyethylene. <a href="javascript:void(0);">(43)</a> The types of pyroplastics were previously operationally defined based on the size and shape of the pieces. <a href="javascript:void(0);">(43)</a>Investigation of the 302 Da isomers revealed profiles similar to those of the SRMs; however, unique differences were observed (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/suppl/10.1021/acsomega.5c11703/suppl_file/ao5c11703_si_001.pdf">Figure S2</a>). Eighteen to twenty-one peaks were detected across the plastic samples. Compared with the SRMs, the pyroplastics showed decreases in the relative abundance of dibenzo[a,e]fluoranthene and increases in dibenzo[a,h]pyrene (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/suppl/10.1021/acsomega.5c11703/suppl_file/ao5c11703_si_001.pdf">Figure S2</a>). This trend was not the case for the white nurdle sample. Starting at a retention time of 16.80 min, two peaks were unique to the pyroplastic samples (not present in the SRMs and especially minor in the white nurdles). These peaks followed that for dibenzo[a,h]pyrene, which had previously been reported as the last detected 302 Da isomer compound in the SRMs, <a href="javascript:void(0);">(21)</a> supporting their novelty as marker compounds of pyroplastics.The plastic samples displayed similarities and differences in the presence and distribution of large PAHs (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/10.1021/acsomega.5c11703#fig3">Figure 3</a>). The white nurdles, burnt plastic, and combustion remnant all contained high-intensity peaks at 20.50 min for 398 Da and 19.55 min for 374 Da. Peaks between 20.00 and 20.25 min of 398 Da and the 19.35 min peak of 374 Da were reduced in intensity for the pyroplastics compared to the white nurdles (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/suppl/10.1021/acsomega.5c11703/suppl_file/ao5c11703_si_001.pdf">Figure S3</a>). Conversely, the peaks between 18.50 and 18.75 min of 350 Da were more intense in the pyroplastics compared to the white nurdles.<img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/ACS_Omega_2026_11_7_12321_12329_Figure_3_Comparison_of_the_resolved_isomers_for_398_374_and_350_Da_of_the_white_nurdles_burnt_plastic_and_combustion_remnant_pieces_ec390ebae3.jpg" alt="ACS Omega 2026, 11, 7, 12321–12329: Figure 3. Comparison of the resolved isomers for 398, 374, and 350 Da of the white nurdles, burnt plastic, and combustion remnant pieces collected from Pamunugama Beach, Sri Lanka, following the 2021 M/V X-Press Pearl ship fire and plastic spill." srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_ACS_Omega_2026_11_7_12321_12329_Figure_3_Comparison_of_the_resolved_isomers_for_398_374_and_350_Da_of_the_white_nurdles_burnt_plastic_and_combustion_remnant_pieces_ec390ebae3.jpg 232w," sizes="100vw" width="1600" height="1077">The levels of all the targeted large PAHs were at least 2 orders of magnitude higher in the pyroplastics than in the white nurdles. These levels included the individual PAHs that were common to the pyroplastics. This trend mirrored that observed for smaller PAHs and the solvent-extractable content of the sample types. <a href="javascript:void(0);">(39,43,46)</a> There were also slight differences in the signatures of the large PAHs found in the pyroplastics. The 398 Da peak at 20.24 min, along with the 374 Da peak at 19.31 min and the 350 Da peak at 18.61 min, were more prominent in the combustion remnant compared to the burnt plastic (<a target="_blank" rel="noopener noreferrer" href="https://pubs.acs.org/doi/suppl/10.1021/acsomega.5c11703/suppl_file/ao5c11703_si_001.pdf">Figure S3</a>).Similar to the differences in large PAH signatures between the SRMs, the plastic samples had different signatures. Such qualitative interpretation of extracted ion chromatograms is forensically accepted for distinguishing sources. <a href="javascript:void(0);">(3)</a> This feature can potentially be utilized to differentiate between plastic types (e.g., virgin, weathered, and partially combusted) as well as to identify sources of the large PAHs and the combustion temperature.<h4>Conclusions</h4>GC-APCI-MS/MS proved a useful technique for detecting large PAHs in diverse environmental matrices, including extracts from pyroplastic field samples. Despite a lack of widely available analytical standards for large PAHs, NIST SRMs provided ample material for method development for their detection. Nonetheless, with the increasing research on microplastics in the environment and their relevance to human health, an environmental SRM with certified values for large PAHs is needed, and pyroplastics may provide such a source of material. Large PAHs and 1,3,5-TPB were detected in pyroplastic field samples and hold promise as chemical markers for pyroplastics, complementing other means for their detection in environmental samples (e.g., appearance and physical properties). Due to the accessibility of GC-APCI, the detection of large PAHs can be integrated into workflows for evaluating environmental samples, including those for microplastics.</div>

Gas Chromatography-Atmospheric Pressure Chemical Ionization (GC-APCI) Expands the Analytical Window for Detection of Large PAHs (≥24 Ringed-Carbons) in Pyroplastics and Other Environmental Matrices

