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Home My WebLink About0125 HARBOR BLUFFS ROAD - HAZMAT J �5 ed. 325- �ao I I I ®/® S M E A KWING YOU ORGANIZED No.10334 2-153L MADE IN USA GET ORGANISED AT SMEAD.COM IMMEDIATE RESPONSE ACTION COMPLETION REPORT WITH PERMANENT SOLUTION STATEMENT AND SUPPORTING DOCUMENTATION RTN 4-0028801 Evans Residential Property 125 Harbor Bluff Road [Map 325, Parcel 1201 Hyannis, MA 02601 Job Number K11381 JULY 209 2021 T r j 1 -EA I BENNETT ENVIRONMENTAL t ASSOCIATES,LLC. " ,tit t :+V.... 1 t•r 11-1, f !^isnY. _, •ASSESSMENT •REMEDIATION •RESOURCE MANAGEMENT ' a i 4 i I 1573 Main Street,Brewster,AAA 02631 L 508-896.17064 Fax 508-896-5109 www.bertnett-ea.com BENNETT ENVIRONMENTAL ASSOCIATES, LLC. A NATURAL SYSTEMS UTILITIES COMPANY LICENSED SITE PROFESSIONALS ® ENVIRONMENTAL SCIENTISTS ® GEOLOGISTS ® ENGINEERS 1573 Main Street, Brewster,MA 02631 ® 508-896-1706 ® Fax 508-896-5109 6 www.bennett-ea.com Job#K11381 ' July 20, 2021 Mr. Andrew Jones, Case Officer MA DEPARTMENT OF ENVIRONMENTAL PROTECTION(MA DEP) Southeast Regional Office (SERA) Bureau of Waste Site Cleanup (BWSC) 20 Riverside Drive Lakeville, MA 02347 RE: IMMEDIATE RESPONSE ACTION COMPLETION AND PERMANENT SOLUTION STATEMENT Evans Residence -RTN 4-28801 125 Harbor Bluffs Road [Assessor's Map/Parcel ID:325-120] - Hyannis, MA 02601 Dear Mr. Jones, j BENNETT ENVIRONMENTAL ASSOCIATES,LLC. (BEA)has prepared the following Immediate Response Action Completion(IRAQ and Permanent Solution Statement(PSS) report with Supporting Documentation, as a summary of the response actions and environmental assessment activities performed since release discovery on May 18, 2021. Immediate Response Actions were implemented to address significant environmental impacts and exposure risks associated with a historical release of home heating oil to an earthen crawlspace under the former dwelling, discovered during demolition of the structure. Subsequent to Remedial Response Actions, including contaminated soil excavation and groundwater pumping, analytical results of soil and groundwater samples report all concentrations of petroleum hydrocarbons below the applicable and most stringent Method 1 Risk Characterization Standards,documenting a condition of No Significant Risk. A Permanent Solution Statement without conditions, is thereby supported for project closure, as framed within the provisions of the MA Contingency Plan(MCP),regulated under 310 CMR 40.0000. This work proceeded under direct LSP oversight in a manner consistent with the MCP Response Action Performance Standards (RAPS) pursuant to 310 CMR 40.0191 and the QA/QC policies of BENNETT ENVIRONMENTAL ASSOCIATES, LLC. The facts and statements herein are, to the best of our knowledge, a true and accurate representation of the Site activities, remedial response actions and environmental conditions associated with the project, as acknowledged by the certifications on the enclosed BWSC-104 and BWSC-105 forms. ENVIRONMENTAL CONDITIONS [Refer to Appendix A] Subject Property The subject property, at 125 Harbor Bluffs Road, is located immediately south of the 1 EMERGENCY SPILL RESPONSE ® WASTE SITE CLEANUP a SITE ASSESSMENT ® PERMITTING ® SEPTIC DESIGN&INSPECTION DESIGN BUILD 6 OPERATION&MAINTENANCE 6 WATER SUPPLY DEVELOPMENT ® WASTEWATER TREATMENT 6 FIELD SERVICES JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 2 OF 14 IRAC-PSS,RTN 4-28801 intersection of Lookout Lane and Harbor Bluffs Road, in the Village of Hyannis in Barnstable, MA (Latitude 41.64349 N, 70.27648 W). The property is situated on Hyannis Harbor some 1/4 mile south of the downtown area [Refer to Figure 1]. The property contains 0.66 acres of land area and was previously developed by a four-bedroom dwelling which has been razed. A new similar dwelling is planned and permitted for construction. The surrounding area is heavily developed in similar residential use. Access to the area of release is presently restricted with temporary fencing and signage,with high frequency/high intensity of use during construction activities. The occupants, on-site workers and visitors to the property are identified as the primary human receptors for potential exposure risks associated with the former soil and localized groundwater impacts. The primary environmental receptor is Hyannis Harbor, located immediately south of the site. Site specific hydrologic references indicate groundwater exists at approximately elevation 4' NGVD, within 6' of ground surface. Regional groundwater contours indicate a southeasterly flow direction towards the Hyannis Harbor, which abuts the Site to the southeast [Refer to Figure 2]. Site specific groundwater flow measurements show groundwater is tidally influenced,both to the east and west, of the southerly groundwater flow direction. According to the Mass GIS Priority Resource Map,the subject property is not located within the Zone II Protective Radius of a Public Water Supply (PWS)well,nor is it located within the Zone A Protective Radius of any surface water reservoir. The subject property and immediately surrounding area to the south and west are shown within a Medium-Yield Potentially Productive aquifer and within an EPA-designated sole source aquifer, as is all land area east of the Cape Cod Canal. As such, the Site and surrounding area are located within a Potential Drinking Water Source Area(PDWSA) [Refer to Figure 3]. Based on the environmental setting and physical location of the property, the RCS-1 and RCGW-1 Reportable Concentrations apply. Additionally, in consideration of"significant risk"under Method 1 —Risk Characterization, the GW-1, GW-2, and GW-3 groundwater standards apply at the Site. Likewise, based on frequency/intensity of use and accessibility of soils, the S-1 and S-2(GW- 1, GW-2, GW-3) Method 1 —Risk Characterization soil standards are applicable to soil impacts in the qualification of"significant risk". Site Description The Defined Site, as that portion of the subject property where oil or hazardous materials (OHM) were released, migrated, or otherwise came to be located, is that portion of the subject property located adjacent to the garage and breezeway of the former dwelling on the eastern portion of the property. The Defined Site is roughly centered on the release as a rectangular area approximately 37' (L)x 28' (W), covering some 1,036 SF of land area [Refer to Site Plan—Appendix A]. BACKGROUND/PRELIMINARY ENVIRONMENTAL ASSESSMENT - On the morning of May 18, 2021, Northeast Construction personnel were demolishing the I ' JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K 113 81 PAGE 3 OF 14 IRAC-PSS,RTN 4-28801 existing dwelling,when petroleum staining on a concrete block wall and a fuel oil odor was observed. The impact was located on the eastern gable end of the crawlspace under the dwelling, adjacent to the attached garage. The source of the release was not apparent but a concrete pad for a former exterior above ground storage tank(AST)was noted on the opposite end of the garage. A double walled tank was located on this pad as having replaced a former AST at this location prior to 2008. Apparently, fuel lines had run through the area of the release enroute to the oil burner in a small partial basement, located in the center of the main house [Refer to Photograph 1]. M k 1 r Air# i VY I Ile Al Yj � $"' r 4 r �-y ✓ fie+ }�y}�R � ��,��q`,fi._ 5�'�+P' vb. F3 PHOTO 1: Release area along the crawlspace foundation wall adjacent to the garage. Note staining of concrete block foundation wall and discolored soils within HB-1 sampling location. After discovering the soil impact and reporting it to the general contractor and property owner, BEA was contacted on May 18, 2021, to investigate the release to determine Notification and Remedial Response liabilities under the MCP. BEA responded to the site and advanced four hand borings, to determine the extent and magnitude of soil impact. Hand boring HB-1 was advanced within the area of staining from 5' to 8' below grade. Soil samples were collected in two-foot intervals and placed in 8-ounce glass jars covered with aluminum septa. The soil samples were then screened with a photoionization detector(PID)by"j ar-headspace"method. Field screening results from HB-1 reported total organic vapor (TOV) concentrations from 61.5 to 78.1 parts per million by volume JULY 20,2021 EVANS—125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 4 OF 14 IRAC-PSS,RTN 4-28801 (ppmv), increasing with depth. Hand boring HB-2 was advanced some 10' west of HB-1,within the footprint of the former dwelling along the foundation wall. Soil samples from HB-2 reported TOVs ranging from 2.9 to 0.4 PPmy and decreasing with depth in the 5-8' samples collected. Hand boring HB-3 was advanced some 5' north of HB-1 to 5-8' below grade, with TOVs reported as 47.4 to 53.4 ppmv from 5-8' below grade,increasing with depth. Hand boring HB-4 was advanced some 9' south of HB-1 along the foundation wall. Soil samples from HB-4 collected from 5-8' below grade reported TOV concentrations between 0.8 and 0.1 ppmv and decreasing with depth. In all locations, groundwater was noted at 6-7' below the surrounding grade. Select soil samples were preserved in the appropriate laboratory containers and submitted to Alpha Analytical Laboratory for extractable petroleum hydrocarbons (EPH) with polycyclic aromatic hydrocarbons (PAHs) analysis to quantify the presence of petroleum compounds in the soils. BEA returned to the Site on May 20, 2021. A sheen was observed on standing water within the HB-1 location. A sample was collected to evaluate what appeared to be localized groundwater impact from contact with impacted soils. This sample was collected to evaluate potential exposure risk to site workers, Notification requirements, disposal options and in consideration of appropriate Remedial Response Actions. A sample was collected from the standing water in appropriate containers and submitted to Alpha Analytical for EPH/PAHs as well as volatile petroleum hydrocarbons (VPH) and target benzene, toluene, ethylbenzene, and xylene (BTEX) analysis to quantify the presence of petroleum compounds in groundwater at the site. Additionally, total dissolved solids and sodium were analyzed in consideration of saltwater intrusion. Laboratory results for soil samples collected were received on May 21, 2021. The results reported concentrations of 2-Methylnaphthalene above the most stringent S-1/GW-1 Method 1 Risk Characterization Standards in soil samples collected from HB-1 and HB-3. Soil samples from HB-2 and HB-4 reported EPH and PAHs as Non-Detect. The results are summarized below in Table 1. Table 1: Soil Sample Results Compared To Method 1 S-1/GW-1 Criteria 125 Harbor Bluffs Rd. Hyannis, MA CLIENT SAMPLE ID Method 1 H13-1:54 HB-2:5-8' HB-3:5-8' HB-4:5-8' SAMPLING DATE Standards 18-MAY-21 18-MAY-21 18-MAY-21 18-MAY-21 LAB SAMPLE ID S-1/GW-1 Units L2126393-01 L2126393-02 L2126393-03 L2126393-04 Extractable Petroleum Hydrocarbons 2-Methylnaphthalene 0.7 mg/kg 5.16, ND(<0.42) 5.87 ND(<0.401) Acenaphthene 4 mg/kg 1.44 ND(<0.42) 1.63 ND(<0.401) C11-C22 Aromatics mg/kg 684 ND(<8.4) 631 ND(<8.02) C11-C22 Aromatics,Adjusted 1000 mg/kg 674 ND(<8.4) 621 ND(<8.02) C19-C36 Aliphatics 3000 mg/kg 299 ND(<8.4) 270 ND(<8.02) C9-Cl8 Aliphatics 1000 mg/kg 986 ND(<8.4) 948 ND(<8.02) Naphthalene 4 mg/kg ND(<0.444) ND(<0.42) ND(<0.43) ND(<0.401) Phenanthrene 10 mg/kg 1.12 ND <0.42 0.693 ND <0.401 Green shading indicates analytes reported above applicable standards Bold numbers indicate those standards exceeded, ND= Non-Detect Laboratory results for the groundwater sample collected from TW-1 were received on May 25, 2021. The results for the stand /V ing water sample reported fractional EPHPH compounds and 2 methynapthalene impacts exceeding the Method 1 GW-1 Standards and fractional C9-C18 Aliphatics exceeding the GW-2 Standards. These results are summarized below in Table 2. f DULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 5 OF 14 IRAC-PSS,RTN 4-28801 Table 2: Groundwater Sample Results Compared To Method 1 Groundwater Standards 125 Harbor Bluffs Rd. H annis, MA CLIENT SAMPLE ID HB-1/TW-1 SAMPLING DATE 20-MAY 21 LAB SAMPLE ID Method 1 Standards L2126733-01 GW-1 GW-2 GW-3 Units General Chemistry Solids, Total Dissolved NA NA NA u /l 210000 Chloride NA NA NA u /I 64000 MCP Total:Metals Sodium, Total NA NA NA u /1 36800 Volatile Petroleum Hydrocarbon's Benzene 5 1000 10000 u /I ND(<2) C5-C8 Aliphatics__—,_.