| HS Code | |
| Product Name | Carbon Disulfide |
| Chemical Formula | CS2 |
| Cas Registry Number | 75-15-0 |
| Molecular Weight | 76.14 g/mol |
| Appearance | Colorless liquid |
| Odor | Sweet, ethereal, chloroform-like; commercial grades may have foul odor |
| Density | 1.263 g/cm3 at 20 °C |
| Melting Point | -111.6 °C |
| Boiling Point | 46.3 °C |
| Flash Point | -30 °C (closed cup) |
| Autoignition Temperature | 90 °C |
| Explosive Limits | 1.3–50% by volume in air |
| Solubility In Water | 0.2 g/100 mL at 20 °C |
| Vapor Pressure | 48 kPa at 20 °C |
| Refractive Index | 1.627 at 20 °C |
| Viscosity | 0.363 mPa·s at 20 °C |
| Dipole Moment | 0 D |
| Un Number | 1131 |
As an accredited Carbon Disulfide factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | Carbon disulfide packaged in 1 L amber glass bottles with PTFE-lined caps, sealed, and labeled flammable, toxic, and health hazard. |
| Container Loading (20′ FCL) | Carbon Disulfide (UN1131) loaded into a 20′ FCL container, securely stowed, ventilated, segregated, and placarded per IMDG dangerous goods regulations. |
| Shipping | Carbon disulfide (UN 1131, Class 3, subsidiary 6.1, PG I) is an extremely flammable, toxic liquid. Ship in approved, tightly closed containers under inert gas if required, away from heat, sparks, oxidizers, and ignition sources. Use proper flammable/toxic placards, PPE, and emergency response procedures. Consult applicable transport regulations. |
| Storage | Store carbon disulfide in a cool, dry, well-ventilated, fire-resistant area away from heat, sparks, flames, and oxidizers. Keep containers tightly closed, grounded, and bonded; use explosion-proof equipment and impermeable secondary containment. Protect from light and static electricity. Maintain minimal inventory and segregate from incompatible materials, including amines and alkali metals. Follow local regulations for flammable, toxic liquids. |
| Shelf Life | Carbon disulfide: indefinite shelf life if stored sealed, cool, dark, dry, away from ignition; purity may degrade under poor conditions. |
Viscose staple production consumes roughly 70–75% of global carbon disulfide demand in the fibre segment. Dissolving pulp with an alpha-cellulose content above 92% is steeped in 17.5–19.0% sodium hydroxide at 45–55°C for 30–45 min; the alkali cellulose is pressed to a press factor of 2.8–3.0, shredded, and oxidatively aged at 28–32°C until the degree of polymerisation declines to 270–350. Ageing time is adjusted batch-to-batch because pulp intrinsic viscosity and hemicellulose content shift the depolymerisation rate; over-aged crumb produces dope with weak gel strength, while under-aged crumb yields filtration pressure rises above 0.8 MPa in the primary viscose filter. Carbon disulfide is then metered into the xanthator at 30–34% by weight of alpha-cellulose, with the reaction held at 20–28°C by jacket water and vacuum recovery. The target gamma value for regular staple is 0.45–0.55; higher CS2 doses increase solubility but also elevate free CS2 in the dope and the by-product load in the spinning room.
Xanthated crumb is dispersed in dilute sodium hydroxide at 5–12°C in a vacuum dissolver equipped with a high-shear impeller, forming dope with 8.5–9.3% alpha-cellulose, 5.0–5.8% sodium hydroxide, and sulphur content 2.2–2.6%. The dope is ripened until the ammonium chloride number reaches 10–16 mL of 10% NH4Cl; this is a critical control point because the ripening index determines coagulation response in the acid bath. Filtration through 20–30 µm stainless steel or cotton fibre media is followed by deaeration under −0.09 MPa gauge vacuum. The filtered dope is then extruded through spinnerets with hole diameters 70–90 µm into a coagulation bath containing 95–110 g/L H2SO4, 210–240 g/L Na2SO4, and 0.5–1.5 g/L ZnSO4 at 48–52°C. The zinc ion modulates the coagulation rate; concentrations above 2.0 g/L in regular staple lines are avoided in many plants because they accelerate skin formation and require closer spin-bath acid control. Stretch ratios from 12–20% are applied in the plastic state, after which the tow is cut and washed.
