| HS Code | 241772 |
| Product Name | Water Drainage Enzymes |
| Primary Function | Enzymatic breakdown of organic waste, fats, oils, and grease in drains |
| Physical Form | Liquid concentrate |
| Color | Clear to light amber |
| Odor | Earthly or mild scent |
| Ph Value | 6.5 to 8.5 |
| Specific Gravity | 1.0 to 1.1 at 25°C |
| Solubility | Fully miscible in water |
| Biodegradability | Readily biodegradable |
| Shelf Life | 12 months from manufacture date |
| Storage Requirements | Store in a cool, dry place away from direct sunlight |
| Safety Properties | Non-toxic, non-corrosive, and safe for pipes and septic systems |
As an accredited Water Drainage Enzymes factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | A sturdy 1-gallon bottle with child-resistant cap, containing liquid Water Drainage Enzymes for breaking down organic waste in pipes. |
| Container Loading (20′ FCL) | Water Drainage Enzymes are packed in sealed drums/bags, loaded into a 20′ FCL, secured and protected from moisture. |
| Shipping | Water Drainage Enzymes are shipped in sealed, leak-proof containers to prevent spills and moisture exposure. They are non-hazardous under standard transport regulations, but we recommend ambient temperatures, avoiding extreme heat or freezing. Deliveries use standard ground freight with tracking, ensuring safe, timely arrival for commercial or residential use. |
| Storage | Store Water Drainage Enzymes in a cool, dry, well-ventilated area, away from direct sunlight and heat sources. Keep the container tightly sealed to prevent moisture absorption and contamination. Avoid contact with strong acids, alkalis, or oxidizers. Ensure clear labeling and follow local regulations for safe handling and disposal. |
| Shelf Life | Shelf life: 12 months when stored tightly sealed in a cool, dry place, protected from sunlight and moisture. |
Municipal wastewater plants that process thickened waste activated sludge through mesophilic anaerobic digestion at 35–37°C and 15–20-day solids retention time generate a digester filtrate whose extracellular polymeric substances are enriched in protein and α-linked polysaccharide. When a water drainage enzyme preparation containing endo-cellulase and alkaline protease activity is injected into the filtrate line upstream of the polymer mixing ring, the addition ratio is typically set between 0.5 mg/L and 6 mg/L of enzyme protein, or between 0.5 kg/t and 1.5 kg/t of digester dry solids. Bench-scale dose selection uses APHA 2710G capillary suction time, a 500-mL sludge aliquot, and rapid mixing at 300 rpm for 60 s followed by slow mixing at 50 rpm for 10 min. The downstream separation equipment is usually a high-solids scroll decanter centrifuge with polymer dosing at 0.15–0.35% active polymer solution and a centrate discharge line monitored for total suspended solids. Enzyme-treated sludge cake is dewatered to 18–25% total solids and must meet 40 CFR Part 503 pathogen and vector attraction reduction requirements before land application; total solids in the cake are measured by EPA Method 1684. In plants that observe benchtop capillary suction time improvement but no full-scale correlation, the relevant limitation is that polymer demand reduction is not transferable unless centrate total suspended solids and scroll torque are logged over at least three consecutive digester turnover periods. Published data for this specific configuration is limited.
Floor drains and offal screening channels in poultry primary processing carry protein, blood, and fat that create a viscous biofilm layer in collection sumps and equalization tanks. A liquid enzyme preparation with protease and lipase activity is metered into the combined drain stream at 5–25 g/m³ wastewater flow, or into the DAF sludge at 0.2–0.8 kg/t DAF solids, with pH maintained between 5.5 and 8.0 and temperature between 20°C and 38°C. The holding time before dissolved air flotation is 4–8 h; hydrolysis of insoluble protein reduces the load on the DAF polymer and lowers the residual n-hexane extractable material measured by EPA Method 1664B. Effluent is regulated under 40 CFR Part 432, and sanitation in processing areas follows 9 CFR requirements; enzyme dosing is not a substitute for SSOP or HACCP controls. The downstream process employs a balance tank with submersible mixer, a whitewater pump with air saturator at 0.02–0.06 air-to-solids ratio, and a skimmings auger that transfers float solids to rendering. The terminal products are DAF float skimmings with recoverable protein and tallow, and clarified wastewater discharged to municipal sewer under the facility categorical permit.
