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Methylene Chloride DCM Reagent Grade
- Product Name: Methylene Chloride DCM Reagent Grade
- Factroy Site: Binhai New Area, Tianjin, China
- Price Inquiry: sales4@ascent-chem.com
- Manufacturer: Ascent Petrochem Holdings Co., Limited
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- In terms of specification, Methylene Chloride DCM Reagent Grade is supplied with a minimum assay of 99.5% and a maximum water content of 0.02%, making it suitable for analytical extraction and laboratory solvent applications.
| HS Code | 892610 |
| Chemical Name | Methylene Chloride (Dichloromethane) |
| Cas Number | 75-09-2 |
| Molecular Formula | CH2Cl2 |
| Molecular Weight | 84.93 g/mol |
| Appearance | Clear colorless liquid |
| Purity | ≥99.5% (Reagent Grade) |
| Boiling Point | 39.6 °C (103.3 °F) |
| Melting Point | -96.7 °C (-142.1 °F) |
| Density | 1.325 g/cm3 at 20 °C |
| Refractive Index | 1.424 at 20 °C |
| Vapor Density | 2.93 (air = 1) |
| Solubility | Slightly soluble in water; miscible with most organic solvents |
As an accredited Methylene Chloride DCM Reagent Grade factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | Methylene Chloride DCM Reagent Grade, 1 L, packaged in a sealed amber glass bottle with secure cap for safe storage. |
| Container Loading (20′ FCL) | 20′ FCL: Methylene Chloride DCM reagent grade loaded in UN-approved drums, secured, with hazardous cargo documentation, ventilation, and segregation per IMDG. |
| Shipping | Ship Methylene Chloride DCM Reagent Grade as hazardous material via ground transport only. Use approved UN-rated containers, secure upright, and label with proper hazard warnings. Comply with DOT and IATA regulations, include SDS, and avoid temperatures above 40°C. No air or international shipments without special permits. |
| Storage | Store methylene chloride (DCM) reagent grade in a tightly sealed, original container in a cool, dry, well-ventilated area away from direct sunlight, heat, and moisture. Keep it separate from strong oxidizers, acids, and bases. Use corrosion-resistant shelving, avoid incompatible plastics, and ensure proper secondary containment to prevent spills. |
| Shelf Life | Stable for 2–3 years when stored tightly sealed, cool, dry, and away from light and moisture. |
In US EPA Method 3510C, aqueous environmental samples are prepared for semivolatile organic analysis by a three-stage liquid-liquid extraction sequence. A 1 L sample is first adjusted to pH ≤ 2 with 1:1 sulfuric acid. The acid fraction is extracted three times with 60 mL portions of DCM reagent grade in a 2 L PTFE stopcock separatory funnel. The denser DCM phase settles below the aqueous layer because its density at 20 °C is 1.325 g/cm³. After collection of the acid extract, the aqueous phase is adjusted to pH ≥ 11 with 10 N sodium hydroxide. The base-neutral fraction is extracted with three additional 60 mL portions of the same solvent. Each extract is passed through a column of granular anhydrous sodium sulfate to remove emulsified water. The combined extract is concentrated in a Kuderna-Danish apparatus fitted with a 3-ball Snyder column over a water bath maintained at 35 °C to 40 °C, followed by nitrogen blowdown to a final volume of 1.0 mL. The reagent-grade DCM used for this workflow must meet the ACS residue-after-evaporation specification of 0.002% maximum and a water specification of 0.02% maximum. Amylene-stabilized DCM is permitted for many semivolatile procedures, but the stabilizer introduces a low-boiling interference in the full-scan GC-MS window if the final extract is held too long before analysis. For this reason, laboratories performing US EPA Method 8270E often stock amylene-free DCM for acid/base-neutral extraction.
