Haley & Aldrich, Inc. 465 Medford St. Suite 2200 Boston, MA 02129-1400
Tel: 617.886.7400 Fax: 617.886.7600 HaleyAldrich.com
9 December 2010 (Original Submittal 18 November 2009) File No. 31502-160
US Environmental Protection Agency 5 Post Office Square, Suite 100 Mail Code OEP06-4 Boston, MA 02109-3912
Attention: Remediation General Permit NOI Processing
Subject: Notice of Intent (NOI) Temporary Construction Dewatering Spaulding Rehabilitation Hospital Parcels 6 and 7 – Charlestown Navy Yard Charlestown, Massachusetts
Ladies and Gentlemen:
On 18 November 2009, on behalf of Partner’s HealthCare System, Inc., Haley & Aldrich, Inc., (Haley & Aldrich) requested your approval of a National Pollutant Discharge Elimination System (NPDES) Remediation General Permit (RGP) for discharge of water due to temporary construction dewatering associated with the excavations on Parcels 5, 6, and 7. Partners HealthCare System, Inc. (Owner) and Walsh Brothers, Incorporated (Operator) were issued permission to discharge under Permit No. MAG910442 on 2 December 2010.
Per the Environmental Protection Agency’s letter dated 13 September 2010 to Walsh Brothers, entitled “RE: Notice of Availability of the Final 2010 Remediation General Permit and Re-Application for Coverage under the 2010 Remediation General Permit for Parcel 6 and 7 – Charlestown Navy Yard in Charlestown MA (NPDES Permit Number MAG 910442)”, Haley & Aldrich is re-applying for coverage by submitting a Notice of Intent (NOI) to the EPA by December 9, 2010. This request is being submitted within the required 90 days after the effective date of the 2010 RGP.
This resubmittal includes the same information as the 18 November 2010 and includes updated information as appropriate. A summary of dewatering activities and discharge sampling have been submitted via email and as part of Monthly Discharge Monitoring Reports. Please refer to those reports for additional sampling results obtained since the original NOI.
In accordance with the National Pollutant Discharge Elimination System (NPDES) Remediation General Permit in Massachusetts, MAG910000, this letter resubmits a Notice of Intent and the applicable documentation as required by the US Environmental Protection Agency (EPA) for construction site dewatering under the RGP. Temporary dewatering was conducted under the previous permit and is ongoing in support of the construction activities proposed at the Yard's End Parcels 5, 6 and 7 site, US Environmental Protection Agency 9 December 2010 (Original Submittal 18 November 2010) Page 2
located in the Former Charlestown Navy Yard in Charlestown, Massachusetts, as shown on Figure 1 – Project Locus.
The property owner is Partners HealthCare System, Inc. (Partners), who acquired Parcels 6 & 7 from the Boston Redevelopment Authority (BRA) on 24 May 2010. Partners is in the process of constructing a new facility for the Spaulding Rehabilitation Hospital at Parcel 6. The new facility will consist of an eight-story building with two levels of below-grade parking which requires an excavation of up to 30 ft below ground surface. The work will also include excavations for utility installations, soil remediation, and landscaping. Plans for Parcel 7 includes the repair of an existing seawall, construction of a public access harborwalk, soil remediation, and use for short-term construction staging in conjunction with the proposed redevelopment of Parcel 6. Activities on Parcel 5 are limited to soil remediation to support the establishment of a site driveway area.
Site History
The Charlestown Navy Yard area within which the Site is located was formerly part of the Boston Naval Shipyard of the United States Navy. The northeastern and eastern boundary of the site consists of the Little Mystic River or the Boston Inner Harbor. Historically, the Site was under water and was originally used as a timber receiving dock between 1834 and 1890. By 1920, the Site had been filled and developed with several buildings, scrap storage bins, and a dump area. Over time, 17 naval buildings were located at the Site, including storage facilities for oil, paint, flammables, pipe, steel, machinery, and lumber at various times; a refuse incinerator; a sandblasting facility; and a fire pump house. Several other features were formerly located at the Site, including storage bins, dump areas, a fuel oil underground storage tank, and several aboveground storage tanks.
The Boston Naval Shipyard was decommissioned in 1974. BRA, a municipal redevelopment authority, acquired the Site in 1979 for urban renewal purposes. The Site has been largely unused since that time, with the exception of the use of portions of the Site as a staging area for nearby construction projects. Previously existing buildings at the Site were demolished by the late 1990s.
Regulatory Background
Yard’s End Parcels 5, 6 and 7 at the Charlestown Navy Yard were previously reported as one Site to the Massachusetts Department of Environmental Protection (MassDEP) by the BRA in 1990 due to the identification of concentrations of polychlorinated biphenyls (PCBs), oil and grease, and lead in soil. At that time, MassDEP assigned Release Tracking Number (RTN) 3-3372 to the three parcels and subsequently issued a Massachusetts Contingency Plan (MCP, 310 CMR 40.0000) Waiver of Approvals.
Partners conducted due diligence investigations at the Site in 2004 and 2005 and, based on the results, the BRA re-reported the Site to the MassDEP based on oil and hazardous material (OHM) concentrations exceeding MCP Reportable Concentrations at Parcels 6 and 7 in August 2005. At the request of the BRA, MassDEP agreed to assign a new RTN (RTN 3-25132) to Parcels 6 and 7, and to reassign RTN 3-3372 to Parcel 5 only. Although not required due to its status as a municipal redevelopment authority, the BRA voluntarily submitted an MCP Phase I Initial Site Investigation Report, Tier II Classification Submittal and Conceptual Phase II Scope of Work to the MassDEP in August 2006.