Carbon disulfide and hydrogen sulfide are released in the spinning and regeneration step, and the gas collection system typically operates under a permanent negative pressure of 100–200 Pa in the spinneret hood. The air stream is sent to a CS2 recovery train using activated carbon adsorption or condensation, with recovered CS2 returned to the xanthation step. Because carbon disulfide has a lower explosive limit of 1.3 vol% and an autoignition temperature near 90°C, electrical installations within the classified zone are specified under ATEX 2014/34/EU as Group II, Category 2G, temperature class T6. Occupational exposure in the spinning room is managed below the OSHA 8-hour PEL of 20 ppm and, where AIHA or corporate limits are applied, below the ACGIH TLV-TWA of 1 ppm. In closed viscose lines, the main operational boundary is not cellulose solubility but gas-phase CS2 measurement: a rising concentration in the spinneret hood above 5,000 ppm triggers automatic reduction of xanthator batch charging and higher extraction airflow, because the LEL monitor alarm set point is commonly fixed at 20% of LEL, equivalent to 2,600 ppm.
| Control parameter | Value / limit | Reference or design rule |
|---|---|---|
| Lower explosive limit of CS2 in air | 1.3 vol% (13,000 ppm) at 25°C | NFPA 325 |
| Autoignition temperature | 90°C | ASTM E659 |
| OSHA 8-hour TWA PEL | 20 ppm | 29 CFR 1910.1000 Table Z-2 |
| ACGIH TLV-TWA | 1 ppm | ACGIH TLV documentation for carbon disulfide |
| ATEX equipment category for CS2-processing enclosures | Group II, Category 2G, temperature class T6 | Directive 2014/34/EU |
| Spinning hood LEL alarm set point | 20% LEL = 2,600 ppm | IEC 60079-10-1 zone design |
Because cellophane casting uses the same cellulose xanthate chemistry, the carbon disulfide demand per tonne of film is similar to viscose staple, but the downstream equipment and process controls differ. The viscose for cellophane is prepared with a carbon disulfide charge of 28–35% on alpha-cellulose to achieve a gamma value near 0.45–0.55, and the dope is filtered to a higher degree because gel-induced pinholes are immediately visible in the film. Casting is carried out through a slot die with a gap of 0.5–1.0 mm into a coagulation bath containing 120–150 g/L H2SO4 and 18–25% Na2SO4 at 35–45°C. After coagulation, the gel film passes through regeneration baths, dilute sodium hydroxide desulphurisation at 60–70°C, and hypochlorite bleaching. The film is then plasticised in a bath containing 6–12% glycerol and dried in multi-zone hot air ovens at 70–110°C. Carbon disulfide and hydrogen sulfide released from the casting and regeneration sections are extracted by hoods and sent to recovery.
Food-contact cellophane sold into packaging is controlled under cellophane-specific provisions where national legislation references 21 CFR 177.1200 for cellophane, and in the EU under framework regulation 1935/2004 with migration limits for plasticiser additives where applicable. Production records for direct food packaging typically retain residual carbon disulfide, glycerol, and desulphurisation by-product analytical data to demonstrate that the finished film does not impart odour or taste. The main process limitation in cellophane casting is the acid-bath temperature: above 46°C, regeneration accelerates before the film has developed sufficient tensile strength on the first take-up roll, causing web breaks and uneven film gauge. Below 32°C, regeneration slows and produces a film with excessive gel swell and poor optical clarity. Published data for CS2 emissions from standalone cellophane lines is limited because many older cast-film facilities have been replaced by biaxially oriented polypropylene lines.
