Occidental Chemical Corporation - Buffalo Avenue
Other (Former) Names of Site: Hooker Chemical Co.
|EPA Identification Number:||NYD000824482|
|Facility Location:||4700 Buffalo Avenue, Niagara Falls, New York 14302
|Facility Contact Name:||James J. Czapla, (716) 278-7536|
|EPA Contact Name:||None|
|New York State Department of Environmental Conservation (NYSDEC) Case Manager:||Jeffrey E. Dietz, (716) 851-7165, firstname.lastname@example.org|
|Last Updated:||October 2009|
|Environmental Indicator Status:|| Human Exposures Under Control [PDF 274.21 KB, 31 pp] has been verified.
Groundwater Contamination Under Control [PDF 9.23 MB, 35 pp] has been verified.
The Occidental Chemical Corporation’s (OCC) Buffalo Avenue facility is located at 4700 Buffalo Avenue in Niagara Falls, New York, on the east bank of the Niagara River between Lake Erie and Lake Ontario. The plant occupies approximately 115 acres, employs about 200 people, and operates, for the most part, 24 hours a day, seven days a week. The plant produces both organic and inorganic chemicals. The major products manufactured are chlorine, caustic soda, hydrogen, and Dechlorane Plus, a chlorinated fire retardant. Hazardous wastes are generated as a result of some production activities.
Site Responsibility and Legal Instrument
Corrective action at this facility is governed by the New York State Part 373 Permit.
Potential Threats and Contaminants
As a result of the Respurce Conservation and Recovery Act (RCRA) facility investigation (RFI), Occidental has concluded that hazardous waste constituents have been released to the soil and groundwater beneath the facility.
The New York State Department of Environmental Conservation (NYSDEC) considers the soil and groundwater of the entire facility to be contaminated. The most significant areas of contamination are located in the C-Area, D-Area, F-Area, M-Area, N-Area, U-Area, T-Area and Mercury Cell Area. The releases are related to spills and leaks from past manufacturing activities. The hazardous waste contaminants are present in the soil and groundwater as aqueous (dissolved) phase contaminant plumes and as dense non-aqueous phase liquids (DNAPL).
Aqueous phase contamination has been observed at the facility in the soils and unconsolidated sediments above the bedrock (the "overburden") and in the bedrock. The extent of the aqueous phase contamination plume in the overburden appears to be limited to the facility property. However, the extent of the aqueous phase contamination plume in the bedrock is considerably greater.
Contamination of the D, C and B zones (separate water-bearing zones in the upper 125 feet of bedrock) extends from the facility to the Fall Street Tunnel, approximately 1,800 feet to the north of the facility, and to the New York Power Authority conduit drains that run near the western boundary of the property. Aqueous phase contamination has also infiltrated into the sanitary sewers and outfall sewers at the facility. The overburden and bedrock dense non-aqueous phase liquids (DNAPL) plumes are largely confined to the site.
Cleanup Approach and Progress
During the course of investigating and evaluating site conditions, Occidental Chemical Corp. implemented a number of interim corrective measures (ICMs) designed to mitigate the impacts associated with the observed contamination. The implemented ICMs include:
- Extraction wells along the downgradient west and northwest plant boundaries in the D, C, and B Zones.
- Dense non-aqueous phase liquids (DNAPL) collection from on-site bedrock wells.
- Installation of trenches for passive groundwater collection along the southern and southwestern boundaries of the sit.
- Installation of a barrier wall along the Niagara River.
- DNAPL recovery (when sufficient quantity is encountered) and treatment of recovered DNAPL.
- Effectively containing migration of dioxin and elemental phosphorus contamination by capping these areas and adding surface drainage control.
- Demolition of a former mercury cell processing building and removal of elemental mercury from the soils and fill beneath the building.
- Maintenance of capped and existing hard surfaced areas.
Occidental has completed corrective measures studies (CMS) of the following:
- Bedrock Groundwater Remediation, August 1992.
- Overburden Groundwater Remediation, January 1994.
- Overburden Soils, August 1996.
- Final Corrective Measures Study, November 1998.
Based on the results of the corrective measures studies and performance monitoring data generated as part of the interim corrective measures projects, New York State Department of Conservation (NYSDEC) has determined that the interim corrective measures implemented for the bedrock groundwater flow are capable of achieving the goals of the corrective action program and are protective of human health and the environment.