The extraction efficiency of the acid fraction is controlled less by solvent purity than by emulsion production in turbid landfill leachate and sewage sludge matrices. If stable emulsions occupy more than one-third of the separatory funnel volume, mechanical agitation is reduced and sodium chloride is added to a concentration of 20% w/v. Centrifugation at 2000 × g for 10 min often restores a clear phase boundary. In matrices containing more than 1% w/w surfactant, acid recovery can fall below 40% unless continuous liquid-liquid extraction is substituted. The continuous extractor described in US EPA Method 3520C uses a slower DCM throughput and reduces operator contact with the solvent. Published matrix spike data for these configurations are limited; recovery values must be generated for each sample type using acid surrogate standards and matrix duplicates.
| Parameter | Acid Fraction | Base-Neutral Fraction |
|---|---|---|
| Aqueous pH adjustment | pH ≤ 2 | pH ≥ 11 |
| DCM volume per 1 L sample | 3 × 60 mL | 3 × 60 mL |
| Phase separation | DCM lower layer | DCM lower layer |
| Concentration equipment | Kuderna-Danish | Kuderna-Danish |
| Final blowdown | 1.0 mL, 35 °C | 1.0 mL, 35 °C |
What Governs Surrogate Recovery When Emulsions Form in DCM Liquid-Liquid Extraction?
Surrogate recovery in DCM extraction is dominated by the physical behavior of the solvent-water interface rather than by solvent purity. The acid/base-neutral sequence in US EPA Method 3510C assumes a clean phase split after each 60 mL addition. In practice, aqueous samples from meat processing, pulp mill effluent, or landfill leachate contain suspended colloids and surface-active agents that stabilize DCM-in-water emulsions. The standard technique is to reduce shaking intensity and to add sodium chloride to a final concentration of 20% w/v. Sodium sulfate may be used in the same mass range, but its salting-out effect is weaker at low temperature. Centrifugation at 2000 × g to 3000 × g for 5 min to 10 min is used when a clear phase does not form within 2 min. If the emulsion persists, the extract is transferred to a continuous liquid-liquid extractor and processed for 18 h to 24 h. The surrogate standard response is then recorded against the method blank. Low acid-fraction surrogate recovery below 60% is a failure flag unless matrix-specific correction is demonstrably valid. The operational boundary is reached when the sample contains more than 1% w/w nonionic surfactant; at that point, no mechanical salting-out method reliably restores phase separation, and the method should be replaced by solid-phase extraction or direct injection with isotope dilution.
Reagent-grade DCM with amylene stabilizer contributes a gas chromatographic peak in the early elution window. For acid fraction extracts analyzed by US EPA Method 8270E, amylene is typically not reported because the quantitation focuses on semivolatile compounds eluting after the solvent front. However, libraries that include low-mass oxygenated by-products may require amylene-free DCM. Such lots are more sensitive to photolytic degradation and must be stored in amber glass under nitrogen. The use of unstabilized DCM in a laboratory with high ultraviolet exposure can generate acidic decomposition products that reduce extraction pH in unbuffered samples. A buffer control at pH 7 is run alongside each batch to detect this drift.
Low-temperature acetylation of amino alcohols with acyl chlorides uses DCM reagent grade as both the reaction medium and the extraction solvent in a single process stream. The substrate is dissolved in DCM at a loading of 1:8 w/v in a jacketed glass reactor fitted with PTFE baffles and a reflux condenser. The solution is cooled to 0 °C to 5 °C. An acyl chloride is then added over 60 min to 90 min while maintaining the internal temperature below 10 °C. The low boiling point of DCM of 39.6 °C allows the subsequent work-up to be performed at 30 °C under reduced pressure. Since the product remains in the lower DCM layer, aqueous quenching with saturated sodium bicarbonate removes excess acid chloride and water-soluble salts without additional extraction solvent. The reagent-grade requirement is stricter than industrial DCM because residual nonvolatile impurities concentrate in the final crystallization. ACS-grade DCM with a water limit of 0.02% prevents premature hydrolysis of the acyl chloride. The reaction is not suitable for primary amine substrates because acid-base complexation can precipitate the hydrochloride salt and trap product in the aqueous phase. In such cases, a co-solvent ratio of DCM to tetrahydrofuran at 3:1 v/v is used, but the gain in solubility is offset by a higher boiling mixed-solvent azeotrope and longer distillation cycles.
