Statement_of_Work_Redacted.pdf

STATEMENT OF WORK

FOR THE

CLOSURE OF BUILDING 96 MIXED WASTE STORAGE AREA

1. SCOPE/PURPOSE: This Statement of Work (SOW) outlines the requirements for the cleaning, remediation, and repurposing of areas that were previously used to store hazardous waste. This plan will close the area as described by Resource Conservation and Recovery Act (RCRA) and Toxic Substance Control Act (TSCA). This plan describes the facilities, addresses regulatory requirements, outlines the procedures that will be implemented to chemically decontaminate and close the facility, presents the sampling and laboratory analyses that will be performed to verify clean closure, discusses how the cleaning/decontamination wastes will be disposed of, and discusses closure certification.

{Paragraph 1.1)

2. BACKGROUND:

2.1. Building Location: Building 96 is located in the Controlled Industrial Area (CIA). The areas to which the SOW refers are located on the first floor within the Main Bay located towards the center of the building (Figures 1 and 2). The areas are adjacent to each other and have a door for access between the two areas. Most mixed waste storage occurred within the Primary Storage Area. Mixed waste may have also been stored in the Overflow Area. The Primary Storage Area consists of a 17’ x 27.5’ concrete pad bounded on all sides by a 10” berm [and/or cove]. The Overflow Area consists of a 26’ x 46’ room bounded by cement block walls and [coves]. For the purposes of this SOW the MWSA includes both the Primary Storage Area and the Overflow Area. {Paragraph 1.1)

2.2. Process Information: These rooms were used as a Mixed Waste Storage Area (MWSA).

Hazardous materials and waste containing RCRA heavy metals (e.g., cadmium, chromium, silver, arsenic, lead, selenium, barium, and mercury) along with polychlorinated biphenyls (PCBs) that are regulated by the TSCA were stored within the area. The facility has the capacity to store a maximum 260, 55-gallon capacity drums. The types of mixed wastes stored at the MWSA facility prior to off-site disposal are presented in Table 1. {Paragraph 1.1)

2.3. Radiological History: A radiological release of the area has been completed and approved by Portsmouth Naval Shipyard (PNS) and outside regulatory agencies. The radiological release was performed in accordance with Naval Nuclear Propulsion Program (NNPP) requirements. NNPP established comprehensive and prescriptive requirements for the control of radioactivity pursuant to its Atomic Energy Act (AEA) authority, and subsequently also to its authority under Executive Order 12344 and Public Law No. 98-525 §1634. These requirements provide national uniformity in the control of radiation and radioactivity at the NNPP’s Navy and Department of Energy activities, and are applicable to all radioactivities associated with the NNPP, including materials that have been determined to be wastes, and radiological release of radiological facilities storing radioactive materials brittney.meurrens Highlight brittney.meurrens Highlight brittney.meurrens Highlight or waste. This will allow RCRA and TSCA closure of the facility to be accomplished using standard analytical techniques and methodologies.

3. GENERAL:

3.1. All mentions of paragraph numbers after a paragraph are in reference to the Closure plan, Appendix G of the Part B permit application submitted to Maine Department of Environmental Protection (DEP). Paragraph numbers appear in italics.

3.2. Safety Requirements:

3.2.1. Work Site Operation Safety Environment: Contractors and non-PNS Government Agencies (NPGAs) shall be responsible to read and understand the requirements of OSHECM Chapter 250 (Government provided).

3.2.2. The work will be performed in accordance with 29 CFR Part 1910.120 requirements including OSHA trained workers with personal protective equipment and clothing.

{Paragraph 3.2.1)

3.2.3. Hazardous Energy Control (HEC): Contractors and NPGAs are hereby informed that their employees and representatives present on property under PNS cognizance must adhere to Federal OSHA requirements for hazardous energy control lAW 29 CFR 1915.89 and must follow HEC procedures as identified in NAVSEA’s OSHECM Chapter 250 (latest revision). Use Attachment 1 when HEC is required.