In the week of May 11, the following webinars await you in the field of gas / solid phase and especially Raman, FTIR, GC and GC/MS.<blockquote><h4><a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/webinars">👉 DETAILS AND REGISTRATION IN THE WEBINARS SECTION</a></h4>👉 Search and filter in the largest global database with over 5 500 GC, LC, MS and spectroscopy webinars.</blockquote><h5>1. Thermo Fisher Scientific: Uncovering Microplastics: Identification, Quantification, and Exposure Assessment</h5><ul><li>Tu, 12.5.2026 08:00 CEST</li><li><a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/webinar/6136">Registration</a></li></ul>In this webinar, we will explore complementary analytical solutions for comprehensive microplastics characterization.<h5>2. AZoM: From Lab to Line: Leveraging GC and Process MS for Petrochemical Gas Analysis</h5><ul><li>We, 13.5.2026 16:00 CEST</li><li><a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/webinar/6171">Registration</a></li></ul>Explore how GC and process MS work together in petrochemical workflows, combining detailed lab analysis with real-time gas monitoring for faster decisions.<h5>3. Milestone: Modern Sample Prep for Organic Contaminants: PAHs, PFAS, MOSH/MOAH in Food</h5><ul><li>We, 13.5.2026 16:00 CET</li><li><a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/webinar/5822">Registration</a></li></ul>Learn how microwave-assisted extraction streamlines food analysis of PAHs, PFAS, and MOSH/MOAH, improving recoveries, reducing solvents, and meeting regulatory demands.<h5>4. Thermo Fisher Scientific: End-to-end automation in GC/GC-MS: Trends, tools, and practical implementation</h5><ul><li>We, 13.5.2026 18:00 CEST</li><li><a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/webinar/6186">Registration</a></li></ul>In this GC/GC-MS power hour session, we’ll explore how automation is transforming laboratories by helping teams do more with less time, fewer resources, and greater confidence.<h5>5. GERSTEL: Automating Food Safety Workflows for the Analysis of Edible Oils and Fats</h5><ul><li>We, 13.5.2026 20:00 CEST</li><li><a target="_blank" rel="noopener noreferrer" href="https://gcms.labrulez.com/webinar/6168">Registration</a></li></ul>Learn how automated workflows improve data quality in edible oil testing, including FAMEs, MOSH/MOAH, and 3-MCPD analysis with real-world insights.

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Organomation, founded in 1959, designs and manufactures high-quality nitrogen evaporators and extraction systems. Known for innovation and durability, their lab instruments are used globally for efficient sample preparation with strong customer support.

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Phenomenex Strata X-C Solid Phase Extraction (SPE)

Strata-X-C strong cation-exchange SPE retains basic compounds (pKa ≤10.5) with 100% organic wash for maximum cleanup. Offered in tubes, plates, and giga formats.

Strong Cation Mixed-Mode Solid Phase Extraction (SPE)A strong cation-exchange functionalized polymeric sorbent that allows for complete retention of basic compounds with a pKa less than 10.5, making 100% organic wash conditions possible. A 100% organic wash ensures that the maximum amount of interferences are removed from the target compound.<img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_C_SPE_4927d7340d.jpg" alt="Phenomenex: Strata-X-C SPE" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_C_SPE_4927d7340d.jpg 245w," sizes="100vw" width="500" height="268"><ul><li>Recommended Use: Extraction of weakly basic compounds</li></ul><h4>Starting Method</h4><h5>For Bases with pKa ≤ 10.5</h5><ul><li>Column: 1 mL Methanol</li><li>Equilibrate: 1 mL Acidified Water</li><li>Load: Diluted Acidified Sample</li><li>Wash 1: 1 mL 0.1 N HCI in Water (collect this fraction to analyze Polar Neutrals)</li><li>Wash 2: 1 mL 0.1 N HCI in Methanol (collect this fraction to analyze Neutrals/Acids)</li><li>Elute Bases: 2x 500 µL 5 % NH4OH in Methanol</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_single_tube_435d45d0ad.jpg" alt="Phenomenex: Strata X single tube" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_single_tube_435d45d0ad.jpg 156w," sizes="100vw" width="1080" height="1080">Based on 30 mg/1 mL sorbent mass. The above is a convenient starting point for SPE method development, further optimization may be required to tailor the method for your specific extraction needs.<h4>Available Formats</h4><ul><li>96-Well-Plate</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_96_well_plate_9a66005814.jpg" alt="Phenomenex: Strata X 96-well plate" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_96_well_plate_9a66005814.jpg 156w," sizes="100vw" width="1080" height="1080"><ul><li>1, 3, and 6mL Tubes</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_tubes_1_9b04cab6c1.jpg" alt="Phenomenex: Strata X 1, 3, and 6mL Tubes" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_tubes_1_9b04cab6c1.jpg 156w," sizes="100vw" width="1080" height="1080"><ul><li>Giga Tubes (12-150mL Tubes)</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_tubes_2_a8cd1706ec.jpg" alt="Phenomenex: Strata X Giga Tubes (12-150mL Tubes)" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_tubes_2_a8cd1706ec.jpg 156w," sizes="100vw" width="1080" height="1080">

Phenomenex Strata X-CW Solid Phase Extraction (SPE)

Strata-X-CW weak cation-exchange SPE retains strong bases (pKa >8) with 100% organic wash for maximum cleanup. Available in tubes, 96-well plates, and giga formats.