US Environmental Protection Agency 9 December 2010 (Original Submittal 18 November 2010) Page 3
Based on concentrations of PCBs detected in soils, and due to uncertainty regarding the date of the release and the original concentration of the release of PCBs, a portion of the Site is subject to regulation under the Toxic Substances Control Act (TSCA). Accordingly, a Self-Implementing Cleanup and Disposal Plan (Self-Implementing Plan) was submitted to the US Environmental Protection Agency on 18 September 2009. Based on comments from the EPA, a Revised Self-Implementing Cleanup and Disposal Plan was submitted on 23 February 2010.
The proposed remedial activities and Site improvements are being conducted pursuant to an MCP Release Abatement Measure (RAM) Plan that was submitted to MassDEP on 22 December 2009 (dated 21 December 2009), and has been coordinated with and conducted in accordance with the requirements of the TSCA Self-Implementing Plan. The RAM Plan and the TSCA Self-Implementing Plan have provided guidance for the management of soils and groundwater at the Site during redevelopment.
Temporary Construction Dewatering Notice of Intent
In support of the NOI, groundwater samples were collected from two observation wells (HA-C2(OW) and HA-10(OW)) located within the project site. The results of water quality testing conducted for this NOI are summarized in Table I. Additional groundwater quality data have been collected at the site from several site observation wells. The results of the additional water quality testing are summarized in Table II. The location of the observation wells is shown on Figure 3.
Dewatering was and will continue to be conducted from sumps or well points located inside the sheeted excavation, and also from smaller, local excavations outside the proposed foundation limits for the installation of utilities and landscaping and for remedial excavation. Dewatering is necessary to control groundwater, seepage, precipitation, surface water runoff and construction-generated water to enable construction in-the-dry. Construction began in December 2009, and construction dewatering and discharge began on 14 April 2010. Currently, discharge is not occurring, but may be restarted as needed to maintain dry excavations. Note that at the restart of discharge, sampling will be performed in accordance with Initial Treatment System Discharge Start Up requirements.
Prior to discharge, collected watering will be routed through a sedimentation tank and bag filter, at a minimum, to remove suspended solids and undissolved chemical constituents (metals), as shown in the Proposed Treatment System Schematic included in Figure 2 herein. Construction dewatering under this RGP NOI will include piping and discharging to storm drains located within and near the site. The storm drains travel a short distance northeast within the site and discharge directly into the Little Mystic Channel/Boston Inner Harbor. The proposed discharge route is shown on Figure 3, Proposed Dewatering Discharge Route.
US Environmental Protection Agency 9 December 2010 (Original Submittal 18 November 2010) Page 4
Chloride Sampling
As required in the new RGP for sampling parameters, Haley & Aldrich collected a water sample from an existing well on 16th Street on 3 December 2010. Chloride was detected at 4900 mg/l in the water sample, which is likely due to the site’s coastal environment. The laboratory reports are included in Appendix G.
Appendices
The completed “Suggested Notice of Intent” (NOI) form as provided in the RGP is enclosed in Appendix A. The site operator is Walsh Brothers, Incorporated (Walsh). Walsh is the construction manager and will hire a subcontractor to conduct the Site work, including the dewatering activities. Haley & Aldrich, Inc. (Haley & Aldrich) will monitor the Contractor’s dewatering activities on behalf of Partners. In accordance with the requirements for this NOI submission, Partners as the owner and Walsh as the construction manager are listed as co-permittees for this NPDES RGP, and therefore both have signed the NOI form.
Appendix B provides Material Data Safety Sheets (MSDS) and fact sheets for possible chemical additives or treatments to be used in the treatment system. A Best Management Practices Plan (BMPP), which outlines the proposed discharge operations covered under the RGP, is included in Appendix C. Appendices D and E include National Register of Historic Places and Endangered Species Act Documentation, respectively. Appendix F provides the BWSC Permit Application to be submitted separately to the Boston Water and Sewer Commission and a copy of a memorandum sent in January 2010 in response to BWSC’s review. A copy of the groundwater testing laboratory results are provided in Appendix G. Appendix H includes the Notice of Change Form to be submitted to the EPA when property ownership is transferred from the BRA to Partners. Appendix I includes the Notice of Availability and the original RGP dated 2 December 2009.
US Environmental Protection Agency 9 December 2010 (Original Submittal 18 November 2010) Page 5
Closing
Thank you very much for your consideration of this NOI. Please feel free to contact us should you wish to discuss the information contained herein or if you need additional information.