3.2.3.1. When performing work under a PNS contract, all HEC work to be performed by Contractors and NPGAs require that PNS Technical Points of Contact (TPOC) and/or Contracting Officer’s Representative (CORs) be notified of the HEC scope of work prior to starting work. Any changes or deviations in the initial scope of HEC work requires the PNS TPOC and/or CORs be informed of the change/deviation. Appendix 250.B-1 through B-3 of OSHECM Chapter 250 for multiple employer work identifies when Contractor’s and NPGAs are required to assign their Lockout/Tagout-Plus Coordinator (LOTC) to coordinate HEC work with the designated PNS LOTC. HEC locks shall have red bodies and meet the requirements of OSHECM Chapter 250, which includes having labels, or tags affixed to the HEC locks to identify who installs the HEC lock(s) and to provide a point of contact telephone number. HEC locks shall be provided by the contractor of NPGA for their employees use. HEC tags used for Tag-Plus HEC work shall be provided by the designated PNS LOTC to the contractor or NPGA for their use if machinery, equipment, or systems cannot be locked out. OSHECM 250 Tags-Plus procedures will be strictly enforced.

3.2.4. Accidents: The Contractor shall notify the Government TPOC within one (1) hour of the occurrence of any accidents and incidents resulting in personal injury, loss of life, property damage to a government facility or equipment.

3.3. Contractor Work Requirements: Contractors are responsible for reading Attachment 2

- Work at PNS Guidance and adhering to these standards.

3.4. PNS shall retain ownership of all deliverables produced by the contractor.

4. REQUIREMENTS:

4.1. Government Responsibilities:

4.1.1. Vacate personnel currently occupying the areas of Building 96 to assist in accomplishing the required work of this SOW. Provide an area to decontaminate tooling, obtain samples, and lay a decontamination pad along with other required work presented in the Contractor Responsibilities section.

4.1.2. Ensure that all waste inventory has been removed from the area and all non-permanent items are removed. {Paragraph 2)

4.1.3. Ensure access to the area is available for the contractor and all security measures are met.

4.1.4. Ensure space is available to set-up the decontamination pad scoped in the initial site set-up.

4.1.5. Provide the contractor with any records of hazardous materials spilled within the MWSA.

{Paragraph 3.1)

4.1.6. Provide a copy of the latest revision of OSHCHEM Chapter 250 to the contractor.

4.1.7. PNS will provide an onsite point of contact as needed by the contractor during the contract period.

4.1.8. Provide a copy of the Appendix G closure plan for reference to the contractor when accomplishing this SOW.

4.1.9. Ensure operating hours of Building 357 are communicated to the contractor for disposal of waste.

4.2. Contractor Responsibilities:

4.2.1. Qualifications and Services:

4.2.1.1. The contractor shall clearly demonstrate a minimum of 10 years’ experience on removal and disposal of building debris that have been used/exposed to hazardous material.

4.2.1.2. The contractor shall employ/hire a Maine licensed independent professional engineer.

4.2.1.3. The contractor shall provide all services within 60 days of award.

4.2.2. Initial Site Set-up and Processes:

4.2.2.1. A temporary decontamination pad will be established/constructed in Building 96 adjacent to the MWSA. {Paragraph 3.2.1)

A.2.2.2. Equipment, tools, and other smaller objects used at the MWSA will be decontaminated over the decontamination pad by scrubbing/washing them with soap followed by two separate cleanings with a high-pressure, high water temperature washer (steam cleaner) to remove any waste residue. The wastewater and first cleaning rinse water will be transferred from the decontamination pad to 55-gallon DOT drums for sampling and analysis, (Table 2 and Table 3) and disposal by the government at Building 357. {Paragraph 3.2.1)

4.2.2.3. Construction equipment used in closure work will be required to be decontaminated over the decontamination pad prior to the start of work, and upon completion of work and prior to moving the equipment off-site to prevent cross contamination. A high-pressure, high-temperature washer will be used to decontaminate the equipment. The decontamination rinse water will be collected and containerized separately for sampling and analysis off-site. Waste generated for disposal shall be delivered to Building 357 before the end of the shift and not stored onsite over multiple shifts. {Paragraph 3.2.1)

4.2.2.4. Decontamination of personnel is not necessary due to the use of disposable gloves and other disposable personal protective equipment (PPE) for decontamination and sampling. PPE and sampling tools that are single use will be disposed of as industrial waste.