Weak Cation Mixed-Mode Solid Phase Extraction (SPE)A weak cation-exchange functionalized polymeric sorbent that allows for complete retention of basic compounds with a pKa greater than 8, making 100% organic wash conditions possible. A 100% organic wash ensures that the maximum amount of interferences are removed from the target compound.<img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_CW_SPE_b16a0e0baf.jpg" alt="Phenomenex: Strata-X-CW SPE" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_CW_SPE_b16a0e0baf.jpg 245w," sizes="100vw" width="500" height="268"><ul><li>Recommended Use: Extraction of basic compounds, particularly strong bases</li></ul><h4>Starting Method</h4><h5>For Bases with pKa &gt; 8</h5><ul><li>Column: 1 mL Methanol</li><li>Equilibrate: 1 mL Water, pH 6-7</li><li>Load: Diluted Sample, pH 6-7</li><li>Wash 1: 1 mL Water, pH 6-7</li><li>Wash 2: 1 mL Methanol (collect this fraction to analyze Neutrals/Acids)</li><li>Elute Any Bases: 2x 500 µL 5 % Formic Acid in Methanol</li><li>Elute Weak Bases: 2x 500 µL 5 % NH4OH in Methanol</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_single_tube_435d45d0ad.jpg" alt="Phenomenex: Strata X single tube" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_single_tube_435d45d0ad.jpg 156w," sizes="100vw" width="1080" height="1080">Based on 30 mg/1 mL sorbent mass. The above is a convenient starting point for SPE method development, further optimization may be required to tailor the method for your specific extraction needs.<h4>Available Formats</h4><ul><li>96-Well-Plate</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_96_well_plate_9a66005814.jpg" alt="Phenomenex: Strata X 96-well plate" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_96_well_plate_9a66005814.jpg 156w," sizes="100vw" width="1080" height="1080"><ul><li>1, 3, and 6mL Tubes</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_tubes_1_9b04cab6c1.jpg" alt="Phenomenex: Strata X 1, 3, and 6mL Tubes" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_tubes_1_9b04cab6c1.jpg 156w," sizes="100vw" width="1080" height="1080"><ul><li>Giga Tubes (12-150mL Tubes)</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_tubes_2_a8cd1706ec.jpg" alt="Phenomenex: Strata X Giga Tubes (12-150mL Tubes)" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_tubes_2_a8cd1706ec.jpg 156w," sizes="100vw" width="1080" height="1080">

Phenomenex Strata X Solid Phase Extraction (SPE)

Strata-X reversed phase SPE retains neutrals, acids, and bases via π-π, hydrogen bonding, and hydrophobic interactions. Robust cleanup under high organic wash.

Reversed Phase Solid Phase Extraction (SPE)A reversed phase functionalized polymeric sorbent that gives strong retention of neutral, acidic, or basic compounds under aggressive, high organic wash conditions. This sorbent relies on 3 mechanisms of retention: pi-pi bonding, hydrogen bonding (dipole-dipole interactions), and hydrophobic interaction.<img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_d8f4451e42.jpg" alt="Phenomenex: Strata-X" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_d8f4451e42.jpg 245w," sizes="100vw" width="433" height="247"><ul><li>Recommended Use: Extraction of neutrals and aromatics</li></ul><h4>Starting Method</h4><h5>For Neutral Compounds</h5><ul><li>Column: 1 mL Methanol</li><li>Equilibrate: 1 mL Water</li><li>Load: Diluted Sample</li><li>Wash: 1 mL 5-60 % Methanol</li><li>Elute: 2x 500 µL 2 % Formic Acid in Methanol/Acetonitrile</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_single_tube_435d45d0ad.jpg" alt="Phenomenex: Strata X single tube" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_single_tube_435d45d0ad.jpg 156w," sizes="100vw" width="1080" height="1080">Based on 30 mg/1 mL sorbent mass. The above is a convenient starting point for SPE method development, further optimization may be required to tailor the method for your specific extraction needs.<h4>Available Formats</h4><ul><li>96-Well-Plate</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_96_well_plate_9a66005814.jpg" alt="Phenomenex: Strata X 96-well plate" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_96_well_plate_9a66005814.jpg 156w," sizes="100vw" width="1080" height="1080"><ul><li>1, 3, and 6mL Tubes</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_tubes_1_9b04cab6c1.jpg" alt="Phenomenex: Strata X 1, 3, and 6mL Tubes" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_tubes_1_9b04cab6c1.jpg 156w," sizes="100vw" width="1080" height="1080"><ul><li>Giga Tubes (12-150mL Tubes)</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Phenomenex_Strata_X_tubes_2_a8cd1706ec.jpg" alt="Phenomenex: Strata X Giga Tubes (12-150mL Tubes)" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Phenomenex_Strata_X_tubes_2_a8cd1706ec.jpg 156w," sizes="100vw" width="1080" height="1080">

Organomation RapidVap N2 Nitrogen Evaporator

The RapidVap N₂ nitrogen evaporator enables fast solvent evaporation using a controlled nitrogen stream. It combines dry block heating, vortex motion, and end-point detection for efficient sample concentration.