Batch-to-batch variability in reagent-grade DCM water content below 0.02% is not the main source of process drift. More significant is iron contamination introduced from storage drums with damaged phenolic linings. Iron at levels above 0.1 mg/kg accelerates decomposition of DCM to chlorinated by-products under reflux. This failure mode is observed on pilot-scale lines where bulk solvent is stored in carbon steel rather than stainless steel or lined containers. A nitrogen blanket at 20 kPa and amber storage reduce oxidative degradation. When the recovered DCM is reused, it should be redistilled and checked for free acid before the next acylation batch.
Polycarbonate Solution Viscosity Correlates with Moisture and DCM Assay
Solution viscosity measurement for polycarbonate resins in DCM reagent grade is performed according to ASTM D2857-16 with an Ubbelohde capillary viscometer immersed in a water bath controlled at 25.0 °C ± 0.02 °C. The polymer is dried to 0.05% residual moisture before dissolution in DCM at a concentration of 0.5 g/dL. The solution is filtered through a 0.45 µm PTFE membrane to remove gel particles. DCM reagent grade for this test must contain no more than 0.02% water because water promotes polycarbonate hydrolysis during the dissolution step, which depresses intrinsic viscosity. The test is run under stable nitrogen to exclude atmospheric moisture. The efflux time of the solvent blank is measured before and after each polymer sample to correct for capillary drift. The relationship between intrinsic viscosity and molecular weight uses Mark-Houwink coefficients that are valid only at the stated temperature and solvent water content. A shift of 0.1 °C can change efflux time by more than 0.3%, which is analytically significant for resin lot acceptance. Amylene-stabilized DCM does not interfere with viscosity measurement, but stabilizer residue can remain in the recovered polymer film if the solution is cast for mechanical testing. In that case, the stabilizer must be removed by vacuum drying at 40 °C for 24 h.
Manufacturers calibrating viscosity against melt flow rate often observe nonlinear behavior when DCM assays fall below 99.5%. The nonvolatile residue component, typically oligomeric plasticizers extracted from drum linings, acts as a viscosity modifier. Thus, a lot with assay 99.4% can pass viscosity limits but fail subsequent optical clarity testing on cast film. The operational boundary is a maximum residue after evaporation of 0.002%; above this limit, solution haze becomes visible at 10 NTU and the lot is diverted to cleaning applications. For resin specifications with an intrinsic viscosity acceptance range of 0.50 dL/g to 0.60 dL/g, moisture ingress must be controlled during solvent transfer through desiccant vent filters. Published data for these specific configurations are limited, but the sensitivity of polycarbonate hydrolysis to wet DCM is well documented in resin supplier technical bulletins.
When Normal-Phase Preparative Gradients Require Amylene-Free DCM Lots
Normal-phase preparative chromatography of tocopherols, sterols, and medium-polarity natural product fractions uses silica columns eluted with heptane and DCM. DCM reagent grade is the strong solvent in the gradient. A typical preparative method starts at 5% DCM in heptane and rises to 95% DCM over 20 min on a 250 mm × 20 mm silica column packed with 5 µm particles. The UV detection wavelength is normally set at 254 nm, where DCM has acceptable transmittance. Baseline drift during the gradient is caused by trace nonvolatile residue in the DCM lot, not by the solvent cut-off. The use of amylene-stabilized DCM in this mode generates a positive baseline slope because amylene elutes early and is depleted from the mixed mobile phase as the DCM fraction increases. Amylene-free DCM must therefore be specified for UV baseline-critical separations. The pressure drop across the column when DCM reaches 95% is lower than water-based reversed-phase methods but higher than pure heptane because the viscosity of DCM is 0.44 mPa·s at 20 °C versus 0.386 mPa·s for heptane. This difference is small but becomes measurable on 150 mm column formats.