4.2.3. Removal of Visible Debris:

4.2.3.1. Remove any visible debris from the floor and walls by scraping and vacuuming.

Containerize and consolidate the solid waste for sampling and analysis off-site. Waste generated for disposal shall be delivered to Building 357 before the end of the shift and not stored onsite over multiple shifts. Label the container(s) identifying its contents. {Paragraph 3.2.2.1)

4.2.4. Stains. Residue, and First Steam Cleaning:

4 2.4.1. Where stains are present or residue remains after scraping, scrub areas with soap and water. Clean/wash all surfaces with a high-pressure, high temperature washer (steam cleaner) and vacuum up the liquid and condensate. Containerize the liquid and label the container(s) identifying its content. {Paragraph 3.2.2.2)

4.2A.2. Combine and containerize the first cleaning rinse water separately from each room. Label the containers as “First Cleaning Rinse Water.” {Paragraph 3.2.1)

4.2.5. Second Cleaning:

4.2.5.1. A second cleaning with a high-pressure, high temperature washer will be performed. The second cleaning rinse water will be containerized in a separate container for closure documentation sampling and analysis as discussed in Table 2 and Table 3.

Containerize the liquid from the second cleaning and vacuum up the liquid and condensate (i.e., second cleaning rinse water) separately from the first cleaning. Label the container(s) identifying its contents. Transfer the containers to Building 357 by the end of the shift.

{Paragraph 3.2.1, 3.2.2.3)

4.2.5.2. Combine and containerize the second cleaning rinse water separately from each room. Label the containers as “Second Cleaning Rinse Water.” {Paragraph 3.2.1)

4.2.5.3. Except for volatile analyses, a composite sample from the container(s) of the second cleaning rinse water from each room will be taken and analyzed for constituents stored in those areas by the methods specified in Table 2 and Table 3. Where volatile analyses are specified, take a separate sample from each container for laboratory analyses.

{Paragraph 3.3.1)

4.2.6. Cracks. Staining, and Soil Sampling:

4.2.6.1. The floor of the MWSA will be visually inspected for physical evidence of chemical contamination (e.g., signs of spills, presence of liquid, stains, and residues). The MWSA operation log will be reviewed for any record of spills (government provided).

Sampling will be performed in those areas showing physical evidence of chemical contamination or indicated as spill areas in the operation record in addition to the other sample locations outlined in Table 3. Inspect the surface for cracks with evidence of staining and note location. Where staining is evident in cracks, chisel cracked areas until staining is removed to Vz inch on either side of the crack and to a depth of % inch below the base of the crack/stain using clean tools. Prior to chiseling individual stain cracks, the chiseling tools will be steam cleaned to prevent cross contamination. A new pair of chemically clean nitrile gloves will be worn each time an individual stain is chiseled.

Vacuum all debris and the immediate area. Containerize and consolidate the solid wastes in DOT container(s) and label the container(s) to identify the contents. {Paragraph 3.2.2.5)

4.2.6.2. Where a crack with staining is evident and removed and where the crack extends through the full depth of the concrete, the soil below this location will be sampled and analyzed for Total Volatiles by SW-846 8260; Total and TCLP Metals by SW-846 6010;

Total Semivolatiles by SW-846 8270; and PCBs by SW-846 8082. {Paragraph 3.3.2)

4.2.6.2.1. At least two background soil samples will be taken and analyzed for TCLP Volatiles by SW-846 8260; Total and TCLP Metals by SW-846 6010; Total and TCLP

Semivolatiles by SW-846 8270; and Total RGBs by SW-846 8082. TCLP extraction conducted by SW-846 1311 and RGB extraction by SW-846 3540. The background samples shall be taken at locations that are mutually agreeable to RNS and the ME-DER.

{Paragraph 3.3.2)

4.2.6.2.2. The concrete will be cored with a thin walled coring machine and a hand auger or split spoon sampler will be utilized to obtain a soil sample from 0 to 12 inches below the depth of the concrete slab. The soil samples will be placed in ERA approved clean glass containers for the analyses to be performed. The sampling equipment will be cleaned before and after each sample to prevent cross contamination. {Paragraph 3.3.2)

4.2.6.2.3. Equipment and sampling tools that will be reused will be decontaminated after each use according to the procedures specified below in order to prevent cross contamination {Paragraph 3.3.2):