__— -_.._ _—__— —._._ ._ ug/I -- - ND (<100) - - 05-C8 Aliphatics, Adjusted 300 _ 3000 —_ 50000 ug/I ND (<100)— C9_C10 Aromatics 200 4000 50000 ug/1 748 C9-C12 Aliphatics ug/1 1230 C97C12 Aliphatics Adjusted 700 5000_ 50000 ug/1 447 _ — Ethylbenzene_ 700 _ _20000 _ 5000 ug/I 6.45 _ —_—� Mhle tert bpy1 ether _ 70 _ 50000 _ 50000 ug/1 _ — _ND Naphthalene 14 __0 700 20000 ug/1 66_4 .. _. o-Xylene __ _10000 3000 5000 u'9 1 15.9 p/m Xylene 10000 3000 _ 5000 ug/1 11 Toluene 1000 50000 40000 u /1 ND <2 ;EPH w/Targets via GCMS-SIM 2-Methylnaphthalene _ 10 2000 20000 ug/I_ 55.9 Acenaphthene 20 10000 ug/l 2.36 C11-C22 Aromatics ug/I 4100 C11-C22 Aromatics, Adjusted 200 50000 5000 ug/I 4040 C19-C36 Aliphatics 14000 50000 u9/1 3950 C9-Cl8 Aliphatics 700 5000 50000 _ ug/1— 8510 ----------- __ — _—--- ._Naphthalene 140 700 2000 u9L1 ._. ._. 39.6-. . Phenanthrene 40 10000 u /I 17.1 Green shading indicates analytes reported above applicable standards Bold numbers indicate those standards exceeded, ND= Non-Detect Based on these laboratory results, a 20' x 20' x 4'(D) area of significant soil impact (> S- 1/GW-1)was indicated, and a Mass Balance Computation of estimated fuel oil release was computed as indicating a release of more than 10 gallons of fuel oil. The results indicated the likelihood of a 2- Hour Reportable Condition at the Site, and BEA made notification to the DEP on May 21, 2021 to seek verbal approvals to expedite appropriate response actions. BEA requested verbal authorization to excavate up to 75 cubic yards of soil and removal of up to 3,000 gallons of impacted groundwater. MA DEP personnel assigned Release Tracking Number (RTN) 4-28801 to the Site and granted the requested response actions under the IRA [Refer to BWSC-101 —Appendix C]. Additionally, BEA contacted Barnstable Conservation to review the planned remedial actions, to seek permission to proceed with this work under the existing Order of Conditions (SE3-5786). Such permissions were granted in communications from Darcy Karle (5118/21). IMMEDIATE RESPONSE ACTIONS [Refer to Appendix B] f JULY 20,2021 EVANS—125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 6 OF 14 IRAC-PSS,RTN 4-28801 Based on the IRA Plan, outlining the mechanical removal of up to 75 cubic yards of impacted soil and 3,000 gallons of groundwater, site work commenced on May 26, 2021. In order to facilitate dewatering during soil removal, BEA directed Northeast Construction personnel to establish a groundwater sump. The sump was installed to approximately 10' below grade and backfilled with crushed stone. A vacuum truck operated by Global Remediation Services (Global) was then used to collect groundwater. Once dewatering had begun,BEA directed Northeast Construction to excavate impacted soils from the west to the east, in the area of identified impact. BEA personnel provided oversite and field guidance to direct soil removal using field screening and laboratory results from the preliminary assessment conducted. a � PHOTOGRAPH 2: Area of soil removal facilitated by dewatering. Note sump and vac-truck hose in foreground and natural coloration of soils in bottom of hole area at the extent of excavation. Soil samples were collected from the sidewalls of the excavation from 4-8' for PID screening. It was noted that the dark color (brown/black) of soils in the sidewall and bottom of hole correlated with elevated PID response. Field screening results reported low PID readings (< 9.3 ppmv) in all representative sidewall (SW) and bottom-of-hole (BOH) samples collected, indicating the extent of the excavation had been met. Based on the homogeneity of soils and field screening results, sidewall samples were collected from the north, south,east,and west locations with two soil samples(east and west) collected from the bottom of excavation for laboratory analysis. The final dimensions of the excavation were approximately 16' x 16' to a depth of 8' below grade. In addition, 307 gallons of impacted groundwater was pumped from the sump during soil removal operations. Approximately 50 cubic yards of impacted soil were stockpiled on, and covered with plastic sheeting,pending off-site disposal. Samples were collected from the stockpile were also collected for JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 7 OF 14 IRAC-PSS,RTN 4-28801 disposal characterization under COMM-97 regulations,in consideration of soil disposal at the Bourne Integrated Solid Waste Management(ISWM) Facility. BEA returned to the site on June 4, 2021, with Bronson Drilling to advance test borings and install three groundwater monitoring wells. Monitoring well MW-1 was installed in an assumed upgradient location north of the excavation. Monitoring wells MW-2 and MW-3 were installed in assumed downgradient locations south of the excavation and intermediate to Hyannis Harbor. All wells were located within 20' of the edge of the excavation. At the time of monitoring well installation, standing water within the excavation was observed to be clear and free of any odor or sheen. Representative groundwater samples were collected from each well for EPH/PAH and VPH/BTEX analysis. The wells were developed by removing 1 Ox the well volume and pumping until clarity.Low-flow sampling methodology was then used to collect samples,after field parameters(pH, dissolved oxygen, conductivity, and temperature) had stabilized. Laboratory analytical results for endpoint soil samples collected from the extent of the excavation were reported on June 13, 2021. The results reported all concentrations of fractional EPH/4-PAHs and VPH/BTEX analytes as Non-Detect (ND) or less than the applicable and most stringent S-1/GW-1, Method 1 Risk Characterization standards. In all cases wherein the detection limit (50% of reporting limit) is considered under CAM, the ND reporting limit concentrations are less than the strictest S-1/GW-1 standards (2-methynaphthalene and ethylbenzene). The results of laboratory analyses are summarized below in Table 3. TABLE 3: Endpoint Soil Sample Results Compared To Method 1 S-1/GW-1, GW-2, GW-3 Criteria 125 Harbor Bluffs Rd. Hyannis, MA _ CLIENT SAMPLE ID Method 1_._ SW-N_4-8'_ .SW-S:4-8' -SW-E:4-8' .SW-W 4-8' 8' BOH-W @ 8' SAMPLING DATE Risk Characterization 26-MAY-21 26-MAY 21 26-MAY-21 26-MAY-21 26-MAY-21 26-MAY-21 LAB SAMPLE ID Standards L2128325-01 L2128325-02 L2128325-03 L2128325-04 L2128325-05 L2128325-06 S-1/GW-1 S-1/GW-2 S-11GW-3 Units Volatile Petroleum Hydrocarbons Benzene 2 40 _.._ _._ 40 rn 0 ND(<0_311) 0 IN D�<0.086). C5-C8 Aliphatics mg/kg, ND(<6.36). -ND(<15.6) .ND,(<7 83) ND(-4LLN) ND(<4.31) _N-P C5-C8 Aliphatics,Adjusted 100 _ 100- 100_ mg/kg ND <( 6.36) ND(<156) ND(<7.83) ND(<4.86) ND(-4.31) ND(<4.31) C9-C10 Aromatics 100_ 100 100 mg/kg ND(<7 83) ,ND(<4.86 ND L<4 31) ND(<4 31) C9-C12 Aliphatics _ mg/kg .ND( <4.31) ND(<4_39) -------- __C9-C12 Aliphatics,Adjusted 1000 1000 1000 mg/kg .ND(<6 36)__ND.(<15.6_ .ND(<7.8 . - 86) ND(<4.31)_ ND <4.31) Ethy_benzene 40 500 500 mgL 27 D <0.311 A97) 86) ND <0.086 Methyl tert,buty_I ether 0.1 100 100 mg/k gND(<Q064) ND(<0.1'56) ND(<0.078),_ND(<0.049) ND,(<0_043) ND(<0_043) --- ___-- _ _ Naphthalene 4 20 _500 _ oN _ND(<0.254 ND(<0.623) ND(<0.313) ND(<0.194L ND(<0.172) ND(<0.172) o-Xylene 400 100 500 mg/kg D( 0.II ) 0.311). ND < 7 ND(<0 097< p/n yjene 400. 100 - 500. mg/kg ND(<0127) ND(-0O ) ND(<0.157) ND(<0,097) ND(<0,086) ND(<0_086) Toluene 30 500 500 /k ND <0.127 ND <0.311 ND <0.157 ND <0.097 ND <0.086 ND <0.086 _Extractable"Petroleurn Hydrocarbons _ 27Met_hylnaphthalene 0.7 . 80 300 mg/kg ND(<0 442)-ND(<D.722) ND(<0,482) ND(<0_397) ND(<0.388) -_ Acenaphthene -4 1000 __1000 m 2)g/kg _ND(<0.44 ND(<0.722) ND(<0.482) ND(<0.397) ND(<0.388) ND(<0.394) _._... .._C11_C22 Aromatics . . - - ---- mg.69 --19.5- 24.2 _ _ ..11...._..._ND(`7.93, ND(`7:??)._.NI?:7.87)- C11-C22 Aromatics Adjusted ._ 1000 1000 1000 rn kg 19.5. 24 22 11 ND(<7.93) .ND(<7.77) ND.( .J__. _. C19-C36 Aliphatics 3000 3000 3000 mg/k� 13,1 ND(<14.4) ND(<9.63), ND(<7 93) ND(<7.77) ND(<7.87) C9-C18 Aliphatics 1000 1000.._ 1000 _rrK 13.6 _ND(<14.4) ND.(<9.63) ND(<7.93) ND(<7.77) ND(<7;87) Naphthalene 4 20 500 mg%kg ND(<0.442) ND(<0 722) ND(<0.482) ND(<0.397) ND(<0.388) ND(<0.394) Phenanthrene 10 500 500 /k ND <0.442 ND <0.722 ND <0.482 ND <0.397 ND <0.388 ND <0.394 Green shading indicates analytes reported above applicable standards Gray shading represents Non-Detect with laboratory reporting limit greater than the Method 1 Standard Bold numbers indicate those standards exceeded ND=Non-Detect I JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 8 OF 14 IRAC-PSS,RTN 4-28801 Laboratory analytical results for groundwater the samples collected from the monitoring wells were reported on June 17, 2021. The results reported all concentrations of fractional EPH/PAH and VPH/BTEX as Non-Detect. In all cases wherein the detection limit (50% of reporting limit) is considered under CAM, the ND reporting limit concentrations for groundwater are less than the strictest GW-1, GW-2, and GW-3 standards (benzo(a)pyrene). The results of these laboratory analyses for groundwater at the monitoring well locations are summarized below in Table 4. Table 4: Groundwater Sample Results Compared To Method 1 Groundwater Standards 125 Harbor Bluffs Rd. Hyannis, MA CLIENT SAMPLE ID MW-1 MW-2 MW-3 SAMPLING DATE _ 04-JUN-21 04-JUN-21 04-JUN-21 LAB SAMPLE ID L2130129-01 L2130129-02 L2130129-03 GW-1 GW-2 GW-3 Units Volatile Petroleum Hydrocarbons Benzene 5 1000 _ 10000 ug/1 _ ND <2 ND( ND(<2L _C5-C8 Aliphatics - _._ ....... ug��. ND(<100)_. . ....ND(<100) _ND(<100) C5-C8 Aliphatics,Adjusted 300 3000 50000 ug(I ND�<100) ND(<100) ND(<100) --- - - - .. - _C9-C10 Aromatics 200 4000 50000 ug(I ND(<100) ND(<100) ND(<100) C9-C12 Aliphatics _ ug/1 ND(<100) ND(<100) _ND(<100) C9-C12 Aliphatics,Adj _ _usted 700 5000 50000 ug/I ND(<100) _ND(<100) NDJ<100) Eth (benzene- 700 20000 - 5000 u I ND <2 ND <2 ND <2 Methy_I tert butyl ether 70 50000 50000 ug/I ND(<3) ND <3) _.. . .. Naphthalene-_..140_ 700. . . ....20000 .. .. ugh[. ._ o-Xylene 10000.-.... 3000 . ......5000 ug/i.... . _.N��`2�.-.__.. ND p/m Xylene . 10000 3000 5000 u9/1 ND(<2) ND(<2).... ND(<?) __ _. Toluene 1000 50000 40000 u /l ND <2 ND <2 ND <2 EPH w/Targets via-GCMS-SIM 2-Methylnaphthalene 10 2000 20000 ug/l ND(<0.4) ND(<0.4) ND(<0.4) _. _--Acenaphne . _ .2 __. . . .__ ._ 10000 . - l_ .4) - NNDD((<<00..44) _0_ / 0 ,Acenaphtyene 30 1000 40 _. ugI ND, .4). - 1 )- Anthracene _ 60 - 30 _ _ug/l _ (<0.4) ND <0.4 - _ND <0.4 Be nzo(a)anthracene 1 1000 ug/I_ ND(<0.4) NND(<0.4)� ND(<0.4) Benzo(a)pyrene 500 ug/l _ND_ <0 2� D <0.2) _AND 0.2)_ Benzo(b)fluoranthene 1 ._ .._._..._._ .. .. 400 ND(<0:4) ND(<0.4) ND.(1<0.4) - - ----- Benzo(ghi)perylene 5-0--- ...... .._20- .... ug/I. ND(<0.4).. ND :< 4)._ ND Benzo(k)fluoranthene 1 100 ug/l ND(<0_4) ND(<0_.4) ND(<0.4) _._. . .. .. - - . C111-C22 Aromatics _ .. _-..._. .. - - - .u9/1.'... ..ND(<100) ND(<10J.-_. .._._ND j<109)_... C11-C22 Aromatics,Adjusted 200 50000- 5000_ ug%I ND(<100)_ ND(<100) ND(<100L C19-C36 Aliphatics 14000 50000 ug/l ND(<100) -ND(<100) ND<<100) C9_C18 Aliphatics 700 ... 50000 _ ug/I ND(<100) _ NDS<100) _ND(<100) __.. Chrysene.. .. ..2 _. :. _ ._ . 