Sincerely yours, HALEY & ALDRICH, INC
Iliana Alvarado, P.E. Mark X. Haley, P.E. Senior Engineer Senior Vice President
Attachments: Table I - Summary of Groundwater Quality Data Table II - Summary of Additional Groundwater Quality Data Figure 1 - Site Locus Figure 2 - Proposed Treatment System Schematic Figure 3 - Proposed Dewatering Discharge Routes Appendix A – Notice of Intent (NOI) for Remediation General Permit (RGP) Appendix B – MSDS and Fact Sheets Appendix C – Best Management Practices Plan (BMPP) Appendix D – National Register of Historic Places and Massachusetts Historical Commission Documentation Appendix E – Endangered Species Act Documentation Appendix F – BWSC Permit Application (Resubmitted) & January 2010 Memorandum Appendix G – Laboratory Data Reports Appendix H – Notice of Change Form Appendix I – Notice of Availability and Remediation General Permit
US Environmental Protection Agency 9 December 2010 (Original Submittal 18 November 2010) Page 6
c: Partners HealthCare System, Inc.; Attn: Kathryn West Partners HealthCare System, Inc.; Attn: Tim Pattison Partners HealthCare System, Inc.; Attn: David Burson Walsh Brothers, Inc.; Attn: Attn: James Lyons Haley & Aldrich, Inc.; Attn: Mark X. Haley Haley & Aldrich, Inc.; Attn: Lisa Turturro Vanasse Hangen Brustlin, Inc.; Attn: Mark Junghans Perkins + Will; Attn: Jessica Stebbins Boston Water and Sewer Commission; Attn: Francis McLaughlin
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TABLE I - SUMMARY OF GROUNDWATER QUALITY DATA SPAULDING REHABILITATION HOSPITAL PARCELS 6 AND 7 - CHARLESTOWN NAVY YARD CHARLESTOWN, MASSACHUSETTS FILE NO.: 31502-060
LOCATION HA-C2(OW) HA-10(OW) SAMPLING DATE 6/1/2009 6/1/2009 LAB SAMPLE ID L0907022-01 L0907022-02 MATRIX Aqueous Aqueous
VOCs by GC/MS (ug/L) Tetrachloroethene 7.2 ND(0.75) cis-1,2-Dichloroethene 3.2 ND(0.5) Trichloroethene 1 ND(0.5) Total VOCs by GC/MS 11.4 ND
SVOCs by GC/MS (ug/L) Total SVOCs by GC/MS ND ND
SVOCs by GC/MS-SIM (ug/L) Acenaphthene ND(0.1) 0.38 1-Methylnaphthalene ND(0.1) 5.6 2-Methylnaphthalene ND(0.1) 1.3 Total SVOCs by GC/MS-SIM ND 7.28
Total Metals (ug/L) Antimony, Total ND(1) ND(1) Arsenic, Total 3.3 11.3 Cadmium, Total ND(0.4) ND(1) Chromium, Total ND(1) ND(1) Chromium, Hexavalent ND(5) ND(5) Copper, Total 4.1 13.7 Iron, Total 5200 3500 Lead, Total 11.6 11.3 Mercury, Total ND(0.1) 0.4 Nickel, Total ND(1) 4.2 Selenium, Total 5 70 Silver, Total ND(0.8) ND(0.8) Zinc, Total 27.1 62.8
Dissolved Metals (ug/L) Antimony, Dissolved ND(1) ND(1) Arsenic, Dissolved 4.6 11.6 Cadmium, Dissolved ND(0.4) - Chromium, Dissolved ND(1) ND(1) Copper, Dissolved 3.1 13.5 Iron, Dissolved 6000 3500 Lead, Dissolved 5.6 9.7 Mercury, Dissolved ND(0.1) 0.3 Nickel, Dissolved 2.5 4.3 Selenium, Dissolved 9 69 Silver, Dissolved ND(0.8) ND(0.8) Zinc, Dissolved 22.8 60.8
PCBs (ug/L) Total PCBs ND ND
Pesticides by GC (ug/L) 1,2-Dibromoethane ND(0.0105) ND(0.0095)
TPH (ug/L) Total Petroleum Hydrocarbons ND(1600) ND(1600)
General Chemistry Solids, Total Suspended 12000 36000 Cyanide, Total ND(2.5) ND(2.5) Chlorine, Total Residual ND(10) ND(10) Phenolics, Total ND(15) ND(15)
Abbreviations: - : Not analyzed ND(2.5): Not detected; number in parentheses is one-half the laboratory reporting limit
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TABLE II - SUMMARY OF ADDITIONAL GROUNDWATER QUALITY DATA SPAULDING REHABILITATION HOSPITAL PARCELS 6 AND 7 - FORMER CHARLESTOWN NAVY YARD CHARLESTOWN, MASSACHUSETTS FILE NO.: 31502-060
LOCATION HA-I8 HA-4 HA-F6(OW HA-A6(OW) HA-F2(OW) HA-K6(OW) F2 (OW) I8 (OW) SAMPLING DATE 5/15/2009 5/15/2009 6/1/2009 6/4/2009 6/4/2009 6/4/2009 6/22/2006 6/22/2006 LAB SAMPLE ID L0906284-01 L0906284-02 L0907025-01 L0907279-02 L0907279-03 L0907279-04 MATRIX Min Max Aqueous Aqueous Aqueous Aqueous Aqueous Aqueous Aqueous Aqueous
MCP VOCs (ug/L) Total VOCs ND ND ND ND ND ND ND ND ND ND
MCP SVOCs (ug/L) Bis(2-Ethylhexyl)phthalate ND(2.4) 6 ND(2.45) ND(2.4) ND(2.5) ND(2.5) ND(2.5) ND(2.5) ND(2.5) ND(2.5) Total MCP SVOCs ND(6) 6 ND ND ND ND ND ND ND ND
MCP SVOCs by SIM (ug/L) Fluoranthene ND(0.095) 0.3 ND(0.1) ND(0.095) 0.3 ND(0.1) ND(0.1) ND(0.1) ND(0.25) ND(0.25) Pyrene ND(0.095) 0.28 ND(0.1) ND(0.095) 0.2 ND(0.1) ND(0.1) ND(0.1) ND(0.25) ND(0.25) Total MCP SVOCs by SIM ND(0.5) 0.58 ND ND 0.5 ND ND ND ND ND