4.2.6.2.3.1. Wash with tap water and non-phosphate detergent;

4.2.6.2.3.2. Rinse with tap water;

4.2.6.2.3.3. Rinse with 10% nitric acid, ultrapure;

4.2.6.2.3.4. Rinse with tap water;

4.2.6.2.3.5. Rinse with methanol;

4.2.6.2.3.6. Rinse with pesticide-grade hexane;

4.2.6.2.3.7. Rinse with deionized water;

4.2.6.2.3.8. Air-dry and wrap in aluminum foil.

4.2.6.2.4. The samples will be stored in a cooler with ice packs to keep the samples cool until they are delivered to the laboratory for analysis. A chain of custody record form will be utilized (completed by a sampler in field) to track the samples from when they are taken in the field until they are delivered to the laboratory. The chain of custody record form will be signed with the date and time by relinquishing and receiving parties and by the laboratory personnel when the samples are received by the laboratory. {Paragraph 3.3.2)

4.2.6.2.5. The soil sampling results will be evaluated by first subtracting out the background/control sample values from the soil closure documentation sample values. If the resulting concentration of constituents in the soil are below ERA media protection standards for RNS or below ME-DER soil protection criteria; and if the constituents are not leaching out of the soil above the Maine MEG or the ERA MGL, where limits have not been established, or the practical quantitation limit where MEG or MGL limits have not been established', then the soil will not be considered contaminated and further action will not be necessary. ’ If contaminated soil is encountered, additional investigations will b® con<lu^^e^ and the situation evaluated with the ME-DER as to what action will be taken. The MEDEP soil protection criteria will be calculated in accordance with the ME-DER Guidance Manual for Human Health Risk Assessments at Hazardous Substance Sites dated June 1994.

{Paragraph 3.3.2)

4.2.6.3. Gonduct sampling and laboratory analysis specified in Table 2 and Table 3 to document that no hazardous wastes remain, and to determine if decontamination is

Rage 6 of 17 complete. Repeat the above cleaning procedures until the facilities have been sufficiently decontaminated as specified in Table 2 and Table 3. {Paragraph 3.2.2.6)

4.2.7. Sampling. Laboratory Analysis. Quality Assurance and Quality Control (QA and

QC):

4.2.7.1. Sampling:

4.2.7.1.1. Ensure all sampling containers are prepared with appropriate preservatives for the applicable sampling procedures and potential chlorinated tap water usage.

4.2.7.1.2. Samples will be placed in appropriate containers, labeled for identification, tracking, and logged in the field logbook. A sample analysis request or equivalent document will be completed after each sample is taken to establish the chain of custody. The chain of custody ensures sample integrity and tracking of sample custody.

4.2.7.1.3. Quality control samples will be taken during the field sampling to monitor sampling technique, sampling equipment cleanliness, sample variability, sample handling, and laboratory performance (analytical reproducibility). The quality control samples will include replicate samples, equipment/field blanks and transport blanks. (Paragraph 3.3.3)

4.2.7.1.4. Replicate samples are samples taken from the same location and sampling device. Replicate samples are used to check on sampling technique and sample variability.

The replicate samples will be coded so that the laboratory is not biased on performing the analyses. The code that is used will be identified in the field report. (Paragraph 3.3.3)

4.2.7.1.5. One replicate second cleaning decontamination rinse water sample will be taken and submitted to the laboratory for analysis. (Paragraph 3.3.3)

4.2.7.1.6. Equipment/field blanks are samples taken to monitor sampling equipment cleanliness and decontamination procedures during field sampling. One equipment/field blank will be taken during sampling of the second cleaning decontamination rinse water for every ten investigative samples submitted to the laboratory for analysis. The equipment/field blanks will be taken by pouring deionized water over the sampling equipment and collecting the liquid in the sample container. The samples will be analyzed for the same parameters as the closure documentation samples. (Paragraph 3.3.3)

4.2.7.1.7. Transport blanks are prepared when volatile organic compounds (VOCs) analysis is to be performed, and they are prepared in the laboratory when the sample containers are prepared. Transport blanks will be prepared in triplicate by filling 40 mL glass containers (with Teflon lined septum) with deionized water. These containers will travel unopened with the sample containers and be analyzed for the same volatile constituents as the samples being submitted. The transport blanks are taken to monitor whether the samples have been contaminated during transport, as a result of handling in the field, during shipment or during storage in the laboratory. One transport blank will accompany each set of samples that are shipped/delivered to the laboratory for VOC analysis. (Paragraph 3.3.3)