For sulphide mineral flotation collectors, the reaction sequence begins with carbon disulfide addition to a C2–C5 alcohol and sodium hydroxide. In a typical 5 m³ jacketed batch reactor, ethanol is charged with 40–50% aqueous NaOH to form the alkoxide; carbon disulfide is metered beneath the liquid surface over 2–4 h at 8–12°C. The molar feed ratio is normally held at 1.00:1.05 NaOH:CS2 because a slight CS2 excess suppresses hydroxide-driven side reactions while leaving negligible unreacted carbon disulfide after the finishing step. The reaction is strongly exothermic, and the cooling system must be sized for peak heat load during the CS2 feed period rather than average batch duty. Reactor temperature excursions above 25°C cause loss of CS2 to the vapour phase and shift the product toward carbonate and trithiocarbonate by-products. After the addition, the batch is stirred for an additional 30–60 min, and the crude sodium ethyl xanthate slurry is centrifuged or vacuum dried to a free-flowing powder.
In flotation circuits, dry xanthate is makedown to 5–10% aqueous solution and metered at 10–60 g/t of ore in rougher banks, with higher doses up to 100 g/t applied to oxidised or pyrrhotite-bearing ores. The collector adsorbs on chalcopyrite, galena, and sphalerite surfaces after conditioning at pH 8–11; lime is used to depress pyrite where selective copper or lead concentrate is required. The corresponding end products are concentrates with copper grades of 20–30% Cu, lead grades of 50–65% Pb, and zinc grades of 45–55% Zn, depending on ore head grade and flotation circuit residence time. Xanthate stability is a critical boundary condition: below pH 6, hydrolysis generates carbon disulfide, hydrogen sulphide, and alcohol, so storage of makedown solution beyond 8 h or use in acidic pulp is avoided. Flotation plants handling xanthate solutions are required to monitor ambient CS2 around the makedown and reagent storage areas; the ACGIH TLV-TWA of 1 ppm for carbon disulfide is used as the design target for local exhaust ventilation at the makedown hood.
From an audit perspective, xanthate production and flotation reagent selection are not governed by a single ISO standard; the relevant controls are site-level occupational exposure limits, wastewater sulphide, and hazardous area classification. Carbon disulfide storage feeding the xanthate reactor is designed as a closed nitrogen-blanketed system with water-seal conservation, and the reactor is classified as a hazardous zone under IEC 60079-10-1. The autoignition temperature of carbon disulfide near 90°C requires that the drying section be interlocked to shut down heating above 80°C surface temperature. Published engineering data for peak heat load in xanthate reactors is limited because manufacturers commonly size the cooling surface based on laboratory calorimetry scaled by the CS2 feed rate and batch inventory.
Carbon disulfide is the sulphur source for tetramethylthiuram disulfide and related dithiocarbamate accelerators used in sulphur-cured rubber. The first stage is the reaction of dimethylamine with carbon disulfide in aqueous sodium hydroxide at 10–20°C to form sodium dimethyldithiocarbamate, typically at a molar ratio of 1.00:1.05 dimethylamine:CS2 and pH 8.5–9.5; excess CS2 is stripped under vacuum before the oxidation step. The intermediate solution is present at 25–40% solids, and the endpoint is determined by iodometric titration of the dithiocarbamate anion. In the second stage, oxidation with sodium hypochlorite or hydrogen peroxide at 5–15°C couples two dithiocarbamate moieties to form the thiuram disulfide. The oxidation stoichiometry and residual amine concentration determine the dithiocarbamate-to-thiuram conversion: an unreacted dimethylamine fraction above 0.5 mol% leaves free amine in the downstream curing system and is analytically relevant because secondary amine-derived accelerators can form N-nitrosamines under certain nitrosating conditions.