Dissolved Metals (ug/L) Antimony, Dissolved ND(1) ND(3) ND(1) ND(1) ND(1) ND(1) ND(1) ND(1) ND(3) ND(3) Arsenic, Dissolved ND(2.5) 11.6 ND(2.5) ND(2.5) ND(2.5) ND(2.5) ND(2.5) ND(2.5) ND(25) ND(25) Barium, Dissolved ND(5) 100 30 39 44 73 54 59 ND(100) ND(100) Beryllium, Dissolved ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) Cadmium, Dissolved ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) Chromium, Dissolved ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) Lead, Dissolved ND(2.5) 61 ND(5) 22 ND(5) ND(5) ND(5) ND(5) 12 ND(2.5) Mercury, Dissolved ND(0.1) 0.1 ND(0.1) ND(0.1) ND(0.1) ND(0.1) ND(0.1) ND(0.1) ND(0.1) ND(0.1) Nickel, Dissolved ND(12.5) 20 ND(12.5) ND(12.5) ND(12.5) ND(12.5) ND(12.5) ND(12.5) ND(20) ND(20) Selenium, Dissolved ND(5) 25 ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) ND(25) ND(25) Silver, Dissolved ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) Thallium, Dissolved ND(1) ND(1) ND(1) ND(1) ND(1) ND(1) ND(1) ND(1) ND(1) ND(1) Vanadium, Dissolved ND(5) ND(25) ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) ND(25) ND(25) Zinc, Dissolved ND(25) 1700 96 212 ND(25) ND(25) 528 177 1700 300
PCBs (ug/L) Total PCBs ND ND ND ND ND ND ND ND ND ND
VPH (ug/L) C5-C8 Aliphatics, Unadjusted ND(10) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(10) ND(10) C9-C12 Aliphatics, Unadjusted ND(10) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(10) ND(10) C9-C10 Aromatics ND(10) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(10) ND(10) C5-C8 Aliphatics, Adjusted ND(10) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(10) ND(10) C9-C12 Aliphatics, Adjusted ND(10) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(25) ND(10) ND(10)
EPH (ug/L) C9-C18 Aliphatics ND(42.75) ND(250) ND(52.5) ND(52) ND(50) ND(42.75) ND(42.75) ND(42.75) ND(250) ND(250) C19-C36 Aliphatics ND(42.75) ND(250) ND(52.5) ND(52) ND(50) ND(42.75) ND(42.75) ND(42.75) ND(250) ND(250) C11-C22 Aromatics, Unadjusted ND(42.75) ND(75) ND(52.5) ND(52) ND(50) ND(42.75) ND(42.75) ND(42.75) ND(75) ND(75) C11-C22 Aromatics, Adjusted ND(42.75) ND(75) ND(52.5) ND(52) ND(50) ND(42.75) ND(42.75) ND(42.75) ND(75) ND(75)
Abbreviations: - : Not analyzed ND(2.5): Not detected; number in parentheses is one-half the laboratory reporting limit
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TABLE II - SUMMARY OF ADDITIONAL GROUNDWATER QUALITY DATA SPAULDING REHABILITATION HOSPITAL PARCELS 6 AND 7 - FORMER CHARLESTOWN NAVY YARD CHARLESTOWN, MASSACHUSETTS FILE NO.: 31502-060
LOCATION HA-4 (MW) HA-10 (MW) F11 (OW) A6 (OW) SAMPLING DATE 6/21/2006 6/21/2006 6/21/2006 6/20/2006 LAB SAMPLE ID MATRIX Min Max Aqueous Aqueous Aqueous Aqueous
MCP VOCs (ug/L) Total VOCs ND ND ND ND ND ND
MCP SVOCs (ug/L) Bis(2-Ethylhexyl)phthalate ND(2.4) 6 ND(2.5) 6 ND(2.5) ND(2.5) Total MCP SVOCs ND(6) 6 ND 6 ND ND
MCP SVOCs by SIM (ug/L) Fluoranthene ND(0.095) 0.3 ND(0.25) ND(0.25) ND(0.25) ND(0.25) Pyrene ND(0.095) 0.28 ND(0.25) ND(0.25) ND(0.25) ND(0.25) Total MCP SVOCs by SIM ND(0.5) 0.58 ND ND ND ND
Dissolved Metals (ug/L) Antimony, Dissolved ND(1) ND(3) ND(3) ND(3) ND(3) ND(3) Arsenic, Dissolved ND(2.5) 11.6 ND(15) ND(15) ND(15) ND(15) Barium, Dissolved ND(5) 100 ND(100) ND(100) ND(100) ND(100) Beryllium, Dissolved ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) Cadmium, Dissolved ND(2) ND(2) ND(2) ND(2) ND(2) ND(2) Chromium, Dissolved ND(5) ND(5) ND(5) ND(5) ND(5) ND(5) Lead, Dissolved ND(2.5) 61 ND(2.5) ND(2.5) 15 ND(2.5) Mercury, Dissolved ND(0.1) 0.1 ND(0.1) ND(0.1) ND(0.1) ND(0.1) Nickel, Dissolved ND(12.5) 20 ND(20) ND(20) ND(20) ND(20) Selenium, Dissolved ND(5) 25 ND(25) ND(25) ND(25) ND(25) Silver, Dissolved ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) ND(3.5) Thallium, Dissolved ND(1) ND(1) ND(1) ND(1) ND(1) ND(1) Vanadium, Dissolved ND(5) ND(25) ND(25) ND(25) ND(25) ND(25) Zinc, Dissolved ND(25) 1700 300 ND(100) ND(100) ND(100)
PCBs (ug/L) Total PCBs ND ND ND ND ND ND
VPH (ug/L) C5-C8 Aliphatics, Unadjusted ND(10) ND(25) ND(10) ND(10) ND(10) ND(10) C9-C12 Aliphatics, Unadjusted ND(10) ND(25) ND(10) ND(10) ND(10) ND(10) C9-C10 Aromatics ND(10) ND(25) ND(10) ND(10) ND(10) ND(10) C5-C8 Aliphatics, Adjusted ND(10) ND(25) ND(10) ND(10) ND(10) ND(10) C9-C12 Aliphatics, Adjusted ND(10) ND(25) ND(10) ND(10) ND(10) ND(10)
EPH (ug/L) C9-C18 Aliphatics ND(42.75) ND(250) ND(250) ND(250) ND(250) ND(250) C19-C36 Aliphatics ND(42.75) ND(250) ND(250) ND(250) ND(250) ND(250) C11-C22 Aromatics, Unadjusted ND(42.75) ND(75) ND(75) ND(75) ND(75) ND(75) C11-C22 Aromatics, Adjusted ND(42.75) ND(75) ND(75) ND(75) ND(75) ND(75)
Abbreviations: - : Not analyzed ND(2.5): Not detected; number in parentheses is one-half the laboratory reporting limit
Haley & Aldrich, Inc. G:\31502\060 - NPDES RGP\Tables\2009-1116-HAI-Yrd End RGP Table II-F.xls Print Date: 11/18/2009 SITE COORDINATES:42°22'43"N 71°2'58"W SPAULDING REHABILITATION HOSPITAL PARCELS 6 AND 7 - CHARLESTOWN NAVY YARD CHARLESTOWN, MASSACHUSETTS
3
1 PROJECT LOCUS 5 0 2 - 0 6 0 1 . P D SCALE: 1:24,000 F U.S.G.S. QUADRANGLE: BOSTON NORTH, MA NOVEMBER 2009 FIGURE 1
BWSC OUTFALL NO. DO 075 LEGEND: APPROXIMATE LOCATION OF PROPOSED POINT OF DISCHARGE D APPROXIMATE ROUTE OF DISCHARGE TO OUTFALL
APPROXIMATE LOCATION OF PROPOSED TREATMENT SYSTEM D D K6-OW OW-100 DESIGNATION AND APPROXIMATE LOCATION OF OBSERVATION WELL INSTALLED BY CARR-DEE CORP. OF MEDFORD, MASSACHUSETTS AND MONITORED BY WALSH BROTHERS IN BWSC OUTFALL NO. DO 077 JUNE 2010
