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Env Info Document

Harbor Brook CSO Abatement Project Facility Plan (Aug 2005)
by Brown and Caldwell
for Onondaga County Dept of Water Environment Protection

2. Harbor Brook In-Water System

2.1 Original Harbor Brook in-water system concept

The original HB IWS concept included the construction of a storage structure at the mouth of Harbor Brook along with the associated Harbor Brook Floatables Control Facility (HB FCF), located just upstream. The HB IWS was to be constructed in two increments, the demonstration phase and the full size, both of which would provide temporary containment of wet-weather discharges for subsequent treatment at Metro. The design basis for the demonstration facility was to capture Harbor Brook flows (including CSOs, urban stormwater, and baseflow) for up to the one-half of the 1-year frequency, 2-hour duration, design storm event, defined in 15-minute rainfall intervals, which equates to a storage volume of 13 million gallons (MG). Upon successful demonstration, the facility would be expanded to capture the 1-year design storm, with a storage volume of 26 MG.

The HB IWS is a form of storage that would consist of a series of floating pontoons to which heavy gauge PVC curtains would be attached. The curtains would be arranged to create separate cells or bays to capture wet-weather flows. Curtain weights would be used to keep the curtains fixed to the lake bottom. A conceptual layout of the HB IWS is provided on Figure 2.1. A more specific layout would be developed to meet actual site conditions. The floating pontoons, PVC curtains, curtain weights, and a pump station that would return captured flow to the treatment plant following a wet-weather event are shown. Openings between cells would allow the flow to pass from cell to cell. The cell openings would be located to minimize the potential for the short-circuiting of flow through each cell. These openings would also allow for fish passage through the HB IWS.
Figure 2.1. Conceptual layout of the Harbor Brook in-water system
Figure 2.1. Conceptual layout of the Harbor Brook in-water system

When an overflow event occurs, the wet-weather flow would be directed to the HB IWS through the first cell, displacing the clean water that it normally holds. Wet-weather flow would proceed through each consecutive cell either until the wet-weather event is captured, or until the clean water is completely displaced and the facility is full of stormwater. Flow through IWS installations located in Sweden and in Fresh Creek, NY have shown that the arrangement of the ports between the cells creates a flow pattern that approximates plug flow through the facility. Plug flow is a theoretical flow pattern where material is discharged from the facility in the same order in which it enters.

A pumping station, drawing from the first cell would be used to convey captured flow to Metro, once treatment capacity is available following a wet-weather event. Solid material would tend to settle within the first cell of the HB IWS. Provisions would need to be made to remove these accumulated solids on a regular basis and for their subsequent treatment and disposal. The frequency of solids removal would be established during the facility demonstration.

The original HB IWS required several unique features based on specific site constraints and its status as a demonstration facility. A flow diversion structure with a tilting-weir gate would be located onshore near the mouth of Harbor Brook. In the open position, the gate would allow flow to drain naturally to the Lake. In the closed position, the gate would divert wet-weather flow to the HB IWS.

Level sensors located within key CSO outfalls would be used to determine the start and end of an overflow event, and control the position of the gate with the goal of capturing the “first flush” as well as additional CSOs up to a combined stream and CSO volume of 13 MG (demonstration phase). The sensors and a number of rain gages at different points in the Harbor Brook basin would be connected to a supervisory control and data acquisition system (SCADA) at Metro. In a similar manner, a level sensor would be installed at the US Geological Survey (USGS) Gauging Station on Harbor Brook, approximately 1000 feet upstream of Onondaga Lake to measure the volume of flow that enters the HB IWS.

2.2 Impediments to the original HB IWS concept

On March 16, 1999 the County and its consultants presented the HB IWS concept to EPA officials at the Region 2 offices. The principal EPA concern at that time, related to Onondaga Lake’s designation as a Federal Superfund Site, pursuant to the Comprehensive Environmental Response, Compensation Liability Act (CERCLA). Because of the magnitude of the Superfund issue, as described below, other possible concerns, such as impacts to floodplain, wetlands, fish and wildlife, were not investigated further.

The Onondaga Lake Superfund Site includes eight NPL Subsites. The two areas of immediate concern to the HB IWS are the Lake Bottom subsite and the Wastebed B/Harbor Brook subsite.

These subsites include sediments and groundwater that are contaminated with mercury, benzene, toluene, ethylbenzene, xylenes (BTEX), chlorinated benzenes, polynuclear aromatic hydrocarbons (PAHs), PCBs, polychlorinated dibenzo-p-dioxins or polychlorinated dibenzofurans, and calcite.

A Remedial Investigation (RI) and Feasibility Study (FS) was conducted by Honeywell for the Lake Bottom subsite to document the nature and extent of the contamination in the Lake, assess the human health and ecological risks posed by this contamination and to identify and evaluate remedial alternatives to address the contaminated sediments. NYSDEC issued a Proposed Remedial Action Plan (PRAP) for the Onondaga Lake Bottom subsite in late November 2004. The selected remedial action will be decided upon in a Record of Decision (ROD) issued by NYSDEC which is currently scheduled for March, 2005. After the issuance of a ROD, the approved remedial action would then be designed and implemented.

Some of these issues could be avoided if the proposed HB IWS were to be constructed following remediation; however, the timing on completion of remediation is currently unknown. The NYSDEC estimates that it will take approximately 3 years to design the lake bottom remedy and 4 years to construct it. This estimate does not include addressing the remediation of the Wastebed B/Harbor Brook NPL subsite

All of these unknowns would require further investigation and add to the complexity and uncertainty as to when and how, or whether, this site could realistically be remediated and used for the site of the IWS. The current extent of the contamination in the vicinity of the proposed IWS and the presence of ongoing contaminant releases were not known to the ACJ parties when the ACJ was written. As a result of the impediments identified above, the HB IWS is not considered a viable CSO abatement approach for the Harbor Brook Basin.

2.3 Alternatives to the HB IWS

In consideration of the impediments outlined in Section 2.2, as well as the requirements of the State Environmental Quality Review Act (SEQRA), alternatives for the abatement of Harbor Brook CSOs have been developed and evaluated. The ACJ states:

If the [HB IWS] project is not deemed technically acceptable, the County will proceed with the design and construction of the Delaware and State Fair RTFs [regional treatment facilities] at a schedule to be proposed by the County to DEC. [Appendix B, p. 10]

This facility plan, however, goes beyond the wording in the ACJ and includes a complete review of alternative technologies and potential sites for CSO abatement facilities to address the 18 permitted CSOs that discharge to Harbor Brook. As required under the ACJ, opportunities for sewer separation have also been evaluated as a comprehensive and/or partial CSO abatement approach as well.

An evaluation of technologies and alternative sites has been completed in order to provide a thorough analysis of the options available for the abatement of CSOs discharging to Harbor Brook. The technologies and site options were evaluated independently based on certain criteria. Selected technologies were then assembled into treatment processes at specific sites. These site-specific abatement alternatives were further evaluated based on cost, and then assembled into various scenario combinations designed to achieve abatement of the Harbor Brook CSOs.


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Susan Miller, Project Deputy Director
Phone 315-435-2260   Fax 315-435-5023
 Onondaga County Dept of Water Environment Protection