Textile finishing mills that run cotton and cotton-blend woven goods through size boxes use α-amylase in the desizing bath at 0.5–2.0 g/L or 0.1–0.3% on weight of fabric, depending on size composition and squeezer pickup. The desizing step is operated at 60–90°C for thermostable α-amylase, with steam injection in the pad-batch or steam-box stage and a knife-over-roll washing train whose first two compartments are held at 50°C. The enzyme cleaves starch size into low-viscosity dextrins, and the resulting washwater passes through a rotary wedge-wire screen before reuse or discharge. Drainability of the screen is governed by starch viscosity rather than pH, and the Schopper-Riegler drainability test ISO 5267-2:2011 can be used to monitor filtrate behavior. Compliance for wastewater discharge is checked against the Zero Discharge of Hazardous Chemicals ZDHC Wastewater Guidelines and relevant national permits; enzyme formulations are expected to be free of restricted substances on the ZDHC MRSL. The finished product is desized woven fabric with residual size below 0.5 g/kg fabric, and the recovered screen solids are a starch-rich by-product that may be routed to anaerobic treatment.
Mechanical pulp and recycled fiber mills that run screw presses and twin-wire presses on sludge and furnish streams observe drainage loss when hemicellulose and fines form a hydrated gel around the press screen. A cellulase-hemicellulase preparation is dosed into the press feed tank at 0.1–0.5 kg/t dry solids, with pH 6.0–7.5 and temperature 45–55°C; reaction time before pressing is 30–90 min. The enzyme activity reduces the water-binding capacity of the fines fraction, but it cannot compensate for presses operating outside the design hydraulic loading. The process uses a screw press with perforated screen basket and internal cone pressure, or a twin-wire press with gravity and pressure zones; pressate is returned to the whitewater loop. Canadian standard freeness under TAPPI T 227 or ISO 5267-2:2011 is the relevant drainability parameter. Effluent from the mill remains subject to 40 CFR Part 430 or the equivalent national permit, and enzyme addition does not alter the requirement to monitor BOD5 and suspended solids. Terminal products are dewatered sludge cake at 35–50% dry solids for mill fuel or land application, and clarified pressate recycle water.
Municipal lift stations and commercial grease trap networks accumulate calcium-fatty acid deposits on pump volutes, check valves, and wet well walls. A lipase-protease blend with lipase activity not less than 1,000 FIP U/g is dosed into the wet well or grease trap at 50–500 mL/m³ of daily flow, or in grease traps at 100–500 mL per 1,000 L trap volume per day, with sufficient mixing to avoid short-circuiting. The required contact time is 12–24 h because hydrolysis occurs at the biofilm-water interface, not in free solution; enzyme addition does not replace pumping. Effluent limits for oil and grease rely on EPA Method 1664B or local sewer use ordinances, and in Europe the enzyme preparation may be assessed under Detergent Regulation (EC) No 648/2004 for labeling of enzyme activity. The downstream process is the normal pump station or gravity sewer, with enzyme solution injected by a peristaltic metering pump through an injection quill into the force main or trap inlet. Terminal products are pump station effluent within discharge limits, reduced frequency of vacuum truck removal and maintenance, and retained floatable FOG that is collected by the hauler.
For decentralized wastewater systems showing effluent ponding over the infiltrative surface, drainage enzyme treatment targets the biomat polysaccharide matrix that reduces soil pore water velocity. A dry enzyme preparation is mixed with a carrier and dosed into the tank outlet at 1–2 kg per 4,000 L tank volume per quarter, after the tank has been pumped and inspected; liquid formulations are dosed at 500 mL per 4,000 L per month. Enzyme activity requires temperature above 18°C and pH between 6.5 and 8.5; below 10°C activity is negligible. The percolation field hydraulic function is measured by ASTM D2434-19 soil permeability and by ponding depth in observation ports. Compliance for onsite systems is referenced to NSF/ANSI 40 for residential wastewater treatment units and state or county onsite wastewater codes; enzyme application does not remove the need to verify tank sludge accumulation and pump-out intervals. The terminal product is the restored infiltrative surface receiving septic tank effluent, and the system returns to unsaturated flow; scum and sludge remain in the tank for scheduled pump-out.
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Water Drainage Enzymes is a formulated multi-enzyme system supplied as WDE-100, WDE-250, and WDE-500. The preparation is designed for organic deposit control in sanitary drainage, grease interceptor, lift-station wet well, and septic-system applications. The formulation combines subtilisin-type protease, α-amylase, lipase, cellulase, and urease fractions with a nonionic alcohol ethoxylate carrier and buffer salts. The carrier is screened against OECD 301B ready biodegradability; QC release tests include ASTM D1293-18, ASTM D4052-22, and ASTM D2196-20. The operating window is pH 6.5–8.5 and temperature 20–50 °C. The product is not intended for inorganic scale removal, and it does not restore flow in fully occluded pipes.