70_ _.. ..._ug/1, ._ ._ .N1 1<0 4) .._ _ND(<0.4) ND(<0.4)..... Di benzo(a,h)anthracene 0.5 40 ug%I ND(<0.4) -ND(<0.4) ND(<0�4) Fluoranthene 90 200 ugll ND(<0.4) ND(<0.4) Fluorene .....30.: .. .. ..... . _40_.. ._. ....ug7� ....NDJ<0.4) .... .. ND(<0 ---. _Indeno(1L23-cd)Pene.._.. 5 100 ) __ -----_ - LL_._ _ _. .-. Naphthalene 140 70_0 20000:_... . 1_ _ D(<0.41 __ ._._ ug/ _. .ND_ . ND.(G04) Phenanthrene - 40-- ----- - - - 10000 - - ug/1- --ND(<0.4)- -- ND(<0.4) ._.__ND_(`0 P rene 60 20 u !I ND <0.4 ND <0.4 ND <0.4 Green shading indicates analytes reported above applicable standards Gray shading represents Non-Detect with laboratory reporting limit greater than the Method 1 Standard - Bold numbers indicate those standards exceeded, ND= Non-Detect A sieve analysis was performed on a composite soil sample from the water-bearing zones in borings TB-1 and T13-2. The analysis was performed to determine grain size distribution and soil type JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 9 OF 14 IRAC-PSS,RTN 4-28801 to estimate hydraulic conductivity for solute transport in groundwater. Soils in the shallow aquifer below the surficial clayey sediments were found to be mainly coarse sand with an estimated hydraulic conductivity of 200 ft/day. Given a hydraulic gradient of 0.00585'/foot across the Site, the groundwater velocity was estimated as 4.68 feet/day. Time of Travel calculations to downgradient monitoring wells MW-2 and MW-3 was calculated as within 8 days,with a retardation value of 20% applied. As such, the solute transport and time of travel calculations support the conclusion of localized groundwater impact in the area of the historical release,wherein groundwater samples from downgradient monitoring wells reported concentrations of petroleum hydrocarbons as ND. The sieve analysis results and time of travel calculations are included for reference in Appendix B. The analytical results for soil samples collected at the extent of excavation and groundwater samples collected from representative monitoring wells indicate that a condition of No Significant Risk has been achieved as a result of the remedial response actions performed.These results indicated the response actions undertaken under the IRA were successful and support a Permanent Solution Statement for project closure. The laboratory results are further discussed and qualified under CAM protocols and Representativeness Evaluation and Data Usability Analysis (REDUA) in the Risk Characterization section of this report. The laboratory reports and summary spreadsheets are included for reference in Appendix D. Remedial Waste Management From July 7 to July 8,2021,three loads of petroleum-contaminated soils were transported off- site under an approved MA DEP Bill of Lading and Waste Characterization profile. The soil was transported to the Bourne ISWM Facility in Bourne, MA for use as daily cover. A total of 74.92 tons was delivered as representing some 50 cubic yards of soil. The Attestation of Shipment Completion document, verifying receipt of the material, is provided for reference in Appendix C. As previously noted, 307 gallons of impacted groundwater was removed by a vac-truck and managed as remedial waste as part of the IRA. This oil contact water was transported by Global Remediation to Tradebe Treatment&Recycling of Stoughton,LLC,under a Uniform Waste Manifest on May 26, 2021. The Uniform hazardous Waste Manifest is included for reference in Appendix C. RISK CHARACTERIZATIONAMMINENT HAZARDS [Refer to Appendix D] As presented, the S-1 and S-2 (GW-1/GW-2/GW-3) soil categories are applicable in consideration of Method 1 Risk Characterization,consistent with the provisions of 310 CMR.40.0933. These standards were developed to evaluate potential ingestion and particulate inhalation based on accessibility, frequency, and intensity of use of the soils. The GW-1, GW-2 and GW-3 groundwater categories further apply to Method 1 Risk Characterization per 310 CMR 40.0932. These standards were developed to evaluate potential ingestion, inhalation, and dermal contact exposures, and evaluate potential leaching to groundwater and environmental impacts. For the purposes of risk characterization, considering reasonably foreseeable future use of the Site, the strictest S-1 (GW-1) Method 1 Risk Characterization soil standards are also weighed against laboratory results in consideration of all foreseeable activities and use of the property. Soil JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 10 OF 14 IRAC-PSS,RTN 4-28801 After the completion of contaminated soil removal, laboratory analyses of end-point samples reported all concentrations of EPHJPAHs and VPH/BTEX compounds as ND or significantly below the applicable and most stringent S-1/GW-1 Method 1 Risk Characterization standards. Such is prefaced by the fact that in the case of the SW-S: 4-8' sample, wherein there were elevated reporting limits for 2-methynaphthalene and ethylbenzene. In both cases,the detection limit concentrations, as 50% of the reporting limit, is less than the S-1/GW-1, Method 1 — Risk Characterization standards and reported non-Detect. As such, all the analytical data for soils at the extent of the excavation,both discretely and as an Exposure Point Concentration,support a finding of No Significant Risk in support of a Permanent Solution Statement without any conditions or stipulations. Groundwater Based on the Site being within a Potential Drinking Water Supply Area (PDWSA), and the average depth to groundwater being less than 15' from grade, the GW-1, GW-2, and GW-3 groundwater categories are considered applicable in consideration of Method 1 - Risk Characterization, as consistent with the provisions of 310 CMR 40.0932. The June 2021 sampling of the monitoring wells, as reflective of groundwater impacts, reported all concentrations of EPH/PAHs and VPH/BTEX as ND wherein the reporting limit concentrations are less than the Method 1, GW-1, GW-2, and GW-3 criteria except for benzo(a)pyrene, which has a reporting limit concentration equal to the GW-1, Method 1 — Risk Characterization standard. Wherein the detection limit is 50% of the reporting limit, this compound is not present above the standard and therefore demonstrates a condition of No Significant Risk associated with groundwater at the Site in support of a Permanent Solution Statement. Indoor Air The results of laboratory analysis of endpoint soil samples and representative groundwater samples noted above, do not constitute a threat of vapor intrusion and the vapor intrusion pathway is incomplete as support a finding of No Significant Risk. As such,no sub-slab soil vapor or indoor air testing was performed or deemed necessary to support a Permanent Solution Statement without conditions. DATA USABILITY ASSESSMENT & REPRESENTATIVENESS EVALUATION The following presents a discussion of the Site information used to support the Permanent Solution Statement as required by 310 CMR 40.1056(2) (k) and incorporating the guidance provided in MA DEP Policy WSC-07-350. It provides an evaluation and demonstration of the adequacy of the spatial and temporal data sets used to support the PSS and makes conclusions on the accuracy, precision and sensitivity of the data used, consistent with the internal QA/QC Policies of BEA [Refer to Appendix F]. Conceptual Site Model DULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 11 OF 14 IRAC-PSS,RTN 4-28801 A fuel oil release was discovered by an excavation contractor, during construction activities at the Site to raze the existing dwelling. The release is presumed related to the use of fuel oil at the property for domestic heating purposes and may be related to an underground storage tank (UST), removed in 1988 or possibly an aboveground storage tank (AST) that replaced the UST. The oil infiltrated shallow soils from approximately 4' below grade to the capillary fringe at 8' below grade. The release occurred in clayey soils,which appears to have limited the spread of soil and groundwater impacts to a finite area under the footprint of the former dwelling. Immediate Response Actions were expedited under verbal approvals and resulted in the removal of 74.92 tons (±50 cubic yards) of petroleum-contaminated soils from an approximate 16' x 16' area from 4-8' below grade. A vac-truck was used to remove impacted water during soil removal operations, resulting in 307 gallons of impacted groundwater removed. The soil and groundwater were transported off-site and disposed of as remedial waste at licensed facilities. End-point soil sampling of the sidewall and bottom of hole areas reported EPH/VPH and target analyte concentrations as ND or significantly below the applicable and most stringent S-1/GW- 1 Method 1 Risk Characterization standards, supporting No Significant Risk. Monitoring wells installed downgradient of the release area were sampled and reported all concentrations of EPH/VPH and target analytes as ND,supporting No Significant Risk.Time of travel calculations indicate solute transport from the release area to downgradient monitoring wells is approximately 8 days. Given the historical nature of the release,any dissolved-phase petroleum would have already been transported to the downgradient wells from the release area. This qualifies the representativeness of the groundwater analysis and confirms no residual groundwater impact. Field Screening PID screening and field observations were used to qualify significant impact in soils and to make informed, dynamic decisions in the field in advance of submitting samples for MA Certified analyses. In some cases, Dexsil PetroFlag testing was conducted to qualify TPH concentrations in the field. Samples with higher levels of odor or PID readings were assumed to be more contaminated than those samples with lower levels. Comparison of visual observations, PID screening results and laboratory analytical data indicates that the field screening data correlates well with the analytical data. Sampling Locations Contaminated soil removal was performed based on field PID/Dexsil PetroFlag screening and visual observations, as work progressed from contaminated soil to clean soil. PID/Dexsil PetroFlag screening was used to qualify the horizontal and vertical extent of contaminated soil, in support of excavation and loading activities. EPH and VPH laboratory analysis were used to evaluate the impacted soils based on the nature of the contaminant being fuel oil. Soil samples were collected for analyses from the extent of soil removal from representative bottom-of-hole and sidewall areas as critical samples. All end-point soil samples were preserved for EPH/PAH and VPH/BTEX analysis. The samples were placed in appropriately preserved laboratory f JULY 2d,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 12 OF 14 IRAC-PSS,RTN 4-28801 containers in the field and stored on ice in a cooler, pending shipment to the laboratory under a properly executed chain-of-custody. Monitoring well installation was performed immediately outside the release area to qualify groundwater quality immediately downgradient of the release area and intermediate to identified receptors. The monitoring well screens were installed across the groundwater interface, as representative of petroleum impact to groundwater. Field duplicates or trip blanks for soil samples were not collected nor considered necessary because the Disposal Site was small, soil removal operations had produced clean conditions along the majority of exposure points and the contamination was fuel oil. Temporal Data Laboratory results from soil samples collected from the extent of excavation report no residual impact above the most stringent S-I/GW-1 Method 1 Standards, supporting No Significant Risk. Groundwater samples from representative downgradient monitoring wells indicate that historical release did not impact groundwater quality. Laboratory data from soil and groundwater indicate the vapor intrusion pathway is incomplete. Therefore, there is no need to