The RapidVap N₂ Evaporation Systems provide a fast, automated alternative to <a target="_blank" rel="noopener noreferrer" href="https://lcms.labrulez.com/products/1904">Kuderna-Danish</a> and rotary evaporators, compatible with a wide range of aggressive chemicals. By directing a controlled stream of nitrogen or dry gas onto the sample surface, these systems reduce the partial pressure above the liquid to accelerate evaporation, with optional vortex motion and dry heat for further speed.&nbsp;The main block accommodates eight large samples up to 450 mL each, and an accessory block supports eight 170 mL tubes for solid phase extraction.&nbsp;The unique Cool-Zone block design slows evaporation after the end point, preventing samples from going completely dry and allowing time for solvent exchange or removal. Built-in alarms notify users when the process reaches the timed end point or approaches completion, enabling unattended operation.&nbsp;<ul><li>Dry Block: Dry heating system prevents potential contamination source</li><li>Increased Surface Area: Vortex motion increases surface area for faster evaporation</li><li>PTFE-Coated Chamber: Aluminum with PTFE coating for broad range of chemical compatibility</li><li>End-Point Detection: Signal completion of run allows samples to be left unattended while drying to desired end point</li></ul>In partnership with Labconco.<img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Organomation_Rapid_Vap_N2_Nitrogen_Evaporator_2_eb75d729d4.jpg" alt="Organomation RapidVap N2 Nitrogen Evaporator " srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Organomation_Rapid_Vap_N2_Nitrogen_Evaporator_2_eb75d729d4.jpg 235w," sizes="100vw" width="1152" height="764"><h3>STANDARD FEATURES</h3><ul><li>Dry block heating system prevents adding potential contamination source</li><li>Vortex action, heat, and vacuum combine to accelerate evaporation</li><li>PTFE-coated chamber for broad range of chemical compatibility</li><li>Microprocessor-controlled vortex motion increases surface area for faster evaporation</li><li>Signal completion of run allows samples to be left unattended while evaporation to desired end point</li><li>Microprocessor-controlled nitrogen blow down manifold to facilitate liquid to gas phase change</li></ul><h3>REQUIREMENTS (not included):</h3><ul><li>Glassware</li><li>Nitrogen source with flow rate of 0.6 CFM/17 LPM minimu</li><li>Gas pressure regulator</li></ul><h3>OPTIONS</h3><ul><li>RS-232 Link for two-way communication (Cat# LC-7910010)</li></ul><h3>SPECIFICATIONS</h3><ul><li>Instrument: RapidVap N2</li><li>Instrument Catalog Number: LC-7910000</li><li>Bath Type: Dry aluminum blocks</li><li>Number of Sample Positions: Up to 8</li><li>Dimensions (w x d x h): 21.7 x 19.0 x 13.5 in</li><li>Weight: Net: 99 lbs. (45 kg)</li><li>Weight: Gross: 107 lbs. (49 kg)</li><li>Sample Layout: Circular</li><li>Lid Material: Glass</li><li>Pressure Regulator: 0–20 psi</li><li>Temperature Range: 0–100 °C</li><li>Warranty: 1 year</li><li>Electrical Requirements: 115V, 60 Hz</li><li>Vortex Motion: Up to 500 RPM</li></ul><h5>Nitrogen Requirements</h5><ul><li>Flow Rate: 0.6 CFM / 17 LPM minimum</li><li>Pressure: 5–10 psi</li></ul><h3>ACCESSORIES</h3><ul><li>PTFE-coated aluminum blocks</li><li>Borosilicate glass tubes</li><li>600 mL tubes with stems</li><li>170 mL tubes with stems</li><li>Flat bottom tubes</li><li>Eight-place stainless steel racks</li><li>Glassware caps</li></ul>

Organomation RapidVap N2/48 Nitrogen Evaporator

The RapidVap N₂/48 Nitrogen Evaporation System rapidly concentrates up to 48 samples using nitrogen blowdown, vortex motion, and dry block heating without the need for water baths.