Pumping from the bedrock along the west and northwest property boundaries is an effective way to draw in and treat groundwater from both on site and off site. Any bedrock groundwater beneath the plant is captured by the extraction wells before migrating off site. In addition, off site bedrock groundwater adjacent to the site is drawn back to the extraction wells. The collected groundwater is then treated to remove the chemicals.
The hydraulic and chemical monitoring results show that the extraction system is operating effectively. The hydraulic monitoring data show that hydraulic containment along the plant boundary has been achieved in the bedrock D, C and B Zones, and in some cases extends well beyond the plant boundary. The chemical monitoring data obtained from the off site monitoring wells since pumping began in April 1996 have shown that there has been a decrease in the level of organic compounds in the groundwater; a decrease attributable to the groundwater containment and extraction.
The collection of dense non-aqueous phase liquids (DNAPL) from on-site bedrock wells has removed significant quantities of DNAPL from the bedrock and is reducing the chemical source in the groundwater.
The sanitary sewer network beneath the plant is constructed to allow limited infiltration of groundwater into the system, which provides a means for collection and treatment of the groundwater. The infiltrated groundwater and associated chemical loading flows to the City of Niagara Falls wastewater treatment plant and is treated prior to discharge to the Niagara River. Collection of groundwater in the sewers in the middle of the plant results in considerably less contaminated groundwater migrating across the plant perimeter.
The facility’s outfall sewer system is currently monitored under the DEC-issued State Pollution Discharge Elimination System (SPDES) permit. OCC will continue to implement corrective measures to the outfall system as dictated by SPDES monitoring. Previous corrective measures made to the outfall system have been very effective in reducing groundwater infiltration. Similarly, the discharge of the sanitary sewer is continuously monitored to confirm that the effluent is within discharge limits set by the city’s wastewater treatment plant. Consequently, it is occasionally necessary for OCC to implement corrective measures on the sanitary sewers to address specific groundwater infiltration situations.
Monitoring data indicate that the bedrock groundwater extraction system is restricting off-site chemical migration, as chemical concentrations have decreased over time. Chemicals off site are being drawn back toward the plant where they are captured by the extraction system.
Deed restrictions and standard operating procedures also have been implemented. The standard operating procedures guide excavations at the plant so that chemical migration and worker exposure are prevented, and groundwater does not infiltrate potable water mains after repairs are made. If additional dense non-aqueous phase liquid (DNAPL) is encountered, it can be removed because personnel and equipment are available. Exposed contaminated soil has been capped with gravel, asphalt or clean topsoil.
An exposure or environmental risk may exist if the groundwater remedial system should fail, although the technology is reliable and readily controlled. If it fails, the monitoring equipment will detect the failure and trigger the implementation of corrective actions. Long-term protection of workers and the public will be ensured by deed restrictions, implementation of institutional controls such as SOPs for excavation and water main repair, maintenance of the plant perimeter fence, and DNAPL volume reduction.
The facility’s existing RCRA operating permit authorizes OCC to operate a corrective measures program as the final corrective action remedy, and also to operate a monitoring program to evaluate the effectiveness of the corrective action remedy. The major products manufactured are chlorine, caustic soda, hydrogen, and Dechlorane Plus, a chlorinated fire retardant. In addition to wastes generated from the manufacturing processes, OCC also generates non-aqueous phase liquid (NAPL) waste from its on-site remedial programs. Hazardous waste that are generated from the active plant operations are not treated or disposed off on site. These wastes are stored on site for less than 90 days.
As a part of the corrective action process on site, ground water, contaminated with hazardous waste constituents from past operations, is treated on site in a SPDES permitted wastewater treatment system.
OCC submitted the Part 373 Permit renewal application as required in 6 NYCRR 373-1.8 on December 13, 2004, and subsequent updates through March, 2007. Following a public comment period, NYSDEC renewed the permit in September, 2008. The permit expires on September 28, 2018.
Final Cleanup Status or Projection
- Final Remedy Construction (RCRAInfo database code CA550) has been achieved.
Copies of supporting technical documents and correspondence cited in this fact sheet are available for public review at:
New York State Department of Environmental Conservation - Region 9
270 Michigan Avenue
Buffalo, NY 14203
Phone: (716) 851-7165
The New York State Department of Environmental Conservation (NYSDEC) makes its public records available for a review under the Freedom of Information Law (FOIL).