D K6-OW DESIGNATION AND APPROXIMATE LOCATION OF TEST BORING/MONITORING WELL INSTALLED BY NEW HAMPSHIRE BORING AND MONITORED BY HALEY & ALDRICH, INC. FROM 6 APRIL 2009 TO 29 MAY 2009
HA-I8(MW) HA-F2(MW) DESIGNATION AND APPROXIMATE LOCATION OF TEST BORING/MONITORING WELL INSTALLED BY NEW HAMPSHIRE BORING, INC. AND MONITORED BY HALEY & ALDRICH, INC. DURING THE PERIOD 3 APRIL 2006 TO 23 JUNE 2006. D HA-4 DESIGNATION AND APPROXIMATE LOCATION OF MONITORING WELL INSTALLED BY NEW HAMPSHIRE BORING, INC. AND MONITORED BY HALEY & ALDRICH, INC. ON 15 AND 16 THIRD AVENUE NOVEMBER 2004.
B-MW-1 DESIGNATION AND APPROXIMATE LOCATION OF TEST BORING AND MONITORING WELL INSTALLED BY BROWN & CALDWELL ON HA-4(OW) 11 AND 12 JUNE 2003. APPROXIMATE LIMITS OF TOXIC SUBSTANCES CONTROL ACT HA-F2(MW) (TSCA) REGULATED AREA AND SOURCE OF DISCHARGE HA-F11(MW)
PARCEL 7 (
OW-101 P PARCEL 6 U B
L APPROXIMATE LOCATION OF I C
-
V
A D R PROPOSED BELOW-GRADE I A B L E
NOTES: W FOOTPRINT I D
SECOND AVENUE T H ) S
T 1. EXISTING CONDITIONS BASE PLAN OBTAINED FROM ELECTRONIC R DRAWING ENTITLED "10787-EX.DWG" AND PREPARED BY VANASSE
E D
E ~ HANGEN BRUSTLIN, INC. AND TRANSMITTED ON 5 MAY 2009. T 2. PROPOSED BUILDING FOOTPRINT OBTAINED FROM ELECTRONIC PIER 11 DRAWING ENTITLED "UTILITY PLAN", DATED 09/04/2009, ADDENDUM #1 (9/18/09), RECEIVED FROM PERKINS + WILL, BOSTON, MASSACHUSETTS ~ ON 26 OCTOBER 2009. HA-10(OW)
B-MW-3(DESTROYED) OW-100
D HA-A6(MW) FIRST AVENUE LIMITS OF SUBGRADEEXCAVATION / SOURCE OF DISCHARGE 0 80 160
PARCEL 6 SCALE IN FEET
G PARCEL 5 W D . 9 2
2 SPAULDING REHABILITATION HOSPITAL B -
0 DRY DOCK PARCEL 6 AND 7 - CHARLESTOWN NAVY YARD 6
1 NO. 5 CHARLESTOWN, MASSACHUSETTS - 2 0 5 1 3
\ APPROXIMATE 2 PROPOSED DEWATERING 0
5 LIMITS OF WORK 1
3 DISCHARGE ROUTES \ S C I H P A
R SCALE: AS SHOWN G \ : DECEMBER 2010 FIGURE 3 J
APPENDIX A
Notice of Intent (NOI) for Remediation General Permit (RGP)
NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
B. Suggested Form for Notice of Intent (NOI) for the Remediation General Permit
1. General facility/site information. Please provide the following information about the site: a) Name of facility/site: Facility/site mailing address:
Location of facility/site: Facility SIC Street: code(s): longitude:______latitude:______b) Name of facility/site owner: Town:
Email address of facility/site owner: State: Zip: County:
Telephone no. of facility/site owner:
Fax no. of facility/site owner: Owner is (check one): 1. Federal____ 2. State/Tribal____ 3. Private____ 4. Other ____ if so, describe: Address of owner (if different from site):
Street:
Town: State: Zip: County: c) Legal name of operator: Operator telephone no:
Operator fax no.: Operator email:
Operator contact name and title:
Address of operator (if different from Street: owner):
Town: State: Zip: County:
Remediation General Permit Page 10 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000 d) Check Y for Ayes@ or N for Ano@ for the following: 1. Has a prior NPDES permit exclusion been granted for the discharge? Y___ N___, if Y, number:______2. Has a prior NPDES application (Form 1 & 2C) ever been filed for the discharge? Y___ N___, if Y, date and tracking #:______3. Is the discharge a “new discharge” as defined by 40 CFR 122.2? Y___ N___ 4. For sites in Massachusetts, is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting? Y___ N___ e) Is site/facility subject to any State permitting, license, f) Is the site/facility covered by any other EPA permit, including: or other action which is causing the generation of 1. Multi-Sector General Permit? Y___ N___, discharge? Y___ N___ if Y, number:______If Y, please list: 2. Final Dewatering General Permit? Y___ N___, 1. site identification # assigned by the state of NH or if Y, number:______MA:______3. EPA Construction General Permit? Y___ N___, 2. permit or license # assigned:______if Y, number: ______3. state agency contact information: name, location, and 4. Individual NPDES permit? Y___ N___, telephone number: if Y, number:______5. any other water quality related individual or general permit? Y___ N___, if Y, number:______g) Is the site/facility located within or does it discharge to an Area of Critical Environmental Concern (ACEC)? Y____ N____ h) Based on the facility/site information and any historical sampling data, identify the sub-category into which the potential discharge falls. Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A. Gasoline Only Sites ____ B. Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C. Petroleum Sites with Additional Contamination ____ II - Non Petroleum Site Remediation A. Volatile Organic Compound (VOC) Only Sites _____ B. VOC Sites with Additional Contamination ____ C. Primarily Heavy Metal Sites ____ III - Contaminated Construction Dewatering A. General Urban Fill Sites ____ B. Known Contaminated Sites ____