The RapidVap N₂/48 Evaporation System combines nitrogen blowdown, vortex motion, and controlled heat to accelerate evaporation of up to 48 small samples or eight 450 mL samples simultaneously. A stream of nitrogen or dry gas reduces the partial pressure over the liquid, speeding solvent removal, while microprocessor-controlled vortex motion increases surface area and continuously mixes samples for maximum recovery.&nbsp;Nitrogen delivery can be applied to 2, 4, 6, or all 8 clusters of six ports, conserving gas when processing fewer samples. Using a dry block heating method, the RapidVap N₂/48 offers a reliable, low-maintenance alternative to water bath systems and is ideal for applications such as drug development, bioresearch, combinatorial chemistry, environmental testing, forensics, and toxicology.&nbsp;<ul><li>Dry Block: Dry heating system prevents potential contamination source</li><li>Increased Surface Area: Vortex motion increases surface area for faster evaporation</li><li>PTFE-Coated Chamber: Aluminum with PTFE coating for broad range of chemical compatibility</li><li>End-Point Detection: Signal completion of run allows samples to be left unattended while drying to desired end point</li></ul>In partnership with Labconco.<img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Organomation_Rapid_Vap_N2_48_Nitrogen_Evaporator_2_cc454a8f2d.jpg" alt="Organomation RapidVap N2_48 Nitrogen Evaporator" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Organomation_Rapid_Vap_N2_48_Nitrogen_Evaporator_2_cc454a8f2d.jpg 234w," sizes="100vw" width="1169" height="783"><h3>STANDARD FEATURES</h3><ul><li>Dry block heating system prevents adding potential contamination source</li><li>Vortex action, heat, and vacuum combine to accelerate evaporation</li><li>PTFE-coated chamber for broad range of chemical compatibility</li><li>Microprocessor-controlled vortex motion increases surface area for faster evaporation</li><li>Signal completion of run allows samples to be left unattended while evaporation to desired end point</li><li>Microprocessor-controlled nitrogen blow down manifold to facilitate liquid to gas phase change</li></ul><h3>REQUIREMENTS (not included)</h3><ul><li>Sample block</li><li>Glassware</li><li>Nitrogen source with flow rate of 3.5 CFM/100 LPM minimu</li><li>Gas pressure regulator</li></ul><h3>OPTIONS</h3><ul><li>RS-232 Link for two-way communication (Cat# LC-7910014)</li></ul><h3>SPECIFICATIONS</h3><ul><li>Instrument: RapidVap N2/48</li><li>Instrument Catalog Number: LC-7910012</li><li>Bath Type: Dry aluminum blocks</li><li>Number of Sample Positions: Up to 48</li><li>Dimensions (w x d x h): 21.7 x 19.0 x 13.5 in</li><li>Weight: Net: 92 lbs. (42 kg)</li><li>Weight: Gross: 100 lbs. (45 kg)</li><li>Sample Layout: Circular</li><li>Lid Material: Glass</li><li>Pressure Regulator: 0–20 psi</li><li>Temperature Range: 0–100 °C</li><li>Warranty: 1 year</li><li>Electrical Requirements: 115V, 60 Hz</li><li>Vortex Motion: Up to 500 RPM</li></ul><h5>Nitrogen Requirements</h5><ul><li>Flow Rate: 3,5 CFM / 100 LPM minimum</li><li>Pressure: 5–10 psi</li></ul><h3>ACCESSORIES</h3><ul><li>PTFE-coated aluminum blocks</li><li>Borosilicate glass tubes</li><li>600 mL tubes with stems</li><li>170 mL tubes with stems</li><li>Flat bottom tubes</li><li>Eight-place stainless steel racks</li><li>Glassware caps</li></ul>

Organomation RapidVap Vertex Dry Evaporator

The RapidVap Vertex dry evaporator accelerates solvent evaporation for up to 50 samples using dry block heating, gentle nitrogen blowdown, and an intuitive touchscreen interface.

The RapidVap Vertex Dry Evaporator accelerates sample evaporation by combining efficient dry heat with gentle nitrogen blowdown, allowing laboratories to process up to 50 samples simultaneously.Its intuitive touchpad interface makes it easy to set and control both temperature and run time, and users can save up to ten custom programs to ensure consistent, repeatable workflows. Because it relies on a dry block heater rather than a traditional water bath, the system requires minimal upkeep—no distilled water, additives, or concerns about waterborne contamination.The RapidVap Vertex is well-suited for a wide range of sample prep needs, including pharmaceutical and drug development, clinical laboratories, environmental analysis, agricultural chemistry, and forensic testing.&nbsp;<ul><li>LCD Display: Touchscreen programming shows parameters for block, sample, and time</li><li>Nitrogen Control: Each switch controls nitrogen flow to each row of five nozzles</li><li>Temperature Sensor: Monitors block or sample temperature</li><li>Dry heat - no water bath: Less maintenance, no rust, no condensation, and no potential source of cross contamination</li></ul><img src="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/Organomation_Rapid_Vap_Vertex_Dry_Evaporator_2_c112725d7a.jpg" alt="Organomation RapidVap Vertex Dry Evaporator" srcset="https://storage.googleapis.com/labrulez-bucket-strapi-h3hsga3/thumbnail_Organomation_Rapid_Vap_Vertex_Dry_Evaporator_2_c112725d7a.jpg 245w," sizes="100vw" width="1375" height="768">In partnership with Labconco.<h3>STANDARD FEATURES</h3><ul><li>LCD display with touchscreen programming</li><li>Nitrogen control to each row of nozzles</li><li>Pressure regulator for 0 to 45 psi</li><li>Dry heat for less maintenance and no rust compared to water baths</li><li>Microprocessor-controlled heater up to 100 °C</li><li>Temperature sensor monitors block or sample temperature</li><li>Angled samples to increase surface area for faster evaporation</li></ul><h3>REQUIREMENTS (not included)</h3><ul><li>Aluminum block (Specific cat # depends on your tube size)</li><li>Sample tubes</li><li>Nitrogen source with a flow rate of 6.5 CFM/185 LPM minimum</li></ul><h3>SPECIFICATIONS</h3><ul><li>Instrument Catalog Number: LC-7320020</li><li>Bath Type: Dry aluminum blocks</li><li>Number of Sample Positions: Up to 50</li><li>Dimensions (w x d x h): 20.4 x 13.0 x 12.5 in</li><li>Weight: Net: 35 lbs. (16 kg)</li><li>Weight: Gross: 45 lbs. (20 kg)</li><li>Sample Layout: 5 rows of 10 samples</li><li>Lid Material: Glass</li><li>Pressure Regulator: 0–45 psi</li><li>Temperature Range: 30–100 °C</li><li>Warranty: 1 year</li><li>Electrical Requirements: 115V, 60 Hz</li></ul><h5>Nitrogen Requirements</h5><ul><li>Flow Rate: 6.5 CFM / 185 LPM minimum</li><li>Pressure: &lt;50 psi</li></ul><h3>ACCESSORIES</h3><ul><li>Aluminum blocks</li></ul>