4.2.7.1.8. A summary of the number of QA/QC samples required is presented in Table 3.

{Paragraph 3.3.3)

A.2.7.2. Laboratory Analyses:

4.2.7.2.1. Laboratory quality control checks will be those specified in EPA Methods for the analytical method performed and will generally consist of some or all of the following {Paragraph 3.3.3):

A.2.7.2.1.1. Blanks (method, preparation),

4.2.7.2.1.2. Initial and continuing calibrations,

4.2.7.2.1.3. Surrogate spikes,

4.2.7.2.1.4. Matrix spikes/matrix spike duplicates,

4.2.7.2.1.5. Duplicate samples, and control samples.

4.2.7.2.2. A laboratory quality assurance/quality control (QA/QC) data package will be prepared that documents the laboratory QA/QC procedures that were performed.

{Paragraph 3.3.3)

4.2.7.2.3. The data package will include the following {Paragraph 3.3.3):

4.2.7.2.3.1. A case narratiye including sample ID, client ID, matrix, date sampled, a description of problems encountered during the analysis and a certification statement.

{Paragraph 3.3.3)

4 2.7.2.3.2. A summary sheet containing results for each sample analyzed. The summary sheet should include: site name, sample number, sample matrix, sampler, sample location, date receiyed, date analyzed, analyst, analysis method and parameter, methodology used, PQL, results with units and any analyst qualifiers, and completed laboratory quality control data report forms for all internal quality control procedures (i.e., controls, blanks, matrix spikes, matrix spike duplicates, etc.). {Paragraph 3.3.3)

4 2 7 2.4. The data deliyerable package will be submitted for all closure documentation samples, for soil samples, if taken, and for QA/QC samples. {Paragraph 3.3.3)

4.2.8. Disposal:

4.2.8.1. At completion of the decontamination procedures, the decontamination wastes will be sampled and analyzed to determine the waste’s proper method of disposal. Four types of decontamination waste will be generated including solid material from scraping and yacuuming, liquid from cleaning/washing and steam cleaning, liquid from decontaminating the contractor’s equipment, and waste soils. The yolume of solid material is anticipated to be minimal (less than one 55-gallon drum). The yolume of liquid waste is anticipated to be two to four 55-gallon drums, and the yolume of liquid from decontaminating the contractor s equipment is anticipated to be one 55-gallon drum. {Paragraph 3.4)

4.2.8.2. Each drum of decontamination waste will be sampled and analyzed for Total Volatiles by SW-846 8260; Total and TCLP Metals by SW-846 6010; Total Semivolatiles by SW-846 8270; and PCBs by SW-846 8082 to determine if the waste is hazardous or not.

Table 3 summarizes the number of samples to be taken of the decontamination wastes.

The samples will be taken in accordance with SW-846, Chapter 9 - Sampling Plan; and a statistical analysis performed, if necessary, in accordance with SW-846 protocols (Chapter 9, page 13). {Paragraph 3.4)

4.2.8.2.1. Based on the laboratory analyses, the decontamination wastes will be properly shipped to off-site permitted facilities. Rinsate generated during decontamination of sampling equipment will be collected, analyzed, and placed in DOT containers and stored at Building 357 until testing results determine the disposal requirements. Rinsates shall be delivered to Building 357 before the end of the shift and not stored onsite over multiple shifts.(Paragraph 3.4)

4.2.9. Closure Documentation:

4.2.9.1. Decontamination Liquid Wastes, Bulk Sampling, and Analysis: At completion of the decontamination procedures, sampling and laboratory analyses will be conducted to document that no hazardous wastes remain and that the facilities have been sufficiently decontaminated to protect human health and welfare, and the environment. Sample collections, storage, handling and chain of custody procedures specified in the facility’s closure plan and in US EPA “SW-846, Test Methods for Evaluating Solid Waste, Chapter 9

- Sampling Plan” will be followed. {Paragraph 3.3.1)

4.2.9.2. One to two containers per area of the second cleaning decontamination rinse water are anticipated to be generated. The estimated number of closure documentation samples to be taken is summarized in Table 3.