gather temporal data to further evaluate the impacts of these parameters. Field Completeness The analytical data set is complete. Data from the sidewall and bottom-of-hole areas was obtained as representing the extent of contaminated soil removal. Groundwater data represents groundwater quality within and down-gradient of the area of release as evaluated under projected solute fate and transport modeling. The complete data set supports the PSS wherein all QA/QC thresholds and Presumptive Certainty requirements were met or technically justified. Data Inconsistency No inconsistent data was identified. Visual observations, odors and field screening results were generally well-correlated. No inconsistency was identified between field screening of end-point soil samples and their respective laboratory analyses. Results of groundwater sampling are consistent with field observations and solute fate and transport modeling. Data Not Used The analytical data for soil samples collected at the extent of excavation was considered and used to support the PSS. The analytical data set for the groundwater samples collected from the monitoring wells subsequent to soil removal and dewatering activities was also considered and used to support the PSS. Data Usability JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 13 OF 14 IRAC-PSS,RTN 4-28801 Based on the Representativeness Evaluation,the critical analytical data has been reviewed and validated. The analytical data provided in support of this PSS has met the method quality control requirements and performance standards for "Presumptive Certainty" as described in CAM VII A, Section 2.0(a), (b), (c), and(d)or have been evaluated as comparable to CAM requirements as usable and representative of potential exposure risks. Relative to soil assessment ahead of soil removal, analyses met REDUA for assessment and waste characterization as not critical samples. Deficiencies or other relative to the end-point soil sampling, the following was noted: For the endpoint soil May samples collected on Lab#L2128325 the CAM narrative p Y 26,2021 ( reported an affirmative response for Questions A through G, with negative responses for Questions H and I. The negative response for Question H was issued for the contaminated stockpile sample, which is non-critical data. The negative response for Question I was issued wherein the limited 4 PAH list was requested during EPH analysis. These target analytes were appropriate for a virgin fuel oil release at a residential property with no commercial or industrial history. As such these results meet presumptive certainty for use as critical data. For the groundwater samples collected on June 4, 2021 (Lab#L2130129)the CAM narrative reported affirmative responses for all Questions. As such, these results meet presumptive certainty for use as critical data. The validity and defensibility of the analytical data used to support the findings of the PSS for this Site with respect to accuracy, precision, and completeness pursuant to 310 CMR 40.1056(2)(k) have therefore been satisfied. It has been determined that the Site data is sufficiently representative of actual Site conditions and may be used to support this PSS. BACKGROUND FEASIBILITY EVALUATION A review of cost and feasibility to meet background conditions through additional soil removal was considered as part of this IRA, in accordance with the provisions of 310 CMR 40.1020. Fractional EPH and VPH compounds and target analytes were reported as non-Detect, or at low level concentrations significantly below the most restrictive Method 1 —Risk Characterization standards in all discrete locations sampled. This data demonstrates a condition of No Significant Risk with respect to soils at the Site. As such, current environmental conditions associated with residual low-level petroleum concentrations in soil as non-persistent, naturally degrading compounds meet the "Conditions of Categorical Infeasibility" established in Section 9.3.2 of the MA DEP policy "Conducting Feasibility Evaluations Under the MCP" (WSC-04-160), as specifically pertaining to Section 9.3.2.3, "Remediation of Degradable (Non-persistent) Contaminants". CONCLUSIONS/LIMITATIONS Immediate Response Actions were initiated at the Site, upon discovery of a release of home heating oil at the subject property. Assessment activities included soil sampling and laboratory analysis to define the extent and magnitude of significant petroleum impact. Remedial response actions consisted of soil removal from an approximate 16' x 16' area from 4' to 8' below grade using r JULY 20,2021 EVANS-125 HARBOR BLUFFS RD.HYANNIS/K11381 PAGE 14 OF 14 IRAC-PSS,RTN 4-28801 dewatering to facilitate excavation below the groundwater interface.A total of 74.92 tons (f50 cubic yards) of petroleum-contaminated soils, and 307 gallons of impacted water, were transported off-site to approved facilities as remedial waste. Post-remediation soil and groundwater samples, collected from representative locations, qualify remedial performance. These laboratory results report all concentrations of EPH/PAHs and VPH/BTEX as non-Detect or below the applicable, and most stringent Method 1 Risk Characterization standards, documenting No Significant Risk and meeting regulatory closure objectives. As such, the response actions conducted and confirmatory laboratory data, supports a Permanent Solution Statement(PSS)Without Conditions for project closure,per 310 CMR 40.1041(1). Environmental investigations are inherently limited because conclusions are drawn and g Y recommendations developed, based on information from limited research and Site investigation to target a known release of fuel oil. This report does not warrant against future changes in regulations or policies, nor does this warrant operations or conditions present of a type or at a location not investigated [Refer to MCP Limitations—Appendix F]. The findings of this investigation, as represented herein, set forth the rationale and technical justification for the LSP Opinions offered, as established by the certifications made on the attached BWSC-104 and BWSC-105 Transmittal Forms. The LSP Opinions are based on available data and regulations in effect at the time of this reporting specific to the subject Site. Should the Department have any questions regarding this project, please contact our office at your earliest convenience. Sincerely, BENNETT ENVIRONMENTAL ASSOCIATES, LLC avid�. en%e , LPG, CGWP,LSP Jo D. T e a-Wi dt, P of Record cand Technical Consultant Mtnager of Environmen al Services Encl. Supporting Documentation [Appendices A-G] Cc: Doug and Betsy Evans—Property Owners Cosmo Gallinaro—Insurer's Representative Thomas McKean, Director—Barnstable Health Divisions Mark S. Ells—Barnstable Town Managers Peter J. Burke, Jr., Chief—Hyannis Fire Departments Darcy Karle, Administrator—Barnstable Conservation Departments ' As part of Public Notice requirements, the report Title Page, Narrative, Index, Transmittal forms and Site Plan are included,pursuant to paperwork reduction policy. The full report is available as public record on the MA DEP website database at bttp://public.deR,state.ma.us/SearcbableSites2/Search.aspx or, upon written request to BEA, full copy (electronic or paper)will be provided. I - - IMMEDIATE RESPONSE ACTION COMPLETION REPORT WITH PERMANENT SOLUTION STATEMENT AND SUPPORTING DOCUMENTATION RTN 4-28801 Evans Residential Property 125 Harbor Bluffs Road [Map 325, Parcel 120] Hyannis, MA 02601 Job#K11381 JULY 20, 2021 Prepared For: MA DEPARTMENT OF ENVIRONMENTAL PROTECTION Southeast Regional Offices: Bureau of Waste Site Cleanup/Emergency Response Section 20 Riverside Drive-Lakeville,MA 02347-Andy Jones,Case Officer Prepared By; BENNETT ENVIRONMENTAL ASSOCIATES,LLC A Natural Systems Utilities Company 1573 Main Street-Brewster,MA 02631 -John Tadema-Wielandt,LSP On Behalf Of: Doug and Betsy Evans, Homeowners 90 Harbor Bluffs Road-Hyannis,MA 02631 APPENDIX A: Reference Plans -Figure 1: Site Locus Plan[USGS Topographic Quad.,Hyannis,MA. 1998] (excerpt) -Figure 2: Ground-Water Resources of the Cape Cod,MA... [LeBlanc et al, 1986] (Excerpt) -Figure 3: MA DEP BWSC GIS Map [2021] -Site Plan entitled,"Immediate Response Action Completion with Permanent Solution Statement..."Prepared by BENNETT ENVIRONMENTAL ASSOCIATES,LLC,Dated June 25,2021 APPENDIX B: Field Reports -Mass Balance Fuel Loss Computations -Field Log [May 18,2021 to July 7,2021] -Borehole Logs [June 4,2021] -Monitoring Well Sampling Logs [6/4/21,6/23/21 and 6/24/211 -Sieve Analysis Data and Computation Sheet -Solute Transport-Time of Travel Computations APPENDIX C: Environmental Records/Permits/Correspondence -BWSC-101:Release Log Form [May 21,2021] -Notice of Responsibility [May 25,2021] -Hyannis FD Research -Uniform Hazardous Waste Manifest[#006280994GBF(307 gallons MA98)] -BWSC-I12:Bill of Lading to Transport Waste to Receiving Facility -BWSC-112: Bill of Lading Attestation of Completion of Shipment to Receiving Facility . -BWSC-103:Release Notification w/eDEP Submittal Summary and Receipt -BWSC-104:Permanent Solution Statement w/eDEP Submittal Summary and Receipt -BWSC-105:Immediate Response Action Transmittal Form w/eDEP Submittal Summary and Receipt APPENDIX D: Laboratory Analysis sis -Soil Assessment[Alpha Analytical—Lab#(1,2126393 (5/20/21)]with data summary table -Standing Water Assessment[Alpha Analytical—Lab# L2126733 (5/25/21)]with.data summary table -Soil Endpoints/Disposal Characterizations [Alpha Analytical—Lab# L2128325 (6/13/21)] with data summary table -Groundwater Monitoring Wells [Alpha Analytical—Lab#L2130129(6/17/21)] with data summary table -Data Usability Summary Table APPENDIX E: Quality Assurance/Quality Control Plan APPENDIX F: MCP Limitations Statement Massachusetts Department of Environmental Protection BWSC 101 LL Bureau of Waste Site Cleanup Release Tracking Number RELEASE LOG FORM 4~ - 28801 A.THIS FORM IS BEING USED TO: (check one) 1.Log Date: 5/21/2021 Log Time: 12:10 r AM r PM (mm/dd/yyyy) (hh:mm) N-0 2.Assign a Release Tracking Number(RTN)to a Release or TOR Report. a.Reportable Release or TOR. r b.Release that is Less Than the Reporting Thresholds. r 3.Amend a Previously Recorded Release or TOR Report(RTN Assigned). r a.The Release is a Reportable Release or TOR. r b.The Release is a Release that is Less Than the Reporting Thresholds. r c.The Release or TOR is Retracted. I-d.The Release or TOR is not a Release under M.G.L.c.21E. (BWSC103 must be submitted,as well) B.REPORTING PERSON: 1.Name of Organization: BENNETT ENVIRONMENTAL ADVISORS 2.First Name: DAVID 3.Last Name: BENNE FF 4.Telephone: 5087377350 5.Ext.: 6.Relationship of Person to Release: r PRP Wii Other c.Type,if known(e.g. Current Owner): Consultant for PRP Not an C.RELEASE OR THREAT OF RELEASE(TOR)/SITE LOCATION: 1.Location Aid/Site Name: FUEL OIL RELEASE 2. Street Address: 125 HARBOR BLUFF RD 3.2nd Address Line: 4.City/Town: HYANNIS,BARNSTABLE 5.Zip Code(if known): 6.Type of Location:(check all that apply) r a. School r b.Water Body r c.Right of Way r d.Utility Easement r e.Roadway r f.Municipal r g. State r'h.Residential r i.Open Space r j.Private Property r k.Industrial r 1.Commercial (r m.Federal r n.Other Describe: D.RELEASE OR TOR INFORMATION: 1.Date and Time of Notification: 5/21/2021 Time: 12:10 r AM .PM (mm/dd/yyyy) (hh:mm) 2.Date and Time Reporting Person obtained 5/21/2021 Time: 12:10 r AM r PM Knowledge of Release or TOR: (mm/dd/YYYY) (hh:mm) 3.Date and Time Release or TOR Time: r`AM r PM occurred,if known: (nun/dd/ YYYY) (hh:mm) 4. Sources of the Release or TOR:(check all that apply) r a.Transformer r b.Fuel Tank r c.Pipe r d.OHM Delivery W e.AST r f. Drums r g.Tanker Truck r h.Hose r i.Line r j.UST Describe r k.Vehicle r 1.Boat/Vessel r m.Unknown r n.Other: 5.Federal LUST Eligible: r Yes W No r Unknown Revised: 01/07/2014 Page 1 of 5 Massachusetts Department of