Remediation General Permit Page 11 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
IV - Miscellaneous Related Discharges A. Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B. Well Development/Rehabilitation at Contaminated/Formerly Contaminated Sites ____ C. Hydrostatic Testing of Pipelines and Tanks ____ D. Long-Term Remediation of Contaminated Sumps and Dikes ____ E. Short-term Contaminated Dredging Drain Back Waters (if not covered by 401/404 permit) ____
2. Discharge information. Please provide information about the discharge, (attaching additional sheets as necessary) including: a) Describe the discharge activities for which the owner/applicant is seeking coverage:
b) Provide the following information about each discharge:
1) Number of discharge 2) What is the maximum and average flow rate of discharge (in cubic feet per second, ft3/s)? points: Max. flow______Is maximum flow a design value? Y___ N____ Average flow (include units) ______Is average flow a design value or estimate? ______
3) Latitude and longitude of each discharge within 100 feet: pt.1: lat.______long.______; pt.2: lat.______long.______; pt.3: lat.______long.______; pt.4: lat.______long.______; pt.5: lat.______long.______; pt.6: lat.______long.______; pt.7: lat.______long.______; pt.8: lat.______long.______; etc.
4) If hydrostatic testing, 5) Is the discharge intermittent ____ or seasonal____? total volume of the Is discharge ongoing? Y ____ N______discharge (gals):______c) Expected dates of discharge (mm/dd/yy): start______end______d) Please attach a line drawing or flow schematic showing water flow through the facility including: 1. sources of intake water, 2. contributing flow from the operation, 3. treatment units, and 4. discharge points and receiving waters(s).
Remediation General Permit Page 12 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
3. Contaminant information. a) Based on the sub-category selected (see Appendix III), indicate whether each listed chemical is believed present or believed absent in the potential discharge. Attach additional sheets as needed.
Minimum Maximum daily value Average daily value Sample Analytical Level CAS Believed Believed # of Type Method Parameter * (ML) of Number Absent Present Samples (e.g., Used concentration mass concentration mass Test grab) (method #) (ug/l) (kg) (ug/l) (kg) Method 1. Total Suspended Solids (TSS) 2. Total Residual Chlorine (TRC) 3. Total Petroleum Hydrocarbons (TPH) 4. Cyanide (CN) 57125 5. Benzene (B) 71432 6. Toluene (T) 108883 7. Ethylbenzene (E) 100414 8. (m,p,o) Xylenes (X) 108883; 106423; 95476; 1330207
9. Total BTEX 2 n/a 10. Ethylene Dibromide 106934 (EDB) (1,2- 3 Dibromoethane) 11. Methyl-tert-Butyl 1634044 Ether (MtBE) 12. tert-Butyl Alcohol 75650 (TBA) (Tertiary-Butanol)
* Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III, as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI. 2 BTEX = Sum of Benzene, Toluene, Ethylbenzene, total Xylenes. 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England.
Remediation General Permit Page 13 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
Minimum Maximum daily value Average daily value Sample Analytical Level CAS Believed Believed # of Type Method Parameter * (ML) of Number Absent Present Samples (e.g., Used concentration mass concentration mass Test grab) (method #) (ug/l) (kg) (ug/l) (kg) Method 13. tert-Amyl Methyl 9940508 Ether (TAME) 14. Naphthalene 91203 15. Carbon Tetrachloride 56235
16. 1,2 Dichlorobenzene 95501 (o-DCB) 17. 1,3 Dichlorobenzene 541731 (m-DCB) 18. 1,4 Dichlorobenzene 106467 (p-DCB) 18a. Total dichlorobenzene 19. 1,1 Dichloroethane 75343 (DCA) 20. 1,2 Dichloroethane 107062 (DCA) 21. 1,1 Dichloroethene 75354 (DCE) 22. cis-1,2 Dichloroethene 156592 (DCE) 23. Methylene Chloride 75092 24. Tetrachloroethene 127184 (PCE) 25. 1,1,1 Trichloro-ethane 71556 (TCA) 26. 1,1,2 Trichloro-ethane 79005 (TCA) 27. Trichloroethene 79016 (TCE)
Remediation General Permit Page 14 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
Minimum Maximum daily value Average daily value Sample Analytical Level CAS Believed Believed # of Type Method Parameter * (ML) of Number Absent Present Samples (e.g., Used concentration mass concentration mass Test grab) (method #) (ug/l) (kg) (ug/l) (kg) Method 28. Vinyl Chloride 75014 (Chloroethene) 29. Acetone 67641 30. 1,4 Dioxane 123911 31. Total Phenols 108952 32. Pentachlorophenol 87865 (PCP) 33. Total Phthalates (Phthalate esters) 4 34. Bis (2-Ethylhexyl) 117817 Phthalate [Di- (ethylhexyl) Phthalate] 35. Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a. Benzo(a) Anthracene 56553 b. Benzo(a) Pyrene 50328 c. Benzo(b)Fluoranthene 205992 d. Benzo(k)Fluoranthene 207089 e. Chrysene 21801 f. Dibenzo(a,h)anthracene 53703 g. Indeno(1,2,3-cd) 193395 Pyrene 36. Total Group II Polycyclic Aromatic Hydrocarbons (PAH)