Organomation 6 Position N-EVAP Nitrogen Evaporator

Compact nitrogen evaporator for up to 6 samples with precise flow control, heated bath options, and wide sample compatibility.

The Organomation 6 Position N-EVAP is a compact and cost-effective sample concentrator designed for simultaneous evaporation of up to 6 samples. Based on the proven N-EVAP technology developed in the 1970s, it ensures reliable and reproducible solvent evaporation using nitrogen gas within a heated bath.The system supports a wide range of sample sizes – 10–30 mm OD as standard, and up to 30–56 mm OD with an optional holder. The circular rotating design allows easy front access to all samples.<h4>Key Features</h4><ul><li>Evaporation of up to 6 samples simultaneously</li><li>Adjustable nitrogen flow: 0–10 L/min</li><li>Individually adjustable needle valves for precise control</li><li>Circular rotating sample holder for easy access</li><li>Wide sample diameter range: 10–56 mm OD (with optional holder)</li><li>Stainless steel bath construction for durability</li><li>Water or dry bath configurations available</li><li>High temperature limit switch for safety</li><li>Phthalate-free silicone tubing to prevent contamination</li><li>Efficient nitrogen usage with minimal waste</li></ul><h3>Technical Specifications</h3><h4>General</h4><ul><li>Number of positions: 6</li><li>Sample holder layout: Circular</li><li>Gas manifold: Single ring</li><li>Gas flow meter: 0–10 L/min</li><li>Standard sample OD: 10–30 mm</li><li>Optional sample OD: 30–56 mm</li><li>Gas input pressure: 20–30 psig</li><li>With regulator: 30–160 psig</li></ul><h4>Dimensions</h4><ul><li>Water bath: 33 × 28 × 79 cm</li><li>Dry bath: 33 × 28 × 70 cm</li><li>Reduced height: 33 × 28 × 61 cm</li></ul><h4>Needles</h4><ul><li>Length: 4 in (≈10 cm)</li><li>Gauge: 19 ga</li><li>Material: stainless steel + chrome-plated brass hub</li></ul><h4>Heating – Water Bath</h4><ul><li>Temperature range: 30–90 °C</li><li>Power: 550 W</li><li>Controller: mechanical thermostat</li><li>Accuracy: ±2 °C</li></ul><h4>Heating – Dry Bath</h4><ul><li>Temperature range: 40–130 °C</li><li>Power: 500 W</li><li>Medium: aluminum / glass beads</li><li>Accuracy: ±2 °C</li></ul>

Organomation 20 Position Auto N-EVAP Nitrogen Evaporator

The 20 Position Auto N-EVAP enables automated, safe evaporation of up to 20 samples with digital control and pneumatic sample handling.