4.2.9.3. If these results are below applicable Total Volatiles, Total and TCLP Metals, and Total Semi-Volatiles regulatory levels presented in 40 CFR Part 261.24(b) and the PCB regulatory levels of 40 CFR Part 761, then any hazardous wastes that were potentially present will be considered removed. If no constituents are detected above the State of Maine Maximum Exposure Guideline (MEG; revised 9/92), the EPA Maximum Contamination Level (MCL), or the practical quantitation limit (PQL) if no MEG or MCL exists for the parameters, then the respective facility will be considered sufficiently decontaminated to be protective of human health and welfare and the environment. Where the MEG or MCL is lower than the PQL for the specified method, the PQL will be the limit. If constituents are detected, then additional cleaning specified in Section 4.2.4 and 4.2.5 will be conducted until the above criteria are met.

4 2.9.4. The Total Volatiles, Total and TCLP Metals, and Total Semi-Volatiles results and PCB results of the samples described above will be compared to regulatory levels presented in 40 CFR Part 261.24(b) and PCBs 40 CFR Part 761. If all the closure documentation sample results are below the regulatory levels after the control sample values have been subtracted from the closure documentation sample values, then no hazardous wastes will be considered present. If one or more of the results is positive, a statistical analyses will be performed in accordance with SW-846 protocols (Chapter 9, page 13) to determine if the concrete is considered hazardous or not and whether additional decontamination and subsequent sampling and analyses are necessary. Additional concrete will be removed from the crack(s) if the concrete is determined to still be hazardous.

4.2.9.5. The Total Volatiles, Total and TCLP Metals, Total Semi-Volatiles, and PCB results of the bulk samples described above will also be compared to the MEG, (revised 9/92) and the EPA MCL for the applicable parameters. If no constituents are present that would leach out of the concrete above the Maine MEG or the EPA MCL, where limits have been established, or the PQL where MEG or MCL limits have not been established, after the control sample values have been subtracted from the closure documentation sample values, then the concrete will be considered to be sufficiently decontaminated to be protective of human health and welfare, and the environment.

4.2.10. Closure Certification:

4.2.10.1. A Maine licensed independent professional engineer will be retained to observe the closure activities to ensure the work is performed in accordance with the approved closure plan; and to prepare a closure certification to document the completion of the closure work. The certification of closure will be signed by the Maine licensed professional engineer and by the owner or operator of the PNS MWSA. The certification of closure will include the following {Paragraph 5):

4.2.10.2. A copy of the approved closure plan and letter from the Maine DEP approving the plan. {Paragraph 5)

4.2.10.3. A discussion on the history of spills and associated cleanup at the facility.

{Paragraph 5)

4.2.10.4. Closure activities conducted, name of the contractor(s), certifications, and observations of closure procedures. {Paragraph 5)

4.2.10.5. Sampling and laboratory analyses results. {Paragraph 5)

4.2.10.6. Documentation of disposal of cleaning wastes. {Paragraph 5)

4.2.10.7. Date of completion of closure activities. {Paragraph 5)

4.2.10.8. Certification statement. {Paragraph 5)

5. DELIVERABLES:

5.1. Contractor shall provide a certificate stating that all levels of cadmium, chromium, silver, arsenic, lead, selenium, barium, mercury, and PCBs have been reduced to acceptable levels per Industrial Hygiene Field Operation Manual (IHFOM) Chapter 3, Appendix 3-B.

5.2. The report documenting the results of the independent Maine Professional Engineer closure certification.

6. SECURITY:

6.1. Building 96 is within the CIA of PNS. Any persons not known to be an American citizen of good standing and repute shall be ineligible for access to PNS. Registration in Defense Biometric Identification System (DBIDS) is required. One of the following, either a) or b) is required for proof of citizenship:

a) Passport

b) Driver’s license and birth certificate

Contact the Pass and ID office for entry requirements

Pass and ID office located at Gate 1 Building 384 Hours of Operation; 0600-1430 Monday through Friday Contact Information: (207)-438-2235

6.2. Hours of Work: The work will take place in Building 96 of PNS. All work shall be accomplished during normal working hours of PNS, Kittery, ME, 7:00AM until 3:30PM, Monday through Friday. The on-site work must be coordinated with Code 2380.1 and Code

106.3 point of contact (POC) as it will impact the production environment. The dates may be changed based on the needs of PNS. A pre-construction meeting shall be arranged by the contractor within two weeks of award.