The question of monosulphide formation arises during oxidation when insufficient oxidant is added or pH drifts below 6.5: the reaction can terminate at tetramethylthiuram monosulphide or leave sodium dimethyldithiocarbamate unconverted. Molar feed of sodium hypochlorite is therefore maintained at 1.0–1.2 mol oxidant per 2 mol dithiocarbamate, with redox potential monitored during feeding. The resulting tetramethylthiuram disulfide has a melting point of 155–157°C; the monosulphide by-product contains less releasable sulphur and alters vulcanization kinetics by reducing the crosslink density at equal phr. In a standard ASTM D2084 moving-die rheometer curve, replacement of 0.5 phr tetramethylthiuram disulfide by monosulphide extends t90 and lowers maximum torque, so the user specification normally includes a minimum 96% disulphide content by HPLC.
In rubber compounding, tetramethylthiuram disulfide is used as a secondary accelerator with sulphenamide primary accelerators in natural rubber and styrene-butadiene rubber compounds at 0.5–2.0 phr, or as a sulphur donor at 2.5–4.0 phr in low-free-sulphur or semi-EV cure systems. A typical NR tread compound will use 3–5 phr zinc oxide, 1–2 phr stearic acid, 1.0–1.8 phr sulphur, 0.8–1.2 phr N-tert-butyl-2-benzothiazole sulphenamide, and 0.1–0.3 phr tetramethylthiuram disulfide; curing at 150–160°C in an injection press with clamp force above 1,000 kN results in t90 values of 3–6 min. Because tetramethylthiuram disulfide is itself a nitrosatable secondary amine derivative, its use in rubber articles with food-contact or childcare exposure is restricted in certain markets; formulators may replace it with zinc dibenzyldithiocarbamate or dithiophosphate accelerators when compliance with EU Directive 93/11/EEC nitrosamine release limits is required.
In methylamine-based soil fumigant synthesis, carbon disulfide addition is conducted under alkaline aqueous conditions to produce metam sodium. The reaction of methylamine with carbon disulfide in sodium hydroxide is held at 0–10°C, with pH maintained above 11 during the CS2 feed; the concentrated solution is stabilised as a 32–42% aqueous product and is applied as a soil fumigant. When injected into moist soil at 15–25 cm depth, metam sodium decomposes to methyl isothiocyanate, the active fumigant, with application rates in the range 30–80 gal/acre depending on soil type, temperature, and target pest. Equipment for row-crop soil injection uses positive-displacement pumps and ground-following coulter shanks; field application is regulated under national pesticide laws such as FIFRA in the United States and Regulation 1107/2009 in the European Union where the active substance is authorised. Buffer zones and vapour drift control are mandatory because methyl isothiocyanate is volatile and has a low odour threshold; workers conducting soil injection are equipped with organic-vapour respirators and quantitative fit testing.
The same dithiocarbamate chemistry supports ethylene bisdithiocarbamate fungicides such as mancozeb and metiram, produced from ethylenediamine, carbon disulfide, and metal salts. The reaction proceeds through the intermediate disodium ethylene bisdithiocarbamate, which is then complexed with zinc and manganese under controlled pH and oxidation. The dry powder is formulated as wettable powder or water-dispersible granule with 75–80% active ingredient. Application for late blight and downy mildew on potato, tomato, and vine crops is typically 1.5–3.5 kg/ha of formulated product at 7–10 day intervals, subject to pre-harvest interval restrictions. The manufacturing boundary condition is pH control during complexation: below pH 5 the dithiocarbamate intermediate decomposes to carbon disulfide, ethylenethiourea, and metal sulphides, while above pH 9 the metal complex precipitates with poor filterability and slow drying.