The three models differ by delivery form. WDE-100 is a stabilized aqueous liquid for metering-pump injection. WDE-250 is a non-dusting granule for manual dosing in floor drains. WDE-500 is a thixotropic suspension for high-fat grease interceptors where settleable solids are managed by mechanical pumping. Release specifications are model-specific, and the liquid and suspension models are tested for viscosity because peristaltic pump delivery at 20 °C deviates from diaphragm-pump calibration by up to 4 % when viscosity exceeds 300 mPa·s.
Protease activity is specified as minimum release titre using the Food Chemicals Codex protease assay. The protease component cleaves peptide bonds in egg, meat, dairy, and blood residues; this is the primary mechanism for gelatinous drain film reduction. Amylase acts on α-1,4-glycosidic bonds in gelatinized starch from rice, pasta, and potato waste. Retrograded starch films from deep-fry operations are less susceptible to enzymatic hydrolysis and may require mechanical brushing or extended contact times of 60–120 min. Lipase is interfacially active and hydrolyses triglyceride ester bonds to free fatty acids and glycerol, reducing the cohesive grease layer in interceptor baffles. Cellulase degrades β-1,4-glycosidic bonds in vegetable fibre. Urease hydrolyses urea to ammonia and bicarbonate, producing a mild pH increase in trapped urine deposits. Activity is not cumulative; enzymes degrade organic substrate and are consumed or denatured, so maintenance dosing is required.
Thermal half-life data under accelerated storage show that WDE-100 retains ≥ 85 % of labelled protease activity after 12 months in closed HDPE containers at 25 °C. At 50 °C, protease activity falls to 50 % within 6–8 h in a 1 % aqueous solution. This Arrhenius behaviour constrains continuous exposure to 50 °C; effluent above 60 °C must be tempered before injection. The pH stability boundary is pH 5.0–9.5; below pH 5.0, protonation of the catalytic serine residue in subtilisin-family proteases reduces turnover number by more than one order of magnitude.
Enzyme activity is strongly concentration-dependent. At protein film thickness below 0.5 mm, substrate diffusion limits hydrolysis, so contact time must be extended or dosing frequency increased. Lipase activity is restricted by oil-water interfacial area; in a quiescent interceptor, the top 2 mm of a grease mat is the primary reaction zone. WDE-500 therefore includes an emulsifier-surfactant package that reduces free oil droplet diameter to 20–50 µm under turbulent mixing, increasing accessible interfacial area by approximately one order of magnitude relative to non-emulsified grease.
Table 1 lists release limits applied to production lots. Density and pH are measured for every batch. Viscosity is measured for liquid and thixotropic suspension models because it directly affects pump selection and hold-up in low-flow metering lines. The WDE-250 granule is characterized by bulk density rather than liquid density; the granule is formulated with a moisture-barrier system to limit caking at relative humidity up to 60 %.
| Parameter | WDE-100 | WDE-250 | WDE-500 | Method |
|---|---|---|---|---|
| Physical form | Stabilized aqueous liquid | Non-dusting granule | Thixotropic suspension | Visual inspection |
| Density | 1.05–1.10 g/mL | 0.60–0.75 g/cm³ bulk | 1.02–1.08 g/mL | ASTM D4052-22 / ASTM D7481-18 |
| pH, 1% aqueous | 7.0–8.5 | 6.8–8.0 | 7.0–9.0 | ASTM D1293-18 |
| Viscosity at 25 °C | 50–150 mPa·s | Not applicable | 200–600 mPa·s | ASTM D2196-20 |
| Protease activity | ≥ 100,000 U/mL | ≥ 200,000 U/g | ≥ 80,000 U/mL | Food Chemicals Codex protease assay |
| Amylase activity | ≥ 20,000 U/mL | ≥ 50,000 U/g | ≥ 15,000 U/mL | Food Chemicals Codex amylase assay |
| Lipase activity | ≥ 5,000 U/mL | ≥ 15,000 U/g | ≥ 10,000 U/mL | Food Chemicals Codex lipase assay |
| Storage window | 5–35 °C | 5–35 °C, RH < 60 % | 5–35 °C | Manufacturer stability protocol |
WDE-250 powder is packaged in 1 kg and 10 kg poly-lined foil pouches. Opened containers should be used within 30 days at relative humidity < 60 %. WDE-500 requires re-dispersion if the supernatant layer exceeds 5 % of total volume after prolonged storage; a low-shear paddle mixer at 50–100 min⁻¹ for 15 min restores the suspension. Freezing of WDE-100 at temperatures below -2 °C may produce phase separation, and thawed material should not be used for metering calibration until the liquid is restored to 20 °C and mixed by recirculation for 10 min.