4 The sum of individual phthalate compounds.
Remediation General Permit Page 15 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
Minimum Maximum daily value Average daily value Sample Analytical Level CAS Believed Believed # of Type Method Parameter * (ML) of Number Absent Present Samples (e.g., Used concentration mass concentration mass Test grab) (method #) (ug/l) (kg) (ug/l) (kg) Method h. Acenaphthene 83329 i. Acenaphthylene 208968 j. Anthracene 120127 k. Benzo(ghi) Perylene 191242 l. Fluoranthene 206440 m. Fluorene 86737 n. Naphthalene 91203 o. Phenanthrene 85018 p. Pyrene 129000 85687; 84742; 117840; 84662; 37. Total Polychlorinated 131113; Biphenyls (PCBs) 117817. 38. Chloride 16887006 39. Antimony 7440360 40. Arsenic 7440382 41. Cadmium 7440439 42. Chromium III (trivalent) 16065831 43. Chromium VI (hexavalent) 18540299 44. Copper 7440508 45. Lead 7439921 46. Mercury 7439976 47. Nickel 7440020 48. Selenium 7782492 49. Silver 7440224 50. Zinc 7440666 51. Iron 7439896 Other (describe):
Remediation General Permit Page 16 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
Minimum Maximum daily value Average daily value Sample Analytical Level CAS Believed Believed # of Type Method Parameter * (ML) of Number Absent Present Samples (e.g., Used concentration mass concentration mass Test grab) (method #) (ug/l) (kg) (ug/l) (kg) Method
b) For discharges where metals are believed present, please fill out the following (attach results of any calculations):
Step 1: Do any of the metals in the influent exceed the effluent limits in If yes, which metals? Appendix III (i.e., the limits set at zero dilution)? Y____ N____
Step 2: For any metals which exceed the Appendix III limits, calculate the Look up the limit calculated at the corresponding dilution dilution factor (DF) using the formula in Part I.A.3.c (step 2) of the NOI factor in Appendix IV. Do any of the metals in the instructions or as determined by the State prior to the submission of this NOI. influent have the potential to exceed the corresponding What is the dilution factor for applicable metals? effluent limits in Appendix IV (i.e., is the influent Metal:______DF:______concentration above the limit set at the calculated dilution Metal:______DF:______factor)? Metal:______DF:______Y____ N____ If Y, list which metals: Metal:______DF:______Etc.
4. Treatment system information. Please describe the treatment system using separate sheets as necessary, including: a) A description of the treatment system, including a schematic of the proposed or existing treatment system:
b) Identify each Frac. tank Air stripper Oil/water separator Equalization tanks Bag filter GAC filter applicable treatment unit (check all that Chlorination De- Other (please describe): apply): chlorination
Remediation General Permit Page 17 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system: Average flow rate of discharge______gpm Maximum flow rate of treatment system ______gpm Design flow rate of treatment system ______gpm
d) A description of chemical additives being used or planned to be used (attach MSDS sheets):
5. Receiving surface water(s). Please provide information about the receiving water(s), using separate sheets as necessary: a) Identify the discharge pathway: Direct to Within facility Storm Wetlands ____ Other (describe): receiving (sewer) ____ drain______water_____ b) Provide a narrative description of the discharge pathway, including the name(s) of the receiving waters:
c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water: 1. For multiple discharges, number the discharges sequentially. 2. For indirect dischargers, indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping), such as surface waters, drinking water supplies, and wetland areas. d) Provide the state water quality classification of the receiving water______e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water ______cfs Please attach any calculation sheets used to support stream flow and dilution calculations. f) Is the receiving water a listed 303(d) water quality impaired or limited water? Y____ N____ If yes, for which pollutant(s)? ______Is there a final TMDL? Y____ N____ If yes, for which pollutant(s)? ______
Remediation General Permit Page 18 of 22 Appendix V - NOI NPDES Permit No. MAG910000 NPDES Permit No. NHG910000
6. ESA and NHPA Eligibility. Please provide the following information according to requirements of Permit Parts I.A.4 and I.A.5 Appendices II and VII. a) Using the instructions in Appendix VII and information on Appendix II, under which criterion listed in Part I.C are you eligible for coverage under this general permit? A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F, has consultation with the federal services been completed? Y____ N____ Underway____ c) If consultation with U.S. Fish and Wildlife Service and/or NOAA Fisheries Service was completed, was a written concurrence finding that the discharge is “not likely to adversely affect” listed species or critical habitat received? Y____ N____ d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII, Part I.C, Step 4. e) Using the instructions in Appendix VII, under which criterion listed in Part II.C are you eligible for coverage under this general permit? 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected, attach all written correspondence with the State or Tribal historic preservation officers, including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP.
7. Supplemental information.
Please provide any supplemental information. Attach any analytical data used to support the application. Attach any certification(s) required by the general permit.