Environmental Protection BWSC 101 Bureau of Waste Site Cleanup RELEASE LOG FORM Release Tracking Number F4^! - 28801 -- Check all Notification Thresholds that apply to the Release or TOR: 6.2 Hour Reporting Conditions: 7.72 Hour Reporting Conditions: 8.120 Day Reporting Conditions: r a.Sudden Release r a. Subsurface Non-Aqueous r a.Release of Hazardous Material(s) r b.Threat of Sudden Release Phase Liquid(NAPL)Equal to Soil or Groundwater Exceeding •c.Oil Sheen on Surface Water to or Greater than 1/2 Inch Reportable Concentration(s) •d.Poses Imminent Hazard r b.Underground Storage Tank r b.Release of Oil to Soil Exceeding •e.Could Pose Imminent Hazard (UST)Release Reportable Concentration(s)and r f.Release Detected r c.Threat of UST Release Affecting More than 2 Cubic in Private Well r d.Release to Groundwater Yards r-g.Release to Storm Drain near Water Supply r-c.Release of Oil to Groundwater r h.Sanitary Sewer Release r e.Release to Groundwater Exceeding Reportable (Imminent Hazard Only) near School or Residence Concentration(s) f.Substantial Release Migration r'd. Subsurface Non-Aqueous Phase Liquid(NAPL)Equal to or Greater than 1/8 Inch and Less than 1/2 Inch 9.Type of Release or TOR:(check all that apply) r a.Dumping r b.Fire r c.AST Removal r d.Overfill r e.rupture r f.Vehicle Accident Po'g.Leak r h.Spill r i.Test Failure r j.TOR Only r k.UST Removal Describe V 1.Unknown r m.Other: 10.Media Impacted and Receptors Affected: (check all that apply) r a.Paved Surface r,b.Basement r c. School r d.Public Water Supply r-e.Surface Water r-f.Zone 2 r g.Private Well r-h.Residence r i.Soil r-j.Ground Water r k.Sediments r I.Wetland r m. Storm Drain r n.Indoor Air r o.Air r p.Soil Gas r q.Sub-Slab Soil Gas r r.Critical Exposure Pathway r s.NAPL r t.Unknown r u. Others Specify: 11.List below the Oils(0)or Hazardous Materials(HM)that exceed their Reportable Concentration(RC)or Reportable Quantity(RQ)by the greatest amount. r Check here if an amount or concentration is unknown or less than detectable. O or HM Released CAS Number, O or HM Amount or Units RCs Exceeded,if Applicable if known Concentration #2 FUEL OIL O 40 GAL N/A N/A N/A Revised:01/07/2014 Page 2 of 5 Massachusetts Department of Environmental Protection BWSC 101 Bureau of Waste Site Cleanup RELEASE LOG FORM Release Tracking Number 28801 4 -- _ -__---- 4 1 -- 12.Description of Release or Threat of Release(if additional space is needed,attach additional information in H17) D.BENNETT REPORTING A HISTORIC RELEASE THAT IS SUSPECTED OF BEING A SUDDEN RELEASE. BASED ON ASSESSMENTS,IT IS ESTIMATED THAT A HISTORICAL SUDDEN RELEASE OF APPROXIMATELY 40 GALLONS HAD OCCURRED FROM A SUSPECTED ABOVE GROUND STORAGE TANK IT IS UNKNOWN WHEN RELEASE OCCURRED BUT IS LIKLEY IT OCCURRED DURING PRIOR SITE OWNERSHIP. SITE IS CURRENTLY UNDERGOING DEMOLITION/CONSTRUCTION. E.INVOLVED PARTIES SUMMARY: 1.PRP Status(check one): r a.PRP Unknown r b.PRP unwilling,unable or has not committed to Perform Response Actions W c.PRP Performing Response Actions r d.Release is Adequated Regulated by the US Coast Guard 2.If PRP is not Performing Response Actions,who is? r a.MassDEP State Contractor r b. Other Person 3.Contractor: a.Name of Organization: b.Telephone: c.Contact First Name: d.Last Name: 4.LSP: a.Name: TADEMA WIELANDTJOHN b.LSP#: 1707 c.Telephone: 5085350487 Revised:01/07/2014 Page 3 of 5 Massachusetts Department of Environmental Protection BWSC 101 Bureau of Waste Site Cleanup Release Tracking Number RELEASE LOG FORM 14 - 128801 T�I F.PRP OR PERSON PERFORMING RESPONSE ACTIONS: 1.Name of Organization: 2.Contact First Name: DOUG AND BETSY 3.Last Name: EVANS 4.Street: 90 HARBOR BLUFF RD 5.Title: 6.City/Town: HYANNIS 7.State: MA 8.ZIP Code: 026010000 9.Telephone: 7134441663 10.Ext: 11.Email: 12.Relationship of Person to Release: r7 PRP r-Other c.Type(e.g.Curreht Owner): Current Owner r 13.Check here if this PRP received a field NOR r 14.Check here if an RNF was requested from this PRP r 15.Check here if Provisions of 21E were explained to this PRP. G.RECORD ORAL RESPONSE ACTIVITIES: r 1.IRA Completed Pre-notification F'5.IRA Oral Modified Plan Approved r 2.No IRA Approved at Notification r 6.IRA Oral Plan Denied and/or Request for Written Plan Ir-3.IRA Assessment Only. r 7.Notice of Intent to Conduct a URAM W 4.IRA Oral Plan Approved r 8 IRA-D Oral Plan Approved lr-"9.IRA-D Oversight Work Started 10.Date of Action: 5/21/2021 11.Soil Previously Excavated: r:a.Excavated prior to notification. r b.Excavated as part of an UST closure. c.Quantity of contaminated soil previously excavated and destination,if applicable: 12. Specify any Regional Specific Code(Regional Use): H.ORAL RESPONSE ACTION PLAN: (check all that apply) r 1.Assessment and/or Monitoring Only r-2.Temporary Covers or Caps r 3.Deployment of Absorbent or Containment Materials r 4.Temporary Water Supplies r 5. Structure Venting System r,6.Temporary Evacuation or Relocation of Residents 1-7.Product or NAPL Recovery r 8.Fencing and Sign Posting r 9. Groundwater Treatment Systems r 10.Soil Vapor Extraction r 11.Bioremediation r 12.Air Sparging r 13.Excavation of Contaminated Soils F%_1 a.Re-use,Recycling or Treatment 1-.i.On Site ii.Off Site Authorized volume in cubic yards: 75 r.b. Store 17 i.On Site N-ii.Off Site Authorized volume in cubic yards: r c.Landfill i.Cover ,ii.Disposal Authorized volume in cubic yards: Revised:01/07/2014 Page 4 of 5 Massachusetts Department of Environmental Protection BWSC 101 L Bureau of Waste Site Cleanup Release Tracking Number RELEASE LOG FORM ,� (4 - F28801 ---__� r 14.Removal of Drums,Tanks or Containers: Describe Quantity and Amount: r 15.Removal of Other Contaminated Media: Specify Type and Volume: r 16 Other Response Actions and Additional Comments(describe): RECOVERY AND DISPOSAL OF UP TO 3000 GALS OF CONTAMINATED GROUNDWATER. r 17.Check here if Additional Infonnation is Provided in an Attachment I.DEP STAFF AND FORM PREPARER: 1.DEP Staff: a.Name: JONES ANDY r b.Check here,if Unassigned(or staff name not applicable). 2 .Preparer: a.Name: JONES ANDY b.Signature: ANDREW L.JONES c.Date: 5/21/2021 Revised:01/07/2014 Page 5 of 5 i Massachusetts Department of Environmental Protection BWSC 103 v Bureau of Waste Site Cleanup f` } Release Tracking Number ,a RELEASE NOTIFICATION&NOTIFICATION d, RETRACTION FORM �4 - 28801 Pursuant to 310 CMR 40.0335 and 310 CMR 40.0371 (Subpart C) A.RELEASE OR THREAT OF RELEASE LOCATION: 1.Release Name/Location Aid: FUEL OIL RELEASE 2. Street Address: 125 HARBOR BLUFS RD 3.City/Town: HYANNIS 4.ZIP Code:. 026010000 1 5.Coordinates: a.Latiarde:N 41.64355 b.Longitude:W 70.27636 B.THIS FORM IS BEING USED TO: (check one) 1.Submit a Release Notification 2.Submit a Revised Release Notification 3.Submit a Retraction of a Previously Reported Notification of a release or threat of release including supporting documentation required pursuant to 310 CMR 40.0335(Section C is not required) (All sections of this transmittal form must be filled out unless otherwise noted above) C.INFORMATION DESCRIBING THE RELEASE OR THREAT OF RELEASE (TOR): 1.Date and time of Oral Notification,if applicable: 5/21/2021 Time: 12:10 r—AM W PM mm/dd/yyyy hh:mm 2.Date and time you obtained knowledge of the Release or TOR: 5/21/2021 Time: 11:00 W AM r-PM mm/dd/yyyy hh:mm 3.Date and time release or TOR occurred,if known: Time: r AM I PM mm/dd/yyyy hh:mm Check all Notification Threshold3 that apply to the Release or Threat of Release: (for more information see 310 CMR 40.0310-40.0315) 4.2 HOUR REPORTING CONDITIONS 5.72 HOUR REPORTING CONDITIONS 6.120 DAY REPORTING CONDITIONS rV a.Sudden Release r a. Subsurface Non-Aqueous Phase r a.Release of Hazardous Material(s)to Liquid(NAPL)Equal to or Greater than Soil or Groundwater Exceeding 1/2 Inch(.04 feet) Reportable Concentration(s) b.Threat of Sudden Release J b.Underground Storage Tank(UST) b.Release of Oil to Soil Exceeding Release Reportable Concentration(s)and Affecting More than 2 Cubic Yards r c.Oil Sheen on Surface Water r c.Threat of UST Release c.Release of Oil to Groundwater Exceeding Reportable Concentration(s) r d.Poses Imminent Hazard J= d.Release to Groundwater near Water r d. Subsurface Non-Aqueous Phase Supply Liquid(NAPL)Equal to or Greater than 1/8 Inch(.01 feet)and Less than 1/2 Inch (.04 feet) e.Could Pose Imminent Hazard e.Substantial Release Migration r £Release Detected in Private Well r g.Release to Storm Drain h.Sanitary Sewer Release (Imminent Hazard Only) Revised: 07/18/2013 Pagel of 3 I` Massachusetts Department of Environmental Protection BWSC 103 7L,)J�— RELEASE Bureau of Waste Site Cleanup NOTIFICATION&NOTIFICATION Release Tracking Number RETRACTION FORM 4 - 28801 Pursuant to 310 CMR 40.0335 and 310 CMR 40.0371 (Subpart C) C.INFORMATION DESCRIBING THE RELEASE OR THREAT OF RELEASE (TOR): (cont.) 7.List below the Oils(0)or Hazardous Materials(HIV)that exceed their Reportable Concentration(RC)or Reportable Quantity(RQ)by the greatest amount. Check here if an amount or concentration is unknown or less than detectable. O or HM Released CAS Number, O or HM Amount or Units RCs Exceeded,if Applicable if known Concentration (RCS-1,RCS-2,RCGW-1, RCGW-2) 42 FUEL OIL O 40 GAL RGS-1 Check here if a list of additional Oil and Hazardous Materials subject to reporting,or any other documentation relating to this notification is attached. D.PERSON REQUIRED TO NOTIFY: 1.Check all that apply: r a.change in contact name b.change of address V c.change in the person notifying 2.Name of Organization: 3.Contact First Name: ELIZABETH 4.Last Name: EVANS 5.Street: 90 HARBOR BLUFFS ROAD 6.Title: PROPERTYOWNER 7.City/Town: HYANNIS 8.State: MA 9.ZIP Code: 026010000 10.Telephone: 713-444-1663 11.Ext.: 12.Email: bets.evans@gmail.com r 13.Check here if attaching names and addresses of owners of properties affected by the Release or Threat of Release,other than an owner who is submitting this Release Notification(required). E.RELATIONSHIP OF PERSON TO RELEASE OR THREAT OF RELEASE: r—Check here to change relationship 17 1.RP or PRP rv-a.Owner I—b.Operator r—c.Generator d.Transporter r—e.Other RP or PRP Specify: r—2.Fiduciary,Secured Lender or Municipality with Exempt Status(as defined by M.G.L.c.21E,s.2) 3.Agency or Public Utility on a Right of Way(as defined by M.G.L.c.21E,s.56)) r 4.Any Other Person Otherwise Required to Notify Specify Relationship: Revised: 07/18/2013 Page 2 of 3 f Massachusetts Department of Environmental Protection BWSC 103 Bureau of Waste Site Cleanup RELEASE NOTIFICATION&NOTIFICATION Release Tracking Number RETRACTION FORM 4� 28801 Pursuant to 310 CMR 40.0335 and 310 CMR 40.0371 (Subpart C) F.CERTIFICATION OF PERSON REQUIRED TO NOTIFY: 1.I, ELIZABETH EVANS ,attest under the pains and penalties of perjury(i)that I have personally examined and am familiar with the information contained in this submittal,including any and all documents accompanying this transmittal form,(ii)that,based on my inquiry of those individuals immediately responsible for obtaining the information,the material information contained in this submittal is,to the best of my knowledge and belief,true,accurate and complete,and(iii)that I am fully authorized to make this attestation on behalf of the entity legally responsible for this submittal.I/the person or entity on whose behalf this submittal is made am/is aware that there are significant penalties,including,but not limited to,possible fines and imprisonment,for willfully submitting false, inaccurate,or incomplete information. 