Fraction collection is controlled by UV threshold and the solvent is removed on a rotary evaporator with a bath temperature of 30 °C to 35 °C. DCM reagent grade for preparative work must be tested for free acid because acidic degradation products can modify the silica surface and shift retention times of ionizable analytes. The operational limit for free acid is typically below 0.001 meq/g. When this limit is exceeded, the retention time of organic acids drifts by more than 0.5 min over a single campaign. For this reason, bulk DCM stored in clear glass under warm conditions should not be used for method development without a prior pH check. Published data for this specific configuration is limited.
Class 2 Solvent Control in Extractables and Leachables Screening
DCM reagent grade is used as an exhaustive extraction solvent in extractables testing of medical device materials under ISO 10993-18:2021. The solvent is classified as medium-polarity and swells materials such as silicone rubber, polyurethane, and polyvinyl chloride. Extraction is carried out by Soxhlet apparatus at 40 °C for 24 h to 72 h depending on the device geometry. The DCM extract is concentrated to 1.0 mL and analyzed by GC-MS, LC-MS, and inductively coupled plasma mass spectrometry. Because DCM is itself a Class 2 residual solvent under ICH Q3C(R8), its permitted daily exposure is 6.0 mg/day and its concentration limit in pharmaceutical products is 600 ppm. The use of DCM as an extraction solvent is therefore confined to controlled laboratory preparation. It is not a direct formulation solvent for drug products. Reagent-grade DCM submitted for extractables screening should meet the ACS assay specification of 99.5% minimum and residue after evaporation of 0.002% maximum. Any nonvolatile residue is a direct analytical interference because it is reported as an extractable material from the test article.
The extractables profile obtained with DCM is not equivalent to the leachables profile under aqueous or mixed aqueous-organic conditions. DCM swells hydrophobic polymer networks and extracts high-molecular-weight oligomers, processing aids, and antioxidant degradation products that are not released in water. When the DCM extract is blown to dryness under nitrogen at 35 °C, low-boiling compounds such as siloxane oligomers can be lost. Internal standards are added before concentration to correct for this loss. The operational boundary is a final volume below 0.2 mL; at this point, analyte recovery declines nonlinearly and the extract should be diluted instead of evaporated further.
| Parameter | Specification / Limit | Reference |
|---|---|---|
| DCM assay | ≥ 99.5% | ACS Reagent Monograph |
| Residue after evaporation | ≤ 0.002% | ACS Reagent Monograph |
| Water | ≤ 0.02% | ACS Reagent Monograph |
| DCM permitted daily exposure | 6.0 mg/day | ICH Q3C(R8) |
| DCM concentration limit in drug products | 600 ppm | ICH Q3C(R8) |
| Exhaustive extraction medium-polarity solvent | 40 °C, 24 h to 72 h | ISO 10993-18:2021 |
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- Methylene Chloride DCM Reagent Grade is manufactured under an ISO 9001 quality system and complies with relevant regulatory requirements.
- COA, SDS/MSDS, and related certificates are available upon request. For certificate requests or inquiries, contact: sales4@ascent-chem.com.
Model identifiers for the methylene chloride DCM reagent-grade product family are assigned according to package volume, closure liner material, and stabiliser status. Common suffix identifiers include DCM-RG-1L-A for amylene-stabilised 1 L amber glass, DCM-RG-1L-U for unstabilised 1 L amber glass, DCM-RG-4L-PTFE for a 4 L PTFE-lined cap, and DCM-RG-200L-PL for a 200 L phenolic-lined returnable steel drum. The solvent is defined by CAS 75-09-2, molecular formula CH2Cl2, molecular weight 84.93 g/mol, boiling point 39.6 °C at 101.3 kPa, density 1.325 g/cm³ at 20 °C, and vapour pressure 47.3 kPa at 20 °C. The controlling specification is the ACS Reagent Chemicals monograph for dichloromethane, and the product is released only after lot-specific testing.