The Organomation 20 Position Auto N-EVAP is the most advanced nitrogen evaporator developed by Organomation. It combines the classic N-EVAP system with timed automation and optional nitrogen self-generation.The instrument operates in both automatic and manual modes using an integrated pneumatic system. In automatic mode, samples are removed from the heating bath at the end of the cycle, reducing the risk of sample loss or damage.A digital control system provides precise control of gas flow and bath temperature, ensuring safe and reproducible evaporation of up to 20 samples simultaneously.<h4>Key Features</h4><ul><li>Automatic and manual operation modes</li><li>Capacity of up to 20 samples</li><li>Automatic sample removal after cycle completion</li><li>Digital control of temperature and timing</li><li>Nitrogen flow up to 25 L/min</li><li>Built-in pressure reducing regulator</li><li>Dual nitrogen filtration system</li><li>Pneumatic sample lift (gas piston)</li><li>Safety cover and circuit breaker</li><li>Precision needle valve control</li><li>Phthalate-free high-pressure tubing</li><li>Reduced risk of sample loss through automation</li></ul><h4>Available Model</h4><h5>Automatic 20 Position N-EVAP – Water Bath</h5><ul><li>Catalog number: 11220-A</li><li>Bath type: Water</li><li>Number of positions: 20</li><li>Dimensions: 49 × 46 × 92 cm</li><li>Temperature range: 30–100 °C</li><li>Total wattage: 1100 W</li></ul><h5>Standard Features</h5><ul><li>Adjustable flow meter: 0–25 L/min</li><li>Built-in pressure reducing regulator</li><li>Dual nitrogen filters</li><li>Digital temperature controller (LED)</li><li>Electronic timer</li><li>High temperature limit switch</li><li>Safety cover</li><li>Circuit breaker</li><li>High-pressure phthalate-free tubing</li><li>Precision variable valve technology</li><li>Gas piston lift mechanism</li><li>Set of 20 needles (4" × 19 gauge)</li></ul><h4>Options</h4><ul><li>220v wiring harness</li><li>Z-Purge / positive pressure purge case</li><li>Acid resistant coating on instrument and needles</li></ul><h4>Technical Specifications</h4><h4>General</h4><ul><li>Number of positions: 20</li><li>Sample holder layout: Circular</li><li>Gas manifold: Single Ring</li><li>Gas flow rate: 0–25 L/min</li><li>Sample size range: 10–30 mm OD</li><li>Nitrogen input pressure: 30–110 psig</li><li>Acid resistant coating: Optional</li></ul><h4>Needles</h4><ul><li>Size: 102 mm × 19 ga (4")</li><li>Material: stainless steel with plated brass hub</li></ul><h4>Sample Lift Mechanism</h4><ul><li>Type: Gas piston</li><li>Function: automatic lifting/removal of samples</li></ul><h4>Control System</h4><ul><li>Digital temperature control (LED display)</li><li>Electronic timer for gas and heating</li></ul><h4>Heating Specifications</h4><ul><li>Model: 11196</li><li>Medium: Water</li><li>Inside dimensions: 11 × 11 × 5.5 in</li><li>Outside dimensions: 49 × 46 × 18 cm</li><li>Power: 1100 W</li><li>Temperature range: 30–100 °C</li><li>Controller: digital electronic</li><li>Accuracy: ±2 °C</li></ul><h4>Accessories</h4><ul><li>Nitrogen generator (20 L/min)</li><li>Pasteur pipette adapters</li><li>Pressure reducing regulator 0–160 psi</li><li>High temperature silicone fluid</li><li>Various needle sizes and gauges</li></ul><h4>Replacement Parts</h4><ul><li>NA1955 – Nitrogen generator</li><li>NA0603 – Needles 4" × 19 ga</li><li>NA0636 – Pasteur pipette adapter</li></ul>

Organomation 9 Position MULTIVAP Nitrogen Evaporator

The MULTIVAP 9 Position enables rapid evaporation of large-volume samples using a high-temperature dry block and efficient row-based nitrogen control.

The Organomation 9 Position MULTIVAP is a high-temperature dry block nitrogen evaporator designed for large volume sample evaporation.The system features a rectangular 3×3 gas distribution manifold and a dual post lifting assembly, allowing easy adjustment of needles or pipettes. Nitrogen is directed onto the sample surface, enabling rapid solvent evaporation and efficient sample concentration.Each row of three positions can be individually switched on/off, allowing significant nitrogen savings when processing fewer samples.The system operates with a heated aluminum dry block (30–120 °C) or as an ambient (unheated) version.<h4>Key Features</h4><ul><li>Up to 9 samples simultaneously (3×3 layout)</li><li>High-temperature dry block: 30–120 °C</li><li>Ambient (unheated) version available</li><li>Direct nitrogen delivery onto sample surface</li><li>Row-based gas control (3 samples per row)</li><li>Nitrogen flow range: 0–25 L/min</li><li>Built-in pressure regulator</li><li>Digital temperature control and timer</li><li>Dual spring hoist lifting system</li><li>Includes 50 mm OD beakers</li><li>Custom inserts available for different sample sizes</li><li>Compatible with organic solvents</li><li>Optional acid-resistant configuration</li></ul><h4>Available Models</h4><h5>9 Position MULTIVAP – Dry Block</h5><ul><li>Catalog number: 11809</li><li>Heating type: Dry block</li><li>Number of positions: 9</li><li>Dimensions: 41 × 36 × 76 cm</li><li>Temperature range: 30–120 °C</li><li>Power: 900 W</li></ul><h5>9 Position MULTIVAP – No Heating</h5><ul><li>Catalog number: 11809-O</li><li>Heating type: None</li><li>Number of positions: 9</li><li>Dimensions: 33 × 38 × 66 cm</li><li>Temperature: Ambient</li></ul><h4>Standard Features</h4><ul><li>Adjustable flow meter: 0–25 L/min</li><li>Gas distribution manifold (3×3)</li><li>Nitrogen filter</li><li>Built-in pressure reducing regulator</li><li>Electronic timer</li><li>Digital temperature controller (LED)</li><li>Safety control cover plate</li><li>High temperature limit switch</li><li>Dual band hoist spring assembly</li><li>9 beakers (50 mm OD included)</li></ul><h4>Options</h4><ul><li>220v wiring harness</li><li>Z-Purge / positive pressure purge case</li><li>Acid resistant coating</li><li>Pasteur pipette adapters instead of needles</li><li>Manifold and stand only (no heating platform)</li></ul><h3>Technical Specifications</h3><h4>General</h4><ul><li>Number of positions: 9</li><li>Layout: Rectangular (3×3)</li><li>Spacing: 5.87 cm</li><li>Standard vessels: 50 mm OD beakers</li><li>Optional tube range: 16–40 mm OD</li><li>Gas flow: 0–25 L/min</li><li>Flow control: per row (3 samples)</li><li>Gas input pressure: 30–110 psig</li><li>Acid resistant coating: Optional</li></ul><h4>Needles</h4><ul><li>Size: 102 mm × 16 ga</li><li>Material: stainless steel</li><li>Needle guide: optional for tubes</li></ul><h4>Lift Mechanism</h4><ul><li>Type: Dual pulley &amp; band springs</li><li>Function: adjustable needle height</li></ul><h4>Heating Specifications</h4><ul><li>Model: 9156</li><li>Type: Aluminum dry block</li><li>Dimensions: 41 × 36 × 15 cm</li><li>Power: 900 W</li><li>Temperature range: 30–120 °C</li><li>Controller: digital electronic (LED)</li><li>Accuracy: ±2 °C</li></ul><h4>Accessories</h4><ul><li>Nitrogen generator</li><li>Custom inserts&nbsp;</li><li>Pasteur pipette adapters</li><li>Luer plugs</li><li>Various needle sizes and gauges</li></ul>