2.By ELIZABETH EVANS 3.Title: PROPERTY OWNER Signature 4.For: ELIZABETH EVANS 5.Date: 7/20/2021 (Name of person or entity recorded in Section D) mm/dd/yyyy r 6.Check here if the address of the person providing certification is different from address recorded in Section D. 7.Street: 8.City/Town: 9.State: 10.ZIP Code: 11.Telephone: 12.Ext: 13.Email: YOU ARE SUBJECT TO ANNUAL COMPLIANCE ASSURANCE FEES FOR EACH BILLABLE YEAR FOR TIER CLASSIFIED DISPOSAL SITES.YOU MUST LEGIBLY COMPLETE ALL RELEVANT SECTIONS OF THIS FORM OR DEP MAY RETURN THE DOCUMENT AS INCOMPLETE.IF YOU SUBMIT AN INCOMPLETE FORM,YOU MAYBE PENALIZED FOR MISSING A REQUIRED DEADLINE. Date Stamp(DEP USE ONLY:) Received by DEP on 7/20/20219:52:59 AM Revised: 07/18/2013 Page 3 of 3 Massachusetts Department of Environmental Protection BWSC 104 12 Bureau of Waste Site Cleanup umber N PERMANENT AND TEMPORARY SOLUTION STATEMENT 4 -Release Tracking king 'yPursuant to 310 CMR 40.1000(Subpart J) For sites with multiple RTNs,enter the Primary RTN above. A.SITE LOCATION: 1.Site Name/Location Aid: FUEL OIL RELEASE 2. Street Address: 125 HARBOR BLUFS RD 3.City/Town: HYANNIS 4.ZIP Code: 026010000 5.Coordinates: a.Latitude:N 41.64355 b.Longitude:W 70.27636 6.Check here if the disposal site that is the source of the release is Tier Classified.Check the current Tier Classification Category: F a.Tier I F b.Tier ID F c.Tier H B.THIS FORM IS BEING USED TO:(check all that apply) 1.List Submittal Date of the Permanent or Temporary Solution Statement, or RAO Statement(if previously submitted): mm/dd/yyyy r7 2.Submit a Permanent or Temporary Solution Statement C" a.Check here if this Permanent or Temporary Solution Statement covers additional Release Tracking Numbers (RTNs).RTNs that have been previously linked to a Tier Classified Primary RTN do not need to be listed here. b.Provide the additional Release Tracking Number(s)covered by this - 0_1 -l�J Permanent or Temporary Solution Statement. 1:1 r- 3.Submit a Revised Permanent or Temporary Solution Statement(or revised RAO Statement) 7 a.Check here if this Revised Permanent or Temporary Solution Statement covers additional Release Tracking Numbers(RTNs), not listed on the Permanent or Temporary Solution Statement or previously submitted Revised Permanent or Temporary Solution Statements.RTNs that have been previously linked to a Tier Classified Primary RTN do not need to be listed here. b.Provide the additional Release Tracking Number(s)covered by this - El - Permanent or Temporary Solution Statement. 4.Submit a Permanent or Temporary Solution Partial Statement Check above box,if any Response Actions remain to be taken to address conditions associated with this disposal site having the Primary RTN listed in the header section of this transmittal form.This Permanent or Temporary Solution Statement will record only a Permanent or Temporary Solution-Partial Statement for that RTN.A final Permanent or Temporary Solution Statement will need to be submitted that references all Permanent or Temporary Solution-Partial Statements and,if applicable,covers any remaining conditions not covered by the Permanent or Temporary Solution-Partial Statements. Also,specify if you are an Eligible Person or Tenant pursuant to M.G.L.c.21 s.2,and have no further obligation to conduct response actions on the remaining portion(s)of the disposal site: r- a.Eligible Person r- b.Eligible Tenant 5.Submit a Revised Permanent or Temporary Solution Partial Statement(or revised RAO-Partial Statement) F- 6.Submit an optional Phase I Completion Statement supporting the Permanent or Temporary Solution Statement 7.Submit a Periodic Review Opinion evaluating the status of a Temporary Solution,as specified in 310 CMR 40.1051 (Section F is optional) r 8.Submit a Retraction of a previously submitted Permanent or Temporary Solution Statement(or RAO Statement) (Sections E&F are not required) (All sections of this transmittal form must be filled out unless otherwise noted above) Revised: 6/21/2016 Page 1 of 8 assachusetts Department of Environmental Protection BWSC 104 12 ureau of Waste Site Cleanup ERMANENT AND TEMPORARY SOLUTION STATEMENT Release Tracking Number i k�M1ti _ ursuant to 310 CMR 40.1000(Subpart J) 4 K] - 28801 i For sites with multiple RTNs,enter the Primary RTN above. C.DESCRIPTION OF RESPONSE ACTIONS:(check all that apply;for volumes,list cumulative amounts) r—1.Assessment and/or Monitoring Only F 2.Temporary Covers or Caps r 3.Deployment of Absorbent or Containment Materials r 4.Treatment of Water Supplies r—5.Structure Venting System/HVAC Modification System r—6.Engineered Barrier r 7.Product or NAPL Recovery r 8.Fencing and Sign Posting F 9.Groundwater Treatment Systems 10.Soil Vapor Extraction F 11.Remedial Additives 12.Air Sparging r 13.Active Exposure Pathway Mitigation System 14.Passive Exposure Pathway Mitigation System 1-15.Monitored Natural Attenuation F 16.In-Situ Chemical Oxidation r*_1 17.Removal of Contaminated Soils a.Re-use,Recycling or Treatment r i.On Site Estimated volume in cubic yards r ii.Off Site Estimated volume in cubic yards iia.Facility Name: Town: State: iib.Facility Name: Town: State: iii.Describe: rV b.Landfill ry-1 i.Cover Estimated volume in cubic yards 50 Facility Name: BOURNE ISWM FACILITY Town: BOURNE State: MA r ii.Disposal Estimated volume in cubic yards Facility Name: Town: State: F 18.Removal of Drums,Tanks or Containers: a.Describe Quantity and Amount: b.Facility Name: Town: State: c.Facility Name: Town: State: rv—19.Removal of Other Contaminated Media: a.Specify Type and Volume: DEWATERING AND REMOVAL OF 307 GALLONS OF IMPACTED WATER FROM EXCAVATION b.Facility Name: TRADEBE TREATMENT AND RECYCLING Town: STOUGHTON State: MA c.Facility Name: Town: State: Revised: 6/21/2016 Page 2 of 8 assachusetts Department of Environmental Protection BWSC 104 12 ureau of Waste Site Cleanup Release Tracking Number L ERMANENT AND TEMPORARY SOLUTION STATEMENTuisuant to 310 CMR 40.1000(Subpart J) ) For sites with multiple RTNs,enter the Primary RTN above. C.DESCRIPTION OF RESPONSE ACTIONS (cont.):(check all that apply;for volumes,list cumulative amounts) r-20.Other Response Actions: Describe: F 21.Use of Innovative Technologies: Describe: D.SITE USE: 1.Are the response actions that are the subject of this submittal associated with the redevelopment,reuse or the major expansion of the current use of property(ies)impacted by the presence of oil and/or hazardous materials? F a.Yes W b.No F c.Don't know. 2.Is the property a vacant or under-utilized commercial or industrial property("a brownfield property")? a.Yes W b.No c.Don't know 3.Will funds from a state or federal brownfield incentive program be used on one or more of the property(ies)within the disposal site? r a.Yes rV b.No r c.Don't know If Yes,identify program(s): 4.Has a Covenant Not to Sue been obtained or sought? r a.Yes P_b.No r c.Don't know 5.Check all applicable categories that apply to the person making this submittal: I—a.Redevelopment Agency or Authority F b.Community Development Corporation r-c.Economic Development and Industrial Corporation F d.Private Developer r-e.Fiduciary r f Secured Lender r g.Municipality F h.Potential Buyer(non-owner) T%F i.Other,describe: PROPERLY OWNER This data will be used by MassDEP for information purposes only,and does not represent or create any legal commitment,obligation or liability on the part of the party or person providing this data to MassDEP. E.PERMANENT OR TEMPORARY SOLUTION CATEGORY: . Specify the category of Solution that applies to the Disposal Site,or Site of the Threat of Release. Select either 1,2,or 3. rV 1.Permanent Solution with No Conditions(check one) r a.A threat of release has been eliminated. r` b.All contamination has been reduced to Natural Background levels. r c.A condition of No Significant Risk exists or has been achieved with no Activity and Use Limitation or other limitations, assumptions,or conditions(310 CMR 40.1013). Revised: 6/21/2016 Page 3 of 8 assachusetts Department of Environmental Protection BWSC 104 12 ureau of Waste Site Cleanup RMANENT AND TEMPORARY SO LUTION STATEMENT Release Tracking Number rsuan'to 310 CMR 40.1000(Subpart J) L7 28801 For sites with multiple RTNs,enter the Primary RTN above. E.PERMANENT OR TEMPORARY SOLUTION CATEGORY(coot.): r" 2.Permanent Solution with Conditions(check a and/or b): a.An AUL has been implemented pursuant to 310 CMR 1012(2)(check one) r i.Required pursuant to 310 CMR 40.1012(2) Is the AUL required because the Permanent Solution relies on an Active Exposure Pathway Mitigation Measure pursuant to CMR 310 40.1025? r i.yes r® 2.No r ii.Optionally implemented pursuant to 310 CMR 40.1012(3) b.Limitations or conditions apply pursuant to 310 CMR 40.1013(check all that apply): r i.Gardening Best Management Practices(BMPs)for non-commercial gardening in a residential setting r ii.Concentrations of Oil and Hazardous Material consistent with Anthropogenic Background r- iii.Residual contamination in a Public or Railroad Right-of-Way r iv.Groundwater contamination would exceed GW-2 Standards except for the absence of an occupied building or structure r 3.Temporary Solution(check a or b/and c) r a.Response actions to achieve a Permanent Solution are not currently feasible r— b.Response actions to achieve a Permanent Solution are feasible and are being continued toward a Permanent Solution r`° c.Does the Temporary Solution rely on an Active Exposure Pathway Mitigation Measure pursuant to 310 CMR 40.1026? r i.Yes r ii.No F.PERMANENT AND TEMPORARY SOLUTION INFORMATION: 1.Specify the Risk Characterization Method(s)used to achieve the Permanent or Temporary Solution,described above: V a.Method 1 r' b.Method 2 r c.Method 3 r9 d.Method Not Applicable-Contamination reduced to or consistent with background,or Threat of Release abated 2.Specify all Soil Category(ies)applicable.More than one Soil Category may apply at a Site.Be sure to check off all APPLICABLE categories: a.S-1/GW-I r d.S-2/GW-1 ry g.S-3/GW-1 I— j.Not Applicable r b.S-1/GW-2 W� e.S-2/GW-2 r h.S-3/GW-2 r c.S-1/GW-3 r f.S-2/GW-3 r i.S-3/GW-3 3.Specify all Groundwater Category(ies)impacted.A site may impact more than one Groundwater Category.Be sure to check off all BIPACTED categories: r a.GW-1 r b.GW-2 r c.GW-3 r d.No Groundwater Impacted Revised: 6/21/2016 Page 4 of 8 f assachusetts Department of Environmental Protection BWSC 104 12 ureau of Waste Site Cleanup r ERMANENT AND TEMPORARY SOLUTION STATEMENT Release Tracking Number ursuant to 310 CMR 40.1000(Subpart J) 28801 4 For sites with multiple RTNs,enter the Primary RTN above. F.PERMANENT AND TEMPORARY SOLUTION INFORMATION(cont.): r 4.Check here if the risk assessment includes any changes to the groundwater category pursuant to 310 CMR 40.0932(5)(a)through(e).Check all conditions that apply: r° a.An InterimWellhead Protection Area does not apply based on a hydrogeologic evaluation(310 CMR 40.0932(5)(a)) b.Groundwater was determined not to be in a Potentially Productive Aquifer or is not feasible to be developed as a drinking water supply(310 CMR 40.0932(5)(b)) c.A Non-Potential DrinkingWater Source Area determination was made(310 CMR 40.0932(5)(c)) r d.Existing private wells were permanently closed(310 CMR 40.0932(5)(d)) (� e.Groundwater is located within a Zone A,but is not hydrogeologically connected to a drinking water supply (310 CMR 40.0932(5)(e)) r 5.Check here if the Permanent or Temporary Solution supports a finding of No Significant Risk for petroleum in a GW-1 area pursuant to 310 CMR 40.0924(2)(b)3. 6.Specify whether remediation was conducted: a.Check here if soil remediation was conducted. r%�-. b.Check here if groundwater remediation was conducted. r c.Check here if other remediation was conducted. Specify: 7.Specify whether the analytical data used to support the Permanent or Temporary Solution used the Compendium of Analytical Methods(CAM): r a.CAM used to support all analytical data. r b.CAM used to support some of the analytical data. r c.CAM not used. r 8.Check here to indicate that the Permanent or Temporary Solution Statement includes a Data Usability Assessment and Data Representativeness Evaluation pursuant to 310 CMR 40.1056. 