Release assay by gas chromatography with flame ionisation detection is specified as not less than 99.5% area. Water content is controlled by coulometric Karl Fischer titration per ASTM E1064-20 to no more than 0.02% for standard lots. Residue after evaporation is determined by ASTM D1353-13 and limited to no more than 0.001%. Acidity as HCl is limited to 0.0005 meq/g by titration, and free halogens are reported as passes test under the ACS Reagent Chemicals monograph. Where a heavy metals limit applies to the monograph, the lot certificate reports the result against that limit rather than citing a nominal non-certified value.
Package liners and closures are selected to prevent water ingress and plasticiser extraction. Amber glass bottles are fitted with PTFE-faced caps, and 200 L drums are lined with phenolic coatings that reduce iron contamination to below 0.1 ppm after 30 days storage at 25 °C. Polyethylene containers are not used for extended storage because DCM permeates low-density polyethylene at a measurable rate, leading to weight loss and possible contamination by dissolved polyethylene oligomers.
Why Is Stabiliser Selection a Detector-Dependent Choice in Chromatographic Workflows?
Amylene-stabilised reagent-grade DCM contains a reactive olefin that can form alkylated degradation products under electron-capture detection, resulting in late-eluting extraneous peaks in chlorine-selective chromatograms. Unstabilised lots avoid this interference but are more sensitive to oxidative chloride formation during storage. In pesticide residue extraction, EPA Method 3520C permits methylene chloride as the extraction solvent; however, the analyst validates each lot through a solvent blank concentrated 1000-fold before use with GC-ECD or GC-NPD systems. A stabiliser content below 50 ppm is usually indistinguishable from baseline noise under splitless injection, whereas technical-grade amylene loads above 100 ppm may generate a solvent expansion peak and elevated baseline at high injection volumes.
The selection of amylene-stabilised versus unstabilised grade also affects extract derivatisation. In methods using acidified sodium sulfate or activated silica gel, the olefinic stabiliser can react with chlorinating agents to generate halogenated artefacts that co-elute with target chlorinated pesticides. A stabiliser-free lot is therefore specified when the downstream clean-up uses 10 g activated silica gel in a 20 mm column and the final extract is concentrated to 0.5 mL for GC/MS-SIM analysis. Published data for this specific configuration is limited, but method blanks are used to verify artefact absence before sample batch release.
In liquid-liquid extraction of aqueous samples, the higher density of DCM allows phase separation as the lower layer. A 2 L borosilicate separatory funnel with PTFE stopcock is charged with 1 L of sample and 300 mL of reagent-grade DCM; the mixture is shaken for 2 min with venting after each inversion. The settled DCM phase is passed through 20 g of anhydrous sodium sulfate in a 30 mm glass chromatography column and concentrated in a 20 L rotary evaporator with a -5 °C condenser and 40 °C water bath. The relationship between solvent volume and nonvolatile residue is critical: 0.001% residue after evaporation corresponds to 10 mg/L nonvolatile material. Concentrating 1 L to 1 mL yields 10 mg/mL dry-film equivalent, which is sufficient to foul injection liners and bias quantitation if the final extract is not filtered through a 0.45 µm PTFE syringe filter.
The high vapour pressure imposes a limit on manual pouring operations: local exhaust ventilation with a face velocity of 0.5 m/s at the operator station is used to maintain airborne concentrations below the 50 ppm ACGIH TLV-TWA. Continuous monitoring with a photoionisation detector calibrated to isobutylene is not sufficient for DCM because the response factor is low; a halogen-specific detector or colorimetric tube calibrated to 10–500 ppm is required. This operational boundary is independent of product purity and applies equally to reagent, HPLC, and technical grades.