Organomation 30 Position MULTIVAP Nitrogen Evaporator

The MULTIVAP 30 Position enables high-throughput evaporation of up to 30 samples with a heated dry block, efficient gas control, and custom inserts.

The Organomation 30 Position MULTIVAP is a high-capacity dry block nitrogen evaporator designed for parallel evaporation of up to 30 samples.The system features a rectangular 5×6 gas distribution manifold and a dual post lifting assembly. Nitrogen is directed onto the sample surface, enabling rapid solvent evaporation and efficient concentration.Each row of 5 samples can be independently switched on/off, allowing significant nitrogen savings when processing fewer samples.The system operates with a heated aluminum dry block (30–120 °C) or as an ambient (unheated) version. Custom-made inserts and blocks ensure optimal heat transfer for specific sample sizes.<h4>Key Features</h4><ul><li>Up to 30 samples simultaneously (5×6 layout)</li><li>High-temperature dry block: 30–120 °C</li><li>Ambient (no heating) version available</li><li>Direct nitrogen blowdown onto sample surface</li><li>Row-based gas control (5 samples per row)</li><li>Nitrogen flow: 0–25 L/min</li><li>Built-in pressure regulator</li><li>Digital temperature control and timer</li><li>Dual spring hoist system</li><li>Custom inserts for optimized heat transfer</li><li>Compatible with organic solvents</li><li>Optional acid-resistant version</li></ul><h4>Available Models</h4><h5>30 Position MULTIVAP – Dry Block</h5><ul><li>Catalog number: 11830</li><li>Heating type: Dry block</li><li>Number of positions: 30</li><li>Dimensions: 41 × 36 × 76 cm</li><li>Temperature range: 30–120 °C</li><li>Power: 900 W</li></ul><h5>30 Position MULTIVAP – No Heating</h5><ul><li>Catalog number: 11830-O</li><li>Heating type: None</li><li>Number of positions: 30</li><li>Dimensions: 33 × 38 × 66 cm</li><li>Temperature: Ambient</li></ul><h4>Standard Features</h4><ul><li>Adjustable flow meter: 0–25 L/min</li><li>Gas distribution manifold (5×6)</li><li>Nitrogen filter</li><li>Built-in pressure reducing regulator</li><li>Digital temperature controller (LED)</li><li>Electronic timer</li><li>Safety control cover plate</li><li>High temperature limit switch</li><li>Dual band hoist spring assembly</li></ul><h4>Options</h4><ul><li>220v wiring harness</li><li>Z-Purge / positive pressure purge case</li><li>Acid resistant coating</li><li>Pasteur pipette adapters instead of needles</li><li>Manifold and stand only (no heating platform)</li></ul><h3>Technical Specifications</h3><h4>General</h4><ul><li>Number of positions: 30</li><li>Layout: Rectangular (5×6)</li><li>Spacing: 3.33 cm</li><li>Sample diameter range: 16–30 mm OD</li><li>Gas flow: 0–25 L/min</li><li>Flow control: per row (5 samples)</li><li>Gas input pressure: 30–110 psig</li><li>Acid resistant coating: Optional</li></ul><h4>Needles</h4><ul><li>Size: 102 mm × 19 ga</li><li>Material: stainless steel</li><li>Needle guide: optional</li></ul><h4>Lift Mechanism</h4><ul><li>Type: Dual pulley &amp; band springs</li><li>Function: adjustable needle height</li></ul><h4>Heating Specifications</h4><ul><li>Model: 9156</li><li>Type: Aluminum dry block</li><li>Dimensions: 41 × 36 × 15 cm</li><li>Power: 900 W</li><li>Temperature range: 30–120 °C</li><li>Controller: digital electronic (LED)</li><li>Accuracy: ±2 °C</li></ul><h4>Accessories</h4><ul><li>Nitrogen generator</li><li>Custom inserts</li><li>Pasteur pipette adapters (not compatible with needle guide)</li><li>Luer plugs</li><li>Various needle sizes and gauges</li></ul>

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