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WMA water withdrawal Summary (APPENDIX E, TABLE E5)



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WMA water withdrawal Summary (APPENDIX E, TABLE E5)


Facility

WMA

Permit

Number

WMA

Registration

Number

Source

Authorized Withdrawal (MGD)

Cohasset Water Department

N/A

32106501

3065000-02S Lily Pond

0.65*

*System-wide withdrawal, all sources are not necessarily within this segment; however, Cohasset Water Department reported all water was withdrawn from Lily Pond between 2000 and 2002 (MassDEP 2003c).

NPDES wastewater discharge summary (APPENDIX E, TABLEs E1 and E2)


There are no direct NPDES wastewater discharges to Herring Brook, but a NPDES permit (MA0103098) was issued to the Cohasset Water Department to discharge from the public water supply treatment plant to Lily Pond, which is in the subwatershed of this segment. EPA terminated this permit when the general permit for the Lily Pond Water Treatment Plant (MAG640070) was issued in May 2005.

Use Assessment

Aquatic Life

Habitat and Flow

The poorly designed, deteriorating notched weir-pool fish ladder at Hunters Pond is impassable (Reback et al. 2004).

Biology

Dense growth of the non-native aquatic macrophyte Cabomba caroliniana was observed in both Lily Pond (ENSR 2003) and the Aaron River upstream from the Beechwood Street Dam (MassDEP 2001a).
Based on the presence of the barrier to anadromous fish migration and the presumed infestation of Herring Brook with a non-native macrophyte, the Aquatic Life Use is assessed as impaired. Flow alterations from the water supply diversion are also of concern.

primary and secondary contact recreation and aesthetics


Dense growth of the non-native aquatic macrophyte Cabomba caroliniana was observed in both Lily Pond (ENSR 2003) and the Aaron River upstream from the Beechwood Street Dam (MassDEP 2001a).
The Recreational and Aesthetic uses are assessed as impaired for Herring Brook based on the presumed dense infestation of Herring Brook with a non-native aquatic macrophyte.
Herring Brook (MA94-29) Use Summary Table

Designated Uses

Status

Aquatic Life



IMPAIRED

Causes: Fish barriers and non-native aquatic macrophyte



Sources: Hydrostructure impacts on fish passage and unknown

Fish Consumption



NOT ASSESSED

Primary Contact



IMPAIRED

Cause: Non-native aquatic macrophyte



Source: Unknown

Secondary Contact



Aesthetics




recommendations

The fishway at Hunters Pond should be redesigned and replaced (Reback et al. 2004).


Further investigate/define the extent of the infestation of Cabomba caroliniana.
In order to maintain the integrity of aquatic life in Herring Brook flow regimes should be maintained as close to a natural regime as possible (i.e., the flashboards near Beechwood Street should be used as little as possible to reverse the flow of Aaron River and Herring Brook back into Lily Pond). If changes are implemented monitoring designed to document changes in water quality conditions should be conducted.

Bound Brook (Segment MA94-18)

Location: Flow control structure near Beechwood Street, Cohasset to outlet Hunters Pond, Scituate.

Segment Length: 2.2 miles

Classification: Class B


Land-use estimates (top 3, excluding water) for the 11.3 mi2 subwatershed:

Forest 75%

Residential 16%

Open Land 3%


Bound Brook is listed on the 2002 Integrated List of Waters in Category 3. This segment had insufficient information to make assessments for any of the designated uses (MassDEP 2003a).



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