9.Estimate the number of acres this Permanent or Temporary Solution Statement applies to: 0.01 Revised: 6/21/2016 Page 5 of 8 assachusetts Department of Environmental Protection BWSC 104 12 L7- ureau of Waste Site Cleanup Release Tracking Number ful RMANENT AND TEMPORARY SOLUTION STATEMENTrsuant to 310 CMR 40.1000(Subpart J) I ' I 28801 For sites with multiple RTNs,enter the Primary RTN above. G.LSP SIGNATURE AND STAMP: I attest under the pains and penalties of perjury that I have personally examined and am familiar with this transmittal form,including any and all documents accompanying this submittal.In my professional opinion and judgment based upon application of(i)the standard of care in 309 CMR 4.02(1),(ii)the applicable provisions of 309 CMR 4.02(2)and(3),and 309 CMR4.03(2),and(iii)the provisions of 309 CMR 4.03(3),to the best of my knowledge,information and belief, >if Section B indicates that either a Permanent or Temporary Solution Statement,Phase I Completion Statement and/or Periodic Review Opinion is being provided,the response action(s)that is(are)the subject of this submittal(i)has(have)been developed and implemented in accordance with the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000,(ii)is(are)appropriate and reasonable to accomplish the purposes of such response action(s)as set forth in the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000,and(iii)comply(ies)with the identified provisions of all orders,permits,and approvals identified in this submittal. I am aware that significant penalties may result,including,but not limited to,possible fines and imprisonment,if I submit information which I know to be false,inaccurate or materially incomplete. 1.LSP#: 1707 2.First Name: JOHN 3.Last Name: TADEMA-WIELANDT 4.Telephone: 5085350487 5.Ext.: 6.Email: itadema-wielandt@nsuwater.com 7.Signature: JOHN TADEMA-WIELANDT 8.Date: 7/20/2021 9.LSP Stamp: �� mm/dd/yyyy Seal H.PERSON MAKING SUBMITTAL: 1.Check all that apply: a.change in contact name rb.change of address r c.change in the person undertaking response actions 2.Name of Organization: 3.Contact First Name: ELIZABETH 4.Last Name: EVANS 5.Street: 90 HARBOR BLUFFS ROAD 6.Title: PROPERTYOWNER 7.City/Town: HYANNIS 8.State: MA 9.ZIP Code: 026010000 10.Telephone: 7134441663 11.Ext.: 12.Email: bets.evans@gmail.com Revised: 6/21/2016 Page 6 of 8 assachusetts Department of Environmental Protection BWSC 104 12 ureau of Waste Site Cleanup Release Tracking Number RMANENT AND TEMPORARY SOLUTION STATEMENT �LT rsuant to 310 CMR 40.1000(Subpart J) Ell 28801 For sites with multiple RTNs,enter the Primary RTN above. 1.RELATIONSHIP TO RELEASE OR THREAT OF RELEASE OF PERSON MAKING SUBMITTAL: r Check here to change relationship rv1-1.RP or PRP W a.Owner r-b.Operator r c.Generator r-d.Transporter r e.Other RP or PRP Specify: 2.Fiduciary,Secured Lender or Municipality with Exempt Status(as defined by M.G.L.c.21E,s.2) r 3.Agency or Public Utility on a Right of Way(as defined by M.G.L.c.21E,s.50)) 1' 4.Any Other Person Making Submittal Specify Relationship: J.REQUIRED ATTACHMENT AND SUBMITTALS: 1.Check here if the Pennanent or Temporary Solution on which this opinion is based,if any,are(were)subject to any order(s), permit(s)and/or approval(s) 'ssued by DEP or EPA.If the box is checked,you MUST attach a statement identifying the applicable provisions thereof. 2.Check here to certify that the Chief Municipal Officer and the Local Board of Health have been notified of the submittal of a Permanent or Temporary Solution Statement that relies on the public way/rail right-of-way exemption from the requirements of an AUL. 17 3.Check here to certify that the Chief Municipal Officer and the Local Board of Health have been notified of the submittal of a Permanent or Temporary Solution Statement with instructions on how to obtain a full copy of the report. r7o 4.Check here to certify that documentation is attached specifying the location of the Site,or the location and boundaries of the Disposal Site subject to this Permanent or Temporary Solution Statement.If submitting a Permanent or Temporary Solution Statement for a PORTION of a Disposal Site,you must document the location and boundaries for both the portion subject to this submittal and, to the extent defined,the entire Disposal Site. rV 5.Check here to certify that,pursuant to 310 CMR 40.1406,notice was provided to the owner(s)of each property within the disposal site boundaries,or notice was not required because the disposal site boundaries are limited to property owned by the party conducting response actions.(check all that apply) r- a.Notice was provided prior to,or concurrent with the submittal of a Phase II Completion Statement to the Department. r b.Notice was provided prior to,or concurrent with the submittal of this Permanent or Temporary Solution Statement to the Department. r c.Notice not required. d.Total number of property owners notified,if applicable: 6.Check here if you are submitting one or more AULs.You must submit an AUL Transmittal Form(BWSC113)and a copy of each implemented AUL related to this Permanent Solution or Temporary Solution Statement.Specify the type of AUL(s)below:(required for Permanent Solution with Conditions Statements where an AUL is being implemented) a.Notice of Activity and Use Limitation b.Number of Notices submitted: c.Grant of Environmental Restriction d.Number of Grants submitted: 7.If a Permanent Solution Compliance Fee is required for any of the RTNs listed on this transmittal form,check here to certify that a Permanent Solution Compliance Fee was submitted to DEP,P.0.Box 4062,Boston,MA 02211. 8.Check here if any non-updatable information provided on this form is incorrect,e.g.Site Address/Location Aid.Send corrections to bwsc.edep@state.ma.us. r 9.Check here to certify that the LSP Opinion containing the material facts,data,and other information is attached. Revised: 6/21/2016 Page 7 of 8 assachusetts Department of Environmental Protection BWSC 104 12 ureau of Waste Site Cleanup Release Tracking Number l ERMANENT AND TEMPORARY SOLUTION STATEMENT � ursuant to 310 CNIR 40.1000(Subpart J) KI 28801 For sites with multiple RTNs,enter the Primary RTN above. K.CERTIFICATION OF PERSON MAKING SUBMITTAL: 1.I,ELIZABETH EVANS ,attest under the pains and penalties of perjury(i)that I have personally examined and am familiar with the information contained in this submittal,including any and all documents accompanying this transmittal form,(ii)that,based on my inquiry of those individuals immediately responsible for obtaining the information,the material information contained in this submittal is,to the best of my knowledge and belief,true,accurate and complete,and(iii)that I am fully authorized to make this attestation on behalf of the entity legally responsible for this submittal.I/the person or entity on whose behalf this submittal is made am/is aware that there are significant penalties,including,but not limited to,possible fines and imprisonment,for willfully submitting false, inaccurate,or incomplete information. 2.By: ELIZABETH EVANS 3.Title: Signature 4.For: ELIZABETH EVANS 5.Date: 7/20/2021 (Name of person or entity recorded in Section H) mm/dd/yyyy 6.Check here if the address of the person providing certification is different from address recorded in Section H. 7.Street: 8.City/Town: 9.State: 10.ZIP Code: 11.Telephone: 12.Ext: 13.Email: YOU ARE SUBJECT TO AN ANNUAL COMPLIANCE ASSURANCE FEE OF UP TO$10,000 PER BILLABLE YEAR FOR THIS DISPOSAL SITE.YOU MUST LEGIBLY COMPLETE ALL RELEVANT SECTIONS OF TIUS FORM OR DEP MAY RETURN THE DOCUMENT AS INCOMPLETE.IF YOU SUBMIT AN INCOMPLETE FORM,YOU MAY BE PENALIZED FOR MISSING A REQUIRED DEADLINE. Date Stamp(DEP USE ONLY:) Received by DEP on 7/20/2021 10:23:19 AM Revised: 6/21/2016 Page 8 of 8 Massachusetts Department of Environmental Protection BWSC 105 Bureau of Waste Site Cleanup Release Tracking Number Immediate Response Action (IRA) Transmittal Form Pursuant to 310 CMR 40.0424-40.0427(Subpart D) 28801 A.SITE LOCATION: 1.Release Name/Location Aid: FUEL OIL RELEASE 2.Street Address: 125 HARBOR BLUFS RD 3.City/Town: HYANNIS 4.Zip Code: 026010000 5.Check here if this location is Adequately Regulated,pursuant to 310 CMR 40.0110-0114. r a.CERCLA r-b.HSWA Corrective Action r-c. Solid Waste Management d.RCRA State Program(21 C Facilities) B.THIS FORM IS BEING USED TO:(check all that apply) 1.List Submittal Date of Initial IRA Written Plan(if previously submitted): r 2.Submit an Initial IRA Plan. 3.Submit a Modified IRA Plan of a previously submitted written IRA Plan. r 4.Submit an Imminent Hazard Evaluation.(check one) r a.An Imminent Hazard exists in connection with this Release or Threat of Release. I—b.An Imminent Hazard does not exist in connection with this Release or Threat of Release. r-c.It is unknown whether an Imminent Hazard exists in connection with this Release or Threat of Release,and further assessment activities will be undertaken. r d.It is unknown whether an Imminent Hazard exists in connection with this Release or Threat of Release.However,response actions will address those conditions that could pose an Imminent Hazard. 5.Submit a request to Terminate an Active Remedial System or Response Action(s)Taken to Address an Imminent Hazard. r 6.Submit an IRA Status Report r 7.Submit a Remedial Monitoring Report.(This report can only be submitted through eDEP.) a.Type of Re check one YP Report:P ( ) r-i.Initial Report r u.Interim Report iii.Final Report b.Frequency of Submittal:(check all that apply) r-i.A Remedial Monitoring Report(s)submitted monthly to address an Imminent Hazard. r ii.A Remedial Monitoring Report(s)submitted monthly to address a Condition of Substantial Release Migration. iii.A Remedial Monitoring Report(s)submitted every six months,concurrent with an IRA Status Report. iv.A Remedial Monitoring Report(s)submitted annually,concurrent with an IRA Status Report. c.Number of Remedial Systems and/or Monitoring Programs: A separate BWSC105A,IRA Remedial Monitoring Report,must be filled out for each Remedial System and/or Monitoring Program addressed by this transmittal form. Revised: 11/14/2013 Page 1 of 6 Massachusetts Department of Environmental Protection BWSC 105 L Bureau of Waste Site Cleanup Release Tracking Number Immediate Response Action (IRA) Transmittal Form � Pursuant to 310 CNM 40.0424-40.0427(Subpart D) - 28801 r 8.Submit an IRA Completion Statement. r a.Check here if future response actions addressing this Release or Threat of Release notification condition will be conducted as part of the Response Actions planned or ongoing at a Site that has already been Tier Classified under a different Release Tracking Number (RTN) b.Provide Release Tracking Number of Tier Classified Site(Primary RTN): These additional response actions must occur according to the deadlines applicable to the Primary RTN.Use the Primary RTN when making all future submittals for the site unless specifically relating to this Immediate Response Action. r 9.Submit a Revised IRA Completion Statement. 