7. REFERENCES:

(a) 29 CFR 1910.120 - OSHA’s standard for Hazardous Waste Operations and Emergency Response

(b) OSHECM 250

(c) 1915.89 - Hazardous Energy Control

8. ATTACHMENTS:

Attachment 1 - Hazardous Energy Control brittney.meurrens Highlight

Attachment 2 - Work at PNS Guidance

End of Statement of Work

Figure 1: Location of Building 96 at PNS

Figure 2: Location of the MWSA within the Main Bay of Building 96:

brittney.meurrens Highlight brittney.meurrens Highlight overflow

AREA

PRIMARY

STORAGE

AREA

Table 1: List of mixed wastes stored at the MWSA

Waste Stream Name Waste Stream

ID#

Examples

Mixed Waste Requiring Organic/Characteristic T reatment

MW1 Paint chips, absorbents containing chromate solution, industrial waste containing toxic metals, special hull treatment, chromate liquid, toxic metals from vacuum cleaner debris

Mixed Waste For Macroencapsulation Treatment

MW2 HEPA filters, lead bricks, lead sheet, lead wool, lead shot, absorbents with chromate solution, toxic job control waste.

Mixed Waste Containing PCBs

MW3 Paint chips, absorbents, job control waste, and vacuum cleaner debris containing toxic metals and PCBs.

Potassium Chromate Solution

MW7x Liquid Potassium Chromate Solution

Liquid Waste with Heavy Metals/Corrosivity Characteristic

MWlOx Liquid Waste with Heavy Metals/Corrosivity Characteristic

Table 2; Laboratory analyses and methods for second (final) cleaning rinse water closure documentation samples

Storage Area Analyses and Methods Equipment and items Total Volatiles by SW-846 8260; TCLP

Metals by SW-846 6010; Total Semivolatiles by SW-846 8270; PCBs by

SW-846 8082

Storage rooms TCLP Metals by SW-846 6010; Total Volatiles by SW-846 8260; Total Semivolatiles by SW-846 8270; PCBs by

SW-846 8082

Table 3; Closure documentation samples and decontamination waste samples required

Sample Justification Sample Location/type Number of Samples 2nd Cleaning Decontamination Rinse Water

MWSA 1 sample per container for volatile analyses and 1 composite of every two containers for other analyses

Soil Sample MWSA - below cracks in stained concrete

1 per crack

Soil Sample Background/control samples

2, if soil sampling is necessary

QA/QC Replicate of second cleaning decontamination rinse water

1 for every 10 samples submitted to the laboratory (1 min)

QA/QC Replicate of wipe and bulk samples

1 for every 10 samples of each type submitted to the laboratory (1 min)

QA/QC Equipment/field blank during sampling of second cleaning decontamination rinse water

1 for every 10 samples submitted to the laboratory (1 min)

QA/QC Equipment/field blank during bulk sampling

1 for every 10 samples submitted to the laboratory (1 min)

QA/QC Transport blanks One per set (i.e., cooler) of samples shipped/delivered to laboratory for volatile analyses (1 min)

Decontamination Waste Solid material from scraping and vacuuming

1 (One from each container)

Decontamination Waste Liquid from cleaning/washing and steam cleaning

4 (One from each container)

Decontamination Waste Liquid from decontaminating the contractor’s equipment

1 (One from each container)

Attachment (1) - Hazardous Energy Control

Contractor Compliance Certification Document Rev C 2/10/2016

Purchase Order Number:, New Equipment; Y / N Company Name:_______

Job Location:

Date:

By the contractor's representative's signature below the contractor's representative certifies that the Company whose name is listed above understands and agrees to the following requirements for any task or work the contractor performs aboard the Portsmouth Naval Shipyard (NAVSHIPYD PTSMH) that involves Hazardous Energy Control (HEC).

29 CFR Part 1915.89, which became effective and enforceable on 31 October 2011, provided a new standard addressing hazardous energy control in shipyard employment. Part 1915.89 applies to private-sector contractors performing servicing operations in shipyard employment, and states the Navy's HEC Program is in effect in Naval Shipyards. Private-sector contractors performing work that involves HEC aboard NAVSHIPYD PTSMH are responsible for ensuring the safety of their employees who may perform tasks or work involving HEC.