Remediation General Permit Page 19 of 22 Appendix V - NOI
APPENDIX B
MSDS and Fact Sheets
APPENDIX C
Best Management Practices Plan (BMPP)
NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM REMEDIATION GENERAL PERMIT SPAULDING REHABILITATION HOSPITAL PARCELS 6 AND 7 - CHARLESTOWN NAVY YARD CHARLESTOWN, MASSACHUSETTS
Best Management Practices Plan
A Notice of Intent for a Remediation General Permit (RGP) under the National Pollutant Discharge Elimination System (NPDES) has been submitted to the US Environmental Protection Agency (EPA) in anticipation of temporary construction dewatering planned to occur at the Former Charlestown Navy Yard Parcels 6 and 7 project site located in Charlestown, Massachusetts. This Best Management Practices Plan (BMPP) has been prepared as an Appendix to the RGP and will be posted at the site during the time period that temporary construction dewatering is occurring at the site.
Water Treatment and Management
Construction dewatering effluent is anticipated to be pumped from well points installed in sump pits within the excavation, through hoses, and directly into a tank for sedimentation control. The effluent will then flow through any necessary treatment systems and discharge through hoses to catch basins on site that discharge to the Boston Inner Harbor or the Little Mystic Channel. Dewatering effluent treatment may consist of bag filters, granular activated carbon (GAC), ion exchange, or precipitation, as required.
Discharge Monitoring and Compliance
Regular sampling and testing will be conducted at the influent to the system and the treated effluent as required by the RGP. This includes chemical testing required within the first month of discharging, and the monthly testing to be conducted through the end of the scheduled discharge.
Monitoring will include checking the condition of the treatment system, assessing the need for treatment system adjustments based on monitoring data, observing and recording daily flow rates and discharge quantities, and verifying the flow path of the discharged effluent.
The total monthly flow will be monitored by checking and documenting the flow through the flow meter to be installed on the system. Flow will be maintained below the “system design flow” by regularly monitoring flow and adjusting the amount of construction dewatering as needed.
Monthly monitoring reports will be compiled and maintained at the site.
NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM REMEDIATION GENERAL PERMIT SPAULDING REHABILITATION HOSPITAL PARCELS 6 AND 7 - CHARLESTOWN NAVY YARD CHARLESTOWN, MASSACHUSETTS
System Maintenance
A number of methods will be used to minimize the potential for violations for the term of this permit. Scheduled regular maintenance of the treatment system will be conducted to verify proper operation. Regular maintenance will include checking the condition of the treatment system equipment such as the fractionization tanks, filters, hoses, pumps, and flow meters. Equipment will be monitored daily for potential issues or unscheduled maintenance requirements.
Employees who have direct or indirect responsibility for ensuring compliance with the RGP will be trained by the Operator.
Miscellaneous Items
It is anticipated that the excavation support system, erosion control measures, and the nature of the site and surrounding infrastructure will minimize potential runoff to or from the site. The project specifications also include requirements for erosion control. Site security for the treatment system will be covered within the overall site security plan.
No adverse affects on designated uses of surrounding surface water bodies is anticipated. The nearest surface water body is the Boston Harbor (Little Mystic Channel/Inner Boston Harbor), which borders the northern and eastern limit of the site. Dewatering effluent will be pumped to a sedimentation tank and bag filter, at a minimum, prior to discharge to the storm drains.
Management of Treatment System Materials
Dewatering effluent will be pumped directly to the treatment system from the excavation with use of hoses and sumps to minimize handling. The Contractor will establish staging areas for equipment or materials storage that may be possible sources of pollution away from any dewatering activities, to the extent practicable.
Sediment from the fractionization tank used in the treatment system will be characterized and removed from the site to an appropriate receiving facility, in accordance with applicable laws and regulations. If used, granular activated carbon and/or ion exchange resin may be recycled and/or removed from the site to an appropriate receiving facility. Bag filters, if used, will be disposed of as necessary.
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Appendix D
National Register of Historic Places and Massachusetts Historical Commission Documentation
Index by State and City, page 1, time 08/27/2009 11:28:23 Page 1 of 1 Index by State and City National Register Information System 08/27/2009 11:28:23
No filter Include filter in navigation gfedc RESOURCE Row STATE COUNTY NAME ADDRESS CITY LISTED MULTIPLE 1 MA Suffolk Hoosac Stores 1 & 2- 25 and 115 Charlestown 1985-08-14 Hoosac Stores 3 Water St.
Page 1
http://www.nr.nps.gov/iwisapi/explorer.dll/x2_3anr4_3aNRIS1/script/report.iws 8/27/2009 Welcome to MACRIS Page 1 of 1
The Massachusetts Cultural Resource Information System (MACRIS) allows you to search the Massachusetts Historical Commission database for information on historic properties and areas in the Commonwealth.
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Inventory No: BOS.CO Historic Name: Boston Naval Shipyard Common Name: Charlestown Navy Yard - Boston Navy Yard Address:
City/Town: Boston Village/Neighborhood: Charlestown; Charlestown East Local No: Year Constructed: Baldwin, C. Loammi; Billings, Joseph E.; Parris, Alexander; Treadwell, Architect(s): Daniel Architectural Style(s): Use(s): Military Other; Museum; Other Water Related; Ship Yard Archaeology, Historic; Architecture; Economics; Engineering; Industry; Significance: Invention; Landscape Architecture; Military; Politics Government; Social History; Transportation Area(s): Nat'l Historic Landmark (11/15/1966); Nat'l Register District Designation(s): (11/15/1966)
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APPENDIX E
Endangered Species Act Documentation
NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM REMEDIATION GENERAL PERMIT SPAULDING REHABILITATION HOSPITAL PARCELS 6 AND 7 - CHARLESTOWN NAVY YARD CHARLESTOWN, MASSACHUSETTS
Endangered Species Act Review
In accordance with the NPDES Remediation General Permit Appendix VII, Section D “The Steps To Determine if the ESA Eligibility Criteria Can Be Met”, no endangered species or threatened species or critical habitat are in the proximity of this project site or the points of discharge as verified in the attached ESA Section 7 letter, dated 30 November 2010. The project site meets Criterion A.
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