Aniline, carbon disulfide, and elemental sulphur are charged to a high-pressure autoclave to close the benzothiazole ring and produce 2-mercaptobenzothiazole. The reaction is carried out at 220–250°C and 5–8 MPa, with an approximate molar ratio of 1.0:1.1:1.8 aniline:CS2:sulphur; hydrogen sulphide is continuously vented through a caustic scrubber. The autoclave is constructed with high-alloy lining resistant to ammonium polysulphide corrosion, and the heating rate is controlled to avoid a runaway exotherm above 260°C. After cooling, the crude 2-mercaptobenzothiazole is extracted with dilute alkali and reprecipitated with acid to obtain technical material with purity 95–98%.
2-Mercaptobenzothiazole is then either oxidised with hydrogen peroxide to 2,2'-dithiobenzothiazole or reacted with cyclohexylamine or tert-butylamine to produce N-cyclohexyl-2-benzothiazole sulphenamide and N-tert-butyl-2-benzothiazole sulphenamide. These sulphenamide accelerators are standard primary accelerators in tyre tread and sidewall compounds at 0.8–1.5 phr, in formulations with 2–5 phr zinc oxide, 1–3 phr stearic acid, and sulphur 1.4–1.8 phr. The processing safety advantage of sulphenamides is delayed action: the accelerator complex remains dormant until the scorch induction period ends, then releases 2-mercaptobenzothiazole and amine to activate sulphur crosslinking. Scorch time measured according to ISO 6502 is typically 7–15 min at 135°C, allowing injection moulding of large tyre components without premature vulcanisation. The operational boundary in 2-mercaptobenzothiazole synthesis is hydrogen sulfide management: vent system pressure drop and scrubber pH above 12 are interlocked with the autoclave heating circuit because unscrubbed H2S release above the toxic threshold is not permissible.
In laboratory and selected fine-chemical manufacturing, carbon disulfide serves as a solvent for elemental sulphur, white phosphorus, and certain waxes or resins, particularly where a chlorinated solvent is unsuitable. The solvent use is constrained by the low boiling point of 46.2°C and high vapour pressure, so dissolution is performed in sealed vessels under nitrogen. The application is not a high-volume downstream segment; published industrial data for solvent recovery in this specific configuration is limited. Where white phosphorus is handled, safety systems are built around the pyrophoricity of the solute rather than CS2 toxicity alone. In organophosphorus synthesis, carbon disulfide is also an intermediate for selected thiocarbamates and heterocycles, but these are typically site-specific and produced to internal specifications rather than standalone merchant commodities.
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Carbon disulfide (CAS 75-15-0) is supplied as a low-boiling organosulfur liquid with molecular weight 76.13 g/mol, density 1.263 g/cm³ at 20 °C, melting point -111.6 °C, and normal boiling point 46.3 °C. Product identity is defined by grade specification rather than a universal model number; common purchasing designations are technical grade, low-benzene rayon grade, and reagent grade. The liquid has a closed-cup flash point of -30 °C, an autoignition temperature near 90 °C, and a flammability range of 1.3 vol% to 50 vol% in air. Vapour density is 2.67 relative to air, so spills produce low-lying flammable plumes. Storage and transfer are performed under nitrogen blanketing in areas classified according to IEC 60079-10-1. REACH regulation EC 1907/2006 requires exposure scenario documentation for downstream uses, and transport is governed by UN 1131, Class 3, Packing Group I.
Production of carbon disulfide from methane and sulfur occurs at 600–700 °C over an alumina catalyst, yielding carbon disulfide and hydrogen sulfide. The crude reactor effluent is cooled to 150 °C in a waste-heat exchanger, then scrubbed with an amine solvent to remove hydrogen sulfide. The crude carbon disulfide is distilled in a two-column sequence; the first column removes light sulfur compounds, and the second column produces a heart cut with a boiling range of 46.0–46.5 °C. Residual hydrogen sulfide is stripped with nitrogen to below 10 mg/kg. This route defines the main impurities: unconverted sulfur, dissolved hydrogen sulfide, and trace mercaptans. Published data on exact impurity distributions varies by producer and catalyst age; plant assays are required for process validation.
