An advanced in-situ remediation product that merges activated carbon + ZVI (BOS 100®) with slow-degrading electron donors and peptides to catalyze the degradation of chlorinated solvents.
How It Works
CAT 100 combines the proven BOS 100® platform with engineered biotechnology to create a next-generation in-situ remedy capable of degrading significantly more contaminant mass per unit dose.
Mechanism of Action:
- Contaminant Binding: Chlorinated solvents adsorb to the activated carbon matrix and contact chemically fused zero-valent iron (ZVI)
- Electron Pump: Complex carbohydrates and peptides degrade slowly, generating electrons
- Catalytic Reaction: Electrons are transferred through the carbon-iron matrix to the electrostatically bound contaminant, where it is degraded
- Iron Conservation: Unlike conventional ZVI, iron is not significantly or rapidly consumed because of electron generation and shuttling
- Iron Surface Area: The manufacturing process creates a massive iron surface dispersed throughout the AC, allowing for far greater mass removal per unit of iron
This system promotes both adsorption and catalytic reductive dechlorination, enabling sustained contaminant breakdown with fewer injections and better longevity.
Common Applications
- CVOC source zones with high mass or DNAPL
- Commingled contaminant plumes (e.g., CVOCs + petroleum)
- Sites with rebound issues post-excavation or SVE
- Regulatory-driven sites requiring aggressive, sustained action
Typical Site Types
- Aerospace and defense facilities
- Industrial solvent handling plants
- Superfund and RCRA corrective action sites
- Rail yards and maintenance depots
- Chlorinated solvent manufacturing and degreasing operations
Performance Results
CAT 100 has been deployed at sites across the United States, northern Europe, and South Africa.
- DNAPL Source Treatment: Documented >90% mass reduction in high-concentration source areas within 6–12 months
- Longevity: Active treatment effects observed 5+ years post-injection in challenging, mixed-mass sites
- Mass Efficiency: Field results demonstrate far higher degradation than stoichiometric iron demand models would predict
Product Comparison
| Feature / Spec | BOS 100® | CAT 100® | BOS 200® | BOS 200+® |
|---|---|---|---|---|
| Target Contaminants | Chlorinated solvents (TCE, PCE, DCE, VC) | CVOCs, DNAPL, mixed chlorinated solvent mass | Petroleum hydrocarbons (BTEX, TPH, LNAPL) | Complex PHC sites: LNAPL, MTBE, glycols, etc. |
| Ideal Use Cases | CVOC dissolved groundwater plumes, low-high perm zones, permeable reactive barriers (PRB) | DNAPL source zones, high-mass CVOC, mixed plumes | BTEX/LNAPL plumes, blend into backfill of excavation | LNAPL source zones, high-mass VOC, PRBs |
| Treatment Mechanism | Adsorption + abiotic reductive dechlorination (ZVI) | Adsorption + catalytic degradation + engineered bio | Adsorption + aerobic biodegradation | Adsorption + enhanced bio (aerobic & anaerobic) |
| Activated Carbon Type | Granular AC impregnated with reactive iron | Granular AC impregnated with reactive iron | Powdered activated carbon | Granular AC impregnated with reactive iron |
| Biological Degradation Component | No | Yes | Yes | Yes |
| Delivery Methods | Direct push, trench, soil mix, packer, GeoTAP | Direct push, trench, soil mix, packer, GeoTAP | Direct push, trench, soil mix, packer, GeoTAP | Direct push, trench, soil mix, packer, GeoTAP |
| Year Released | 2004 | 2016 | 2002 | 2016 |
| Projects Completed | 100+ | 50+ | 1000+ | 200+ |