| Standard or regulation | Relevant parameter | Application boundary |
|---|---|---|
| OECD 301B | Ready biodegradability of soluble organics | Surfactant carrier must achieve > 60 % BOD/COD within 28 d; enzyme proteins are not represented by BOD/COD because of rapid adsorption to biomass in activated sludge |
| ASTM D1293-18 | pH of water | QC release for 1 % aqueous solutions |
| ASTM D4052-22 | Density by digital density meter | WDE-100, WDE-500 |
| ASTM D2196-20 | Rotational viscosity | WDE-100, WDE-500; method influences pump calibration |
| ASTM D471-16a | Elastomer swelling | EPDM and silicone tubing compatibility |
| ISO 10707:1994 | Closed bottle aerobic biodegradability | Sewer discharge compatibility evaluation |
In high-load grease interceptors with influent grease loading above 200 g/m³ per day in a 500 L concrete tank, passive dosing from a manual pour-in often fails to contact the floating grease mat because lipase remains in the aqueous phase. In these systems, WDE-500 is introduced upstream of the inlet baffle at 500–1,000 mL/week with a peristaltic pump controlled by a 4–20 mA flow-paced signal. The injection point is placed at least 3 pipe diameters upstream of the interceptor to provide turbulent mixing. EPDM pump tubing is preferred; silicone tubing swells by 8–12 % after 7 days exposure to the nonionic surfactant carrier when tested according to ASTM D471-16a. Viton seals are not recommended for WDE-100 service because of detergent-induced permeation. Field comparisons between enzyme dosing and caustic saponification show that enzyme hydrolysis leaves free fatty acids and glycerol, which remain biodegradable in municipal activated sludge, whereas caustic use above pH 13 can saponify fats into calcium soaps that harden in downstream pipes. Acidic pipe openers at pH < 1 are not equivalent in this application because they do not hydrolyse the protein-starch matrix that binds grease deposits and may accelerate concrete interceptor corrosion.
For a 250 L grease interceptor receiving a daily effluent flow of 1,000 L, a single WDE-500 dose of 500 mL after mechanical pumping produces a measurable free fatty acid increase within 4 h when temperature is maintained at 30–40 °C. Published data for high-solid food waste mixtures with total suspended solids above 1,500 mg/L remain limited because hydrolysis rates are strongly influenced by interfacial area and surfactant concentration. In such matrices, jar-scale treatability testing under ASTM D1293-18 pH control is used to establish the minimum effective dose before line installation.
Bacillus-based bioaugmentation products require viable cells, a lag phase of 6–48 h, and dissolved oxygen; enzymes do not require oxygen and act within 15–120 min. However, enzymes lack self-replication and cannot colonize surfaces. Bacterial products may establish a biofilm and provide longer-lasting degradation if conditions permit. In anaerobic septic systems with dissolved oxygen below 0.5 mg/L, Bacillus metabolisms are slower; WDE-100 can hydrolyse settled organic solids but cannot replace anaerobic digestion capacity or reduce total biosolids volume.
Floor drains in meat processing are dosed with WDE-250 at 100 g per drain per day, followed by 250 mL of water at 20–30 °C. Hot water above 50 °C or sanitizer chases are not used because they denature or inhibit the enzyme fractions. In dairy plants, metering pumps inject WDE-100 at 0.25–0.5 % v/v into wastewater at 2–5 L/h per 150 mm line. For lift stations, WDE-100 is injected at 500 mL per 1,000 L of daily flow upstream of the wet well, with the drop leg located below the water surface to reduce foaming.
Accelerated stability trials in stirred water baths at 40 °C, 50 °C, and 60 °C demonstrate log-linear protease decay. At 50 °C, the half-life in a 1 % solution is 6–8 h; at 60 °C, it is 15–20 min. Continuous recirculation through water heater loops above 50 °C is outside the specified operating range. Dosing must occur downstream of condensate tempering valves and heat recovery units. Protein denaturation is irreversible, and re-cooling does not restore activity. In hard water of 300 mg/L calcium carbonate, the WDE-100 concentrate remains clear at 20 °C; at 40 °C, calcium-induced phase separation occurs after 24 h in steel-cased dosing skids. This observation is based on manufacturer stability records for boiler blowdown drains; published data for high-silica waste streams is limited.
Quaternary ammonium disinfectants at 200 ppm benzalkonium chloride reduce protease activity by > 70 % within 1 h. Sodium hypochlorite at 500 ppm free chlorine completely inactivates amylase and lipase. Drains receiving sanitizer slug loads must be flushed with 20 L of water before enzyme dosing. Peroxide and peracetic acid oxidizers are not compatible with this formulation. The product is a maintenance chemistry, not an emergency opener for fully blocked lines; if water is standing, mechanical rodding or hydrojetting is required before enzyme application.