The contractor's representative's signature below certifies that the contractor understands and shall comply with all requirements for work involving HEC as provided in 29 CFR Part 1915.89 and the Naval Sea Systems Command (NAVSEA) Occupational Safety, Health and Environ mental Corporate Manual (OSHECM) Chapter 250 (latest revision), including Lockout/Tags-Plus (LOTP). The text of 29 CFR Part 1915.89 is available at the OSHA Fact Sheet web site.

WARNING: CONTRACTOR'S FAILURE TO COMPLY WITH THE HEC REQUIREMENTS REFLECTED IN 29

CFR PART 1915.89 AND OSHECM CHAPTER 250 MAY CAUSE SERIOUS INJURY OR DEATH TO THE

CONTRACTOR 'S EMPLOYEES. UNDER NO CIRCUMSTANCES SHALL THE PORTSMOUTH NAVAL

SHIPYARD ASSUME ANY LIABILITIES THAT RTGHTLY ARE THE RESPONSIBILITIES OF THE

CONTRACTOR.

Shop Card Holder/PO:______________________________________________

Lockout/Tags-Plus Coordinator;, Coordination Required (circle one) (Y / N ) LOTP Serial Number:, Contractor's Representative's Name (Print clearly)

Contractor's Representative's Signature

Date:

Fax completed copy to LOTP Committee at x2540

Attachment (2) - Work at PNS Guidance

The following is Guidance for Contractors working/conducting business atNAVSEA Portsmouth Naval Shipyard:

1. Mercury Control (Supplies): Mercury or mercury containing compounds shall not be intentionally added or come in direct contact with hardware or supplies furnished under this contract.

2. Vendor access to Portsmouth Naval Shipyard: Only an American citizen of good standing and repute shall be eligible for access to Portsmouth Naval Shipyard and adjacent areas. Proof of citizenship will be required. Entrance of foreign nationals requires approval. (Ref: SECN AVINST) 5510.34

3. Safety: All representatives who have a need to enter the Controlled Industrial Area, or other areas specifically designated as safety hazardous, should provide themselves with safety headwear to be worn while in the area. Vendors and/or subcontractors performing work on vendor-owned or government-owned plant facilities and equipment shall ensure that all OSH A safety regulations are followed. Prior to working on the Portsmouth Naval Shipyard. All vendors shall view the Code I06 safety video.

4. Security: Commercial vehicles (automobiles) must have conspicuous contractor (company) identification (such as magnetic door-type signs) affixed to the outside of the vehicle if it is to enter the Controlled Industrial Area.

5. OSHA Health and Safety: Vendors preparing specifications, designs or drawings for design, modification or procurement of plant facilities and equipment shall ensure that the appropriate OSHA criteria are included. OSHA regulations must be met except when more stringent Navy requirements apply.

6. Restrictions on use of Yellow Material: Yellow colored items such as those described below are of special significance within the Shipyard and are subject to strict controls. Accordingly, contractors shall not use yellow or orange-yellow colored materials for the following purposes: protective clothing, hoods, sheeting, tarpaulins, polyethylene bottles or other containers, tapes, bags, banding, identification marks on tools, boundary markers, ribbons, vent ducts, etc. Contractor generated yellow colored waste shall be disposed of by the Contractor off-yard. Shipyard refuse containers shall not be used for disposal of yellow colored waste materials. Yellow colored contract generated debris shall be bagged in non-translucent containers, and promptly removed from the Portsmouth Naval Shipyard.

7. Radiological Indoctrination: All Contractor employees performing work with in the Portsmouth Naval Shipyard must view a radiological video. Contractor employees who are expected to be on the Shipyard for greater than thirty (30) calendar days must attend a one-half hour indoctrination briefing. Attendance at the briefing will be required prior to being issued a permanent Shipyard badge. The indoctrination briefing will provide radiological fundamentals and information on radiological postings and controls at the Portsmouth Naval Shipyard.

8. Radiological Postings and Instructions: Any one of a contractor's employee who disregards, alters, moves or otherwise tampers with a radiological posting, or who disobeys a radiological instruction, will not be allowed to continue working at the Portsmouth Naval Shipyard.

9. Removal of Hazardous Material: All contractors, vendors or repair personnel shall be responsible for removal from the Portsmouth Naval Shipyard any appliances, bulbs, lamps or other devices which they replace that contain hazardous chemicals or materials.

10.Specification changes: No changes to specification or other contract technical requirements are allowed without Contracting Officer approval.