In viscose manufacturing, carbon disulfide is metered into alkali cellulose in a high-shear churn or kneader at a charge ratio of 0.30–0.35 kg CS₂ per kilogram of air-dry cellulose. The xanthation reaction is maintained at 25–35 °C; if the jacket temperature exceeds 38 °C, side-reaction formation of sodium trithiocarbonate increases and viscose filterability decreases. Industrial sigma-blade mixers with 1,000 L working volume are operated with oxygen below 1 vol% because the lower flammability limit of carbon disulfide is 1.3 vol%; nitrogen purge is regulated by an oxygen analyzer with a full scale of 0–5 vol% and a trip setpoint at 1 vol%. After xanthation, residual carbon disulfide is removed under vacuum at -70 kPa to -85 kPa gauge and recovered by indirect condensation at -10 °C. The recovered crude material is returned to the feed tank after caustic scrubbing to remove hydrogen sulfide. Equipment datasheets for closed-loop recovery systems specify regeneration efficiencies of 95–99% for this condensation step.
The normal boiling point of 46.3 °C places carbon disulfide in a narrow distillation window between deep refrigeration and steam heating. At 20 °C, vapour pressure is 297 mm Hg, equivalent to 39.6 kPa. A closed-loop distillation column separating carbon disulfide from hydrogen sulfide and sulfur compounds must keep the reboiler temperature below 60 °C and the condenser at 5–10 °C with chilled water or brine. Because the autoignition temperature is near 90 °C, a hot-oil reboiler is not used; low-pressure steam at 100–105 °C is applied only on the shell side with a maximum tube-wall temperature of 70 °C. Rupture discs on distillation vessels are set at 0.3 bar above operating pressure, and the vent line is routed to a thermal oxidizer with a continuous pilot. Column internals are specified in 316L stainless steel because copper alloys accelerate decomposition and produce copper sulfide scale.
Specification packages for low-benzene carbon disulfide used in rayon commonly set purity at ≥ 99.5% w/w by gas chromatography with flame ionization detection, water at ≤ 50 mg/kg by ASTM E1064, nonvolatile residue at ≤ 20 mg/kg by ASTM D1353-13, and benzene at ≤ 5 mg/kg by GC-MS. Bulk tank deliveries are sampled at top and bottom to detect water stratification because carbon disulfide has a water solubility of 2.16 g/L at 20 °C and free water can initiate corrosion in carbon steel piping. Road tankers for UN 1131 material are fitted with pressure-vacuum relief valves set at +0.25 bar and -0.05 bar and with dip pipes terminating within 50 mm of the tank bottom. In-line near-infrared photometers measure water at loading and offloading headers and trip the transfer pump above 100 mg/kg free water.
Carbon disulfide has the highest sulfur loading among common liquid organic sulfur carriers: 84.2% w/w sulfur, compared with 51.6% w/w for dimethyl sulfide and 68.3% w/w for dimethyl disulfide. Decomposition in hydrodesulfurization presulfiding begins at lower reactor inlet temperatures for carbon disulfide than for dimethyl disulfide; the exact onset depends on hydrogen partial pressure and catalyst composition. The lower boiling point of carbon disulfide, 46.3 °C, simplifies separation from light hydrocarbons but increases storage vapour loads. In sulfiding of naphtha hydrotreating catalysts, carbon disulfide is injected upstream of the catalyst bed, while dimethyl disulfide is often selected when a higher boiling point and lower vapour pressure are required for atmospheric storage.