Thermophysical Property Set and Specification Limits at 20 °C
The tabulated values below are used for evaporation rate calculations, condenser sizing, and solvent transfer pump selection. All values are at the indicated temperature and pressure; lot-specific certificates do not repeat these physical constants unless a customer-defined specification requires a densitometer or refractometer entry.
| Property | Value | Condition or Basis |
|---|---|---|
| Molecular weight | 84.93 g/mol | Calculated from molecular formula |
| Boiling point | 39.6 °C | 101.3 kPa |
| Freezing point | -96.7 °C | 101.3 kPa |
| Density | 1.325 g/cm³ | 20 °C |
| Vapour pressure | 47.3 kPa | 20 °C |
| Refractive index | 1.4242 | 589 nm, 20 °C |
| Water solubility | 1.32 g/100 g | 20 °C |
| Dielectric constant | 8.93 | 25 °C |
| Polarity index | 3.1 | Snyder scale |
In Soxhlet extraction of semivolatile organics from particulate matrices, a 500 mL round-bottom flask is charged with 250 mL of reagent-grade DCM and fitted with a 30 mm cellulose thimble. The siphon chamber is maintained at the solvent boiling point, and the cycle rate is typically 6–8 cycles/h with a 250 W heating mantle. The low residue after evaporation of 0.001% reduces extractable blank contamination to below 0.01 µg/mL for GC-ECD when the final extract is concentrated to 1.0 mL under a dry nitrogen stream in a 40 °C block heater. Silica gel or Florisil clean-up is still required for matrices with high sulfur content because the solvent does not remove elemental sulfur from the extract.
For method blanks, the same lot of reagent-grade DCM is used throughout the entire extraction batch. Changing lots without revalidating the method blank can introduce a false positive for halogenated compounds in GC-ECD at detection levels below 0.005 µg/mL. This lot-lock practice is standard in laboratories accredited under ISO/IEC 17025:2017 clause 7.4, where solvent blanks are part of the technical records.
Residue Accumulation Raises Background Signal When Solvent Is Recycled
When recovered DCM is returned to the same rotary evaporator without distillation, nonvolatile residue from sample matrices accumulates in the boiling flask. In a 20 L rotary evaporator operated at 150 mbar and 40 °C, batch audits show that the first recycle can raise residue after evaporation from 0.001% to 0.003–0.008% depending on the suspended solids load of the extract. A 0.45 µm prefilter before evaporation reduces this increase by removing cellulosic fines and inorganic particulates. Distillation through a 50 cm Vigreux column with a 5:1 reflux ratio restores the residue specification to below 0.002%, but the distilled cut must be requalified by ASTM D1353-13 before reuse in trace analysis. The operational limit is not solvent boiling temperature but the residue concentration at the final evaporative step.
When solvent recycling is performed, a re-distillation step through a 50 cm Vigreux column is preferred over simple flash evaporation because stabiliser and residue fractions have different boiling points. The distillate is collected in 250 mL fractions; the first 50 mL and final 50 mL are discarded to purge volatile degradation products and concentrate high boilers. Lot-specific residue and acidity are rechecked by ASTM D1353-13 and titration before the recycled solvent is returned to analytical service.
Because the reagent is minimally stabilised, it has a defined operational boundary in closed distillation apparatus. Thermal stress above 120 °C in the presence of water promotes hydrolysis to formaldehyde-equivalent species and HCl, and the resulting acidity changes the partition coefficient of basic analytes in liquid-liquid extraction. Jacketed glass reactors and ceramic heating blocks are preferred over open flame or resistance wire mantles that exceed 150 °C surface temperature. Published data for this specific configuration is limited, but lot-specific acidity testing after 24 h at 40 °C in borosilicate glass provides a practical stability indicator.