10.Submit a Plan for the Application of Remedial Additives near a sensitive receptor,pursuant to 310 CMR 40.0046(3). (All sections of this transmittal form must be filled out unless otherwise noted above) C.RELEASE OR THREAT OF RELEASE CONDITIONS THAT WARRANT IRA: 1.Media Impacted and Receptors Affected:(check all that apply) r a.Paved Surface I-b.Basement r c.School r-d.Public Water Supply F e.Surface Water r-f Zone 2 r-g.Private Well r-h.Residence W i.Soil r j.Groundwater r k.Sediments r-1.Wetland r-in.Storm Drain r.n.Indoor Air r o.Air p.Soil Gas r q.Sub-Slab Soil Gas r r.Critical Exposure Pathway r s.NAPL r t.Unknown r.Others Specify: 2.Sources of the Release or TOR:(check all that apply) a.Transformer b.Fuel Tank c.Pipe r'd.OHM Delivery r%_0 e.AST f.Drums 1 g.Tanker Truck h.Hose i.Line r j.UST Describe: r k.Vehicle r.1.Boat/Vessel l—m.Unknown r-n. Other: 3.Type of Release or TOR:(check all that apply) r a.Dumping r b.Fire r c.AST Removal r d.Overfill r e.Rupture r-f.Vehicle Accident ry-O g.Leak r-h.Spill r i.Test failure j.TOR Only k.UST Removal Describe: 1.Unknown r-m. Other: 4.Identify Oils and Hazardous Materials Released:(check all that apply) ry-' a.Oils r b.Chlorinated Solvents r c.Heavy Metals r d. Others Specify: D.DESCRIPTION OF RESPONSE ACTIONS:(check all that apply,for volumes list cumulative amounts) 1.Assessment and/or Monitoring Only r 2.Temporary Covers or Caps 3.Deployment of Absorbent or Containment Materials r-4.Temporary Water Supplies r 5.Structure Venting System/HVAC Modification System r 6.Temporary Evacuation or Relocation of Residents 7.Product or NAPL Recovery r 8.Fencing and Sign Posting 9.Groundwater Treatment Systems r 10.Soil Vapor Extraction 11.Remedial Additives r- 12.Air Sparging 13.Active Exposure Pathway Mitigation System 14.Passive Exposure Pathway Mitigation System Revised: 11/14/2013 Page 2 of 6 r Massachusetts Department of Environmental Protection BWSC 105 LA .7), Bureau of Waste Site Cleanup Immediate Response Action (IRA) Transmittal Form Release Tracking Number Pursuant to 310 CMR 40.0424-40.0427 (Subpart D) - 28801 D.DESCRIPTION OF RESPONSE ACTIONS:(cont.) 15.Excavation of Contaminated Soils. r a.Re-use,Recycling or Treatment r i.On Site Estimated volume in cubic yards r ii.Off Site Estimated volume in cubic yards iia.Receiving Facility: Town: State: iib.Receiving Facility: Town: State: iii.Describe: r b.Store r i.On Site Estimated volume in cubic yards r ii.Off Site Estimated volume in cubic yards iia.Receiving Facility: Town: State: iib.Receiving Facility: Town: State: rv- c.Landfill r i.Cover Estimated volume in cubic yards 50 Receiving Facility: BOURNE ISWM FACILITY Town: BOURNE State: MA ii.Disposal Estimated volume in cubic yards Receiving Facility: Town: State: 16.Removal of Drums,Tanks,or Containers: a.Describe Quantity and Amount: b.Receiving Facility: Town: State: c.Receiving Facility: Town: State: 17.Removal of Other Contaminated Media: a.Specify Type and Volume: REMOVE 307 GALLONS IMPACTED WATER DE-WATERING TRADEBE STOUGHTON 18.Other Response Actions: Describe: 19.Use of Innovative Technologies: Describe: Revised: 11/14/2013 Page 3 of 6 I Massachusetts Department of Environmental Protection BwSC 105 Bureau of Waste Site Cleanup Immediate Response Action (IRA) Transmittal Form Release Tracking Number Pursuant to 310 CMR 40.0424-40.0427 (Subpart D) 28801 E.LSP SIGNATURE AND STAMP: I attest under the pains and penalties of perjury that I have personally examined and am familiar with this transmittal form,including any and all documents accompanying this submittal.In my professional opinion and judgment based upon application of(i)the standard of care in 309 CMR 4.02(1),(ii)the applicable provisionsof 309 CMR 4.02(2)and(3),and 309 CMR 4.03(2),and(iii)the provisions of 309 CMR 4.03(3), to the best of my knowledge,information and belief, >if Section B of this form indicates that an Immediate Response Action Plan is being submitted,the response action(s)that is(are)the subject of this submittal(i)has(have)been developed in accordance with the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000, (ii)is(are)appropriate and reasonable to accomplish thepurposes of such response action(s)as set forth in the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000 and(iii)complies(y)with the identified provisions of all orders,permits,and approvals identified in this submittal; >if Section B of this form indicates that an Imminent Hazard Evaluation is being submitted,this Imminent Hazard Evaluation was developed in accordance with the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000,and the assessment activity(ies)undertaken to support this Imminent Hazard Evaluation comply(ies)with the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000; >if Section B of this form indicates that an Immediate Response Action Status Report and/or a Remedial Monitoring Report is(are)being submitted,the response action(s)that is(are)the subject of this submittal(i)is(are)being implemented in accordance with the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000,(ii)is(are)appropriate and reasonable to accomplish the purposes of such response action(s)as set forth in the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000 and(iii)comply(ies)with the identified provisions of all orders,permits,and approvals identified in this submittal; >if Section B of this form indicates that an Immediate Response Action Completion Statement or a request to Terminate an Active Remedial System or Response Action(s)Taken to Address an Imminent Hazard is being submitted,the response action(s)that is(are)the subject of this submittal(i)has(have)been developed and implemented in accordance with the applicable provisions of M.G.L.c.21E and 310 CMR 40.0000,(ii)is(are)appropriate and reasonable to accomplish the purposes of such response action(s)as set forth in the applicable provisions of M.G.L.c.21E and 31.0 CMR 40.0000 and(iii)comply(ies)with the identified provisions of all orders,permits,and approvals identified in this submittal I am aware that significant penalties may result,including,but not limited to,possible fines and imprisonment,if I submit information which I know to be false,inaccurate or materially incomplete. 1.LSP#: 1707 2.First Name: JOHN 3.Last Name: TADEMA WIELANDT 4.Telephone: 508-535-0487 5.Ext: 6.Email: jtadema-weilandt@nsuwater.com 7.Signature: JOHN TADEMA-WIELANDT 8.Date: 7/20/2021 (--lddlyyyy) 9.LSP Stamp: Electronic -Sea] Revised: 11/14/2013 Page 4 of 6 F I" ]DENNETT ENVIRONMENTAL ASSOCIATES, LLC. A NATURAL SYSTEMS UTILITIES COMPANY LICENSED SITE PROFESSIONALS *ENVIRONMENTAL SCIENTISTS*GEOLOGISTS *ENGINEERS 1573 Main Street,Brewster,MA 02631 * 508-896-1706 * Fax 508-896-5109 * www.bennett-ea.com LETTER OF TRANSMITTAL TO: DATE: JOB NUMBER: Mr.Andrew Jones, Case Officer 7/20/21 K11381 MA Department of Environmental Protection MA(DEP) Southeast Regional office(SERO) REGARDING: Bureau of Waste Site Cleanup (BWSC) 20 Riverside Drive Lakeville, MA 02347 Immediate Response Action Completion and Permanent Solution Statement SHIPPING METHOD: Residential Evans[RTN 4-28801] Regular Mail ❑ Pick Up Priority ❑ 125 Harbor Bluffs Road, Hyannis MA Mail ❑ Hand Deliver ❑ Express Mail ❑ Other upload ❑ Certified Mail ❑ Green Card/RR COPIES DATE DESCRIPTION 1 7/20/2021 IRAC-PSS Report 0 For review and comment: ❑ For approval: ❑ As requested: ❑ For your use: REMARKS: CC: Doug and Betsy Evans—Property Owners Cosmo Gallinaro—Insurer's Representative Thomas"McKean,:Director Bamstable,Health.Dlvsio Mark S. Ells—Barnstable Town Manager* Peter J. Burke, Jr., Chief—Hyannis Fire Department* Darcy Karle,Administrator—Barnstable Conservation Department* *As part of Public Notice requirements, the report Title Page, Narrative, Index,Transmittal forms and Site Plan are included, pursuant to paperwork reduction policy. The full report is available as public record on the MA DEP website database at http://public.dep.state.ma.us/SearchableSites2/Search.aspx or, upon written request to BEA, full copy(electronic or paper)will be provided. FROM: David C Bennett, LPG,CGWP, LSP/John Tadema-Wielandt, LSP of Record/dmk If enclosures are not as noted,kindly notify us at once TOWN O.r^ BARNSTABLE M�j� o I b i AW 6 :JNDERGROUND FUEL AND CHEMICAL STORAGE SYSTEMS V��` ASSESSORS MAP NO. �� PARCEL NO. */� �� - 12 ADDRESS' lrn_�r IMIty®/Z S41)f- RA VILLAGE' #)(w //am InI9. og&ol NAME �rL�hL-�W B1L l %/9 VYl _ CONTACT PERSON /��/77 PHONE NUMBER 617- ! !Y &Z� LOCATION OF TALKS: CAPACITY: TYPE OF FUEL. AGE: TYPE: LEAK _OR CHEMICAL: t� DETECTION c.` _� d Swim t e �DAh Rodel 2 give-do � o ' r 3 -00 TAG riow 01J AGE m �° cL C-- DATE OF PURCHASE OF. EACH: 1. tAlVI 60 2. 3. 4. 5. DATE OF FIRE DEPARTMENT PERMIT: lt)&2"®(A) 1 TESTING CERTIFICATION SUBMITTED: ®G -oher. d9 7 PASSED �� DID NOT PASS PLEASE PROVIDE A SKETCH SHOWING THE LOCATION OF TANKS ON THE BACK OF THIS CARD. 4 ,be„u air a .��'� ocf®her TT Lj ��u IL 1-OC�►>t� n GLENTWORTH B. REAM AND ASSOCIATES ^. 632 MAIN ST.,DENNIS, MA 02638, P.O. BOX 931 _. 385-3991,385-3992 l�s HAZ75O2 '3LOW Ra 1PY1,Nu's, m& ®a4,0r amoS��Pc f IRK OFFICE, + INVOICE REMIT TO: Clean Harbors of Kin ston, Inc. Cape Cod Divs g ion lea' darbors 94 Thornton Drive ENVIRONMENTAL SERVICES COMPANIES Hyannis, MA 02601 P.O. BOX 510, BOSTON, MA 02102 (617) 849-1800 G E N o T Glen REam E s � ° 125 Harbor Bluff Road T E Same Hyannis, MA 02601 INV. DESC.: CUSTOMER SALESMAN PURCHASE ORDER NO. TERMS INVOICE DATE INVOICE NO. REA 300 HY _%30 5/3/88 1% 10, Net 15 5/4/88 HY0002 QUANTITY ITEM I.D. DESCRIPTION PRICE U/M AMOUNT Request payment for removal of tank as per .attached worksheets. CONTRACT PRICE: $ 1,600.00 TOTAL DISPOSAL: 100 gallons @ $1.15 per gallon 115.00 Disposal price includes Superfund fee SUB-TOTAL: . $ 1,715.00 I INVOICE TOTAL $ 1,715.00 TAX TRANSPORTATION PREPAID G'�d $ 1,715.00 JOB Nn. - P.O.NO. DA)'&D.4TE_��/ �- - leanHarbo -� . ------ .MAN/Eh,'TT.NO. 1 CON TRA CT MANIFEST NO. (24 Hour Service) IN VOICE NO. CONTACTPERSON MA (800)OIL-TANK NY (518)434-0149 PHONE NO. MA (617)269-5830 ME (207)799-8111 CLIENT /� / RI (401)438-5600 BILLING ADDRESS JOB LOCATION T� �1N 2 /qu f ATTN: LABOR EQUIPMENT NAME TITLE REEGG OT RATE AMOUNT QTY f TYPE Ht/RS RATE AMOUNT 1 1 TOTAL TOTAL MATERIAL DISPOSAL QTY RATE AMOUNT DESCRIPTION OTY RATE AMOUNT TYPE LIQUID {J/ _) SOLID TOTAL OTHER /I // AMOUNT TRANSPORTATION I ,ltifJ�' /,f/,,,(�, t/ �'"•- TOTAL TOTAL JOB DESCRIPTION TOTAL LABOR Xn TOTAL MATERIAL TOTAL EQUIPMENT TOTAL DISPOSAL LIQUID TOTAL DISPOSAL SOLIDS / - /`/X (/ TOTAL OTHER �-.j4-r�.-, OTHER y MATERIAL 5%SALES TAX Y I DAILY TOTAL +•. . • - CERTIE/EW ORKI-X T ....,t Cl.I:-IA ll.4 KRUR.1' n.a TI: h/; C6pe Code 6teanbhlp Auttw ly REFERENCE 4{ Sear hn 5�be gten Shae44R . � ' - GOOGLE SATELLITE IMAGERY 0 2021 a .ati m t - TOWN OF BARNSTABLE GIS MAPPING 2021 fTe� 4 BlacN tat Tureen � - ' � `S &LmMtPNk , ' ��MCkXwn fh k n„.; Fts {q 9 NOTE: THIS SITE PLAN WAS NOT PREPARED FROM ANY INSTRUMENT SURVEY AND UNDER NO CIRCUMSTANCES a +a. �� .; ' SHOULD THE DISTANCES, BEARING AND/OR OTHER FEATURES 5 SHOWN BE USED TO ESTABLISH PROPERTY LINES, ALL LOCATIONS ARE APPROXIMATE. >' a ms pp GZA 122 M w f 25 Habo Buff l8f N83°W G12312 I 0� w HYanma MAU26C, Flow N� 582°W 04/2I Ebb "- �n F = `. �BARN5TABLE Mm rtal r MA KEY MAP LEGEND v ij�TB TEST BORING f / -�-HB HAND BORING PAVED DRIVE /// 0 MW MONITORING WELL AREA OF PERMANENT SOLUTION STATEMENT RTN 4-2550 I 25' x 25' / / PAVED\ DRIVE — /TB-1 / A SEE DETAIL v MW-1, eDWELLIN ® i B-2 / (3)z GAL. --C W-2 EASTERN RFD + ' . C M • CEDARS,&O.C. LOT 3 f A+32A • AREA OF EXCAVATION 19,768 s.F I G' x I G' x 4' (4-8' b s) / RFMO 9.G5 MW-3 ��♦♦. 9 / y N e H B-1/f v v-I • ., .iy'� \t•7\.♦♦♦ MAP 325 .. ,.. �� /�/ 0 ,. \ \ ♦♦♦• PROP.5TOCKADE. .I PARCEL 119 • �' / �j .` \2l ♦♦♦. FENCE WITH 6' E NANCY'L JOHNSON �� 9HED Y/J O� -A � � � ♦♦♦♦ 5PACE UNDER " -TR AREA OF STAINING �pWrs, .♦♦♦.• I #137 '�� OFF�/� ♦♦♦ 5HRUBSL.BEACH PLUM I - I G / \ ♦ 5�♦♦• EACH PLUM I„ f, I} '.(/... ✓� `y`t.J HB-2 - I \. ♦ ♦ 3 yti�p I � \♦ � .♦ SHRUBS,5"O.C. •*✓ i �/ 1 y ! HB �� K� eO. SUMP X / , •~ •+ c c' T5-2 REPAIR/REPLACE 5TAIR5 t 1•, , MW 2 ,A5 NEC.ALLOW 314" �oP" ,- - .SPACING IN DEC$lIJG r \ } if .. 'j � I \\ /.✓ \ LANDWARD EXTENT v ? PATIO \\ COASTAL BARRIER RE5OURCE5 SYSTEM O FEMA IN5URANCE (N / EAWARD OF THI5 LINE) R 2 1 PORT Project: T5 DOUG & BETSY EVANS -.'MW-3 `Y 90 HARBOR BLUFF ROAD HYANNIS,MA 02601 Title: IMMEDIATE RESPONSE ACTION COMPLETION DETAIL with PERMANENT SOLUTION STATEMENT 125 HARBOR BLUFF ROAD-HYANNIS,MA 02601 SCALE I "=G' BENNETT ENVIRONMENTAL BEA: ASSOCIATES, LLC. n�uu `''ATE PLAN _ A NATURAL SYSTEMS UTILITIES COMPANY 0 30 GO 90 LICENSED SITE PROFESSIONALS,ENVIRONMENTAL SCIENTISTS, GEOLOGISTS,ENGINEERS SCALE I "=30' 1573 MAIN STREET,BREWSTER,MA 02631 PHONE:(508)896-1706 www.bennett-ea.com FAX:(508)896-5109 DATE SCALE BY CHECK JOB NUMBER 6/25/21 As Noted SRF DCB K11381DA.X.EV.901