| Property | Carbon disulfide | Dimethyl sulfide | Dimethyl disulfide |
|---|---|---|---|
| Sulfur content | 84.2% w/w | 51.6% w/w | 68.3% w/w |
| Normal boiling point | 46.3 °C | 37.3 °C | 109.7 °C |
| Density at 20 °C | 1.263 g/cm³ | 0.846 g/cm³ | 1.063 g/cm³ |
In naphtha hydrotreater presulfiding, carbon disulfide is introduced with the liquid feed to a fixed-bed reactor loaded with CoMo/Al₂O₃ or NiMo/Al₂O₃ catalyst. The injection rate is controlled to maintain sulfur in the liquid feed at 0.5–2.0 wt% during sulfiding, and hydrogen partial pressure is held at 2.0–3.0 MPa with a gas-to-oil ratio of 500–1,000 m³/m³. Reactor effluent hydrogen sulfide is sampled by colorimetric gas detection tubes and should rise from 0 ppm to over 1,000 ppm as breakthrough progresses. Carbon disulfide is preferred in some units because it decomposes quickly and leaves no persistent liquid sulfur residue, but its low flash point requires the injection skid to be designed for Zone 1 and to include double-block-and-bleed valves on all connections. Published data for this specific configuration is limited at the plant level due to proprietary catalyst activation schedules.
Rayon-grade carbon disulfide is specified with benzene as a marker impurity because benzene residues in viscose spinning baths can be emitted during acid regeneration. The benzene limit is commonly ≤ 5 mg/kg, and the specification also includes sulfur at ≤ 10 mg/kg, water at ≤ 50 mg/kg, and nonvolatile residue at ≤ 20 mg/kg. Gas chromatography with a sulfur chemiluminescence detector achieves a lower limit of quantitation of 0.5 mg/kg for light sulfur compounds. The product is sampled from the production column after a final condensation stage at 10 °C and passed through a 0.45 µm membrane filter before packaging. Bulk material is loaded into 316L stainless steel isotanks or carbon steel tankers with an internal phenolic lining; the lining is inspected annually by dry-film thickness measurement, and a minimum thickness of 200 µm is specified. Published data on long-term lining performance in carbon disulfide service is limited, and customers with high-purity requirements often require dedicated tank service to avoid cross-contamination.
| Parameter | Technical grade | Low-benzene rayon grade | Reagent grade |
|---|---|---|---|
| Purity | ≥ 99.0% w/w | ≥ 99.5% w/w | ≥ 99.9% w/w |
| Water | ≤ 100 mg/kg | ≤ 50 mg/kg | ≤ 20 mg/kg |
| Benzene | ≤ 50 mg/kg | ≤ 5 mg/kg | ≤ 1 mg/kg |
| Nonvolatile residue | ≤ 20 mg/kg | ≤ 20 mg/kg | ≤ 5 mg/kg |
Carbon disulfide stored in contact with air can accumulate peroxides on prolonged exposure to oxygen and ultraviolet light; sampling of long-stored material is conducted through a closed thief after purging with nitrogen and the sample is tested for peroxide by iodometric titration. Storage tanks are pad-mounted with a nitrogen pressure of 50–100 mbar and a low-pressure vacuum breaker at -20 mbar to prevent ingress of air. Copper, zinc, and their alloys are avoided in wetted parts because metal sulfides form and can accelerate corrosion; 316L stainless steel or steel with a baked phenolic lining is used. Carbon disulfide is incompatible with strong oxidizers, azides, amines, and alkali metal amalgams. It should not be stored with alkaline solutions because xanthate formation liberates heat and hydrogen sulfide. Under REACH EC 1907/2006, professional users must document use in the exposure scenario and comply with workplace exposure limits; the ACGIH threshold limit value is 1 ppm as an 8-hour time-weighted average.
Centrifugal pumps for carbon disulfide transfer use dual mechanical seals with a barrier fluid at 0.1–0.3 bar above process pressure; canned-motor or magnetically driven pumps are specified when benzene content below 5 mg/kg must be maintained. PTFE or EPDM elastomers are used in seals; nitrile rubber and natural rubber are unsuitable due to swelling and degradation. Transfer lines are sloped to a drainage sump and electrically bonded with a resistance below 10 Ω to earth. Static discharge risk is managed by limiting linear velocity to 1–2 m/s in loading operations and by using conductive hoses with internal spiral bonding.