Technical-grade dichloromethane is sold on a broader purity basis, commonly 95–99%, and may contain a stabiliser fraction such as amylene, cyclohexane, or propylene oxide at levels above 100 ppm. It is used in paint stripping and degreasing but not in detector-sensitive workflows because stabiliser and nonvolatile residue can generate baseline drift and injector deposits. HPLC-grade DCM is additionally controlled for particulate matter, often through a 0.22 µm absolute-rated filter, and is specified for ultraviolet absorbance at 235 nm or lower. Reagent-grade DCM occupies the intermediate position: it has the ACS assay and water/residue limits required for general analytical work but is not automatically validated for every UV detector baseline requirement. The difference between grades is therefore not total chlorinated solvent content alone; it is the combination of water, residue, stabiliser, acidity, and particulate specifications that determines suitability for a given detector and extraction train.
| Parameter | Reagent grade | HPLC grade | Technical grade | Test method |
|---|---|---|---|---|
| Assay by GC-FID | ≥ 99.5% | ≥ 99.9% typical | 95–99% | USP <621> |
| Residue after evaporation | ≤ 0.001% | ≤ 0.0005% typical | not usually controlled | ASTM D1353-13 |
| Water | ≤ 0.02% | ≤ 0.02% | not usually controlled | ASTM E1064-20 |
| Particulate filtration | not specified | 0.22 µm typical | not specified | supplier filter rating |
| Stabiliser | none or ≤ 50 ppm amylene | none or specified | 100–500 ppm stabiliser typical | GC-FID |
For headspace gas chromatography, the lower water content of reagent and HPLC grades reduces the split of target volatiles into the gas phase. Technical DCM with uncontrolled water can alter split ratios and shift retention times for early-eluting halocarbons. A solvent drying step over molecular sieves 3A for 12 h can reduce water to below 0.005%, but the sieves must be activated at 300 °C for 4 h before use. After drying, the solvent is not returned to the original bottle; it is stored in a 1 L Schott flask fitted with a PTFE stopcock.
The residue test is not a substitute for particle counting. Reagent-grade DCM may contain submicrometre particles that pass visual inspection and residue after evaporation. If the solvent is used for preparative gel permeation chromatography with 5 µm column frits, filtration through a 0.22 µm fluoropolymer membrane is applied immediately before the pump inlet. This avoids pressure excursions above 180 bar on standard HPLC systems when DCM is blended with polar modifiers.
When Reagent-Grade DCM Is Substituted for Technical Solvent in Gravimetric Tests
In polymer dissolution for dilute-solution viscosity work, the reagent is used to dissolve 0.1000 g of resin in 25.0 mL at 25 °C with magnetic stirring in a 50 mL glass vial. The lower residue after evaporation prevents measurable bias in a gravimetric finish: at 0.001% residue, 25 mL contributes 0.25 mg nonvolatile matter, which is within the 0.1 mg readability of a four-place analytical balance. In contrast, technical DCM with 0.005% residue contributes 1.25 mg over the same volume, a fivefold increase that is unacceptable for determination of low-ash polymer residues. Dilute-solution viscosity is measured according to ASTM D2857-22, and the solvent blank is filtered through a 0.45 µm PTFE membrane before use. Contact with amine-cured epoxy resins is avoided because the chlorinated solvent may extract unreacted amine hardener and produce haze in the final solution.
Compliance documentation is issued as a lot-specific certificate containing actual assay, water, acidity, residue, and free halogen results. The certificates are retained for 5 years and are traceable to the ACS Reagent Chemicals monograph and the instrument methods listed above. The product is not sold as a food-contact solvent; if the solvent is used in food-related extraction, residual solvent levels in the final article must be validated under USP <467> or equivalent national limits by the user. For high-humidity sites above 60% RH, containers are conditioned in a desiccator before opening to reduce atmospheric water ingress.
