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This report documents the analysis of data collected during the ER-20-11 well development and hydraulic testing (WDT).
This report presents the results of the next stage of sampling technology evaluations as described in Underground Test Area Activity Sampling Technologies Methods Plan (N-I, 2014b). Testing of the BESST Blatypus system was originally planned; however, communications with the vendor indicated it is premature for the UGTA Activity to field test this technology. The system currently uses latex tubing and nitrogen gas to push the water to the surface. The large amount of nitrogen gas needed due to the depths of the UGTA wells makes this unfeasible. Also, the latex tubing will likely not hold up in steel tubing. Instead, three technologies were evaluated: depth-discrete bailer, jack pump, and submersible pump. Each of these is a proven technology for certain conditions. The evaluation includes logistical and operational data collected during the purging of the well or completion interval and groundwater sampling at three wells.
This report includes the results of the E Tunnel Wastewater Disposal System (ETDS) inspections and monitoring for July, August, and September 2018. Monitoring and sampling activities were performed in accordance with the requirements of Water Pollution Control Permit NEV 96021, Revision 1, effective October 1, 2013. Monthly monitoring was conducted on July 16, August 13, and September 13, 2018. Operating personnel measured the instantaneous flow rate (see Table 1), log hydrogen ion activity (pH), temperature, and specific conductance of the discharge water (see Table 2). Monthly inspections also included an assessment of the general condition of the berms, including ponding (the water levels relative to the overflow pipes); any tunneling or burrowing into the berms; soil conditions on and around the berms, including erosion or sloughing of the interior or exterior slopes of the berms; seeps at the toe of the berms; the presence of any deep-rooting botanicals on the berms; and the physical condition of fencing (see Tables 3 through 7). Monthly rainfall quantities are presented in Table 8.
The Sampling Plans (Rev. 0 and Rev. 1) ensure routine sampling that is critical to understanding contaminant transport near and downgradient of the underground nuclear testing areas, and is designed to ensure compliance with the UGTA Activity Quality Assurance Plan and the Federal Facility Agreement and Consent Order. This report presents the analytical data for the 2018 calendar year (CY) (January 1 through December 31, 2018) to ensure that the Sampling Plans’ objectives are achieved. Appendix D presents data from samples collected in 2016 and 2017. These results were not reported in previous reports because they were not available from the specialized laboratories at the time of the publication of the reports.
The purpose of this CR is to provide a summary of the completed closure activities, documentation of waste disposal, and analytical data to confirm that the remediation goals were met.
The purpose of this Corrective Action Decision Document/Closure Report is to provide justification and documentation supporting the recommendation for closure of CAU 542 with no further corrective action. To achieve this, corrective action investigation (CAI) activities were performed from July 19 through August 25, 2006, as set forth in the Corrective Action Investigation Plan for Corrective Action Unit 542: Disposal Holes. The purpose of the CAI was to fulfill the following data needs as defined during the data quality objective (DQO) process: Determine whether contaminants of concern (COCs) are present. If COCs are present, determine the nature and extent. Provide sufficient information and data to complete appropriate corrective actions.
This calendar year (CY) 2021 annual sampling letter report presents Plan implementation and a summary of field activities, sampling methods, well completion diagrams, and analytical laboratory results from sampling of wells on Pahute Mesa. The CY 2021 letter report also presents data from samples collected in CY 2019. These CY 2019 results were not reported in previous sampling reports because they were not available from the specialized laboratory (Lawrence Livermore National Laboratory [LLNL]) at the time of the previous reports’ publication.
The purpose of this CR is to provide documentation supporting the completed corrective actions and data confirming that the closure objectives for CAU 572 were met. To achieve this, the following actions were performed: • Corrective action investigation (CAI) activities were performed from August 2020 through May 2023, as set forth in the SAFER Plan for CAU 572; and in accordance with the Soils Activity Quality Assurance Plan, which establishes requirements, technical planning, and general quality practices. • Corrective actions were completed during decontamination and demolition (D&D) and disposal activities, and were performed from August 2022 through September 2025.
The purpose of this addendum is to provide the waste disposal documentation for waste generated during the corrective action investigation.
This report serves as the combined annual report for post-closure activities in compliance with the requirements listed in Resource Conservation and Recovery Act Permit Number NEV HW0101 associated with the following closed corrective action units (CAUs): • CAU 90, Area 2 Bitcutter Containment • CAU 91, Area 3 U-3fi Injection Well • CAU 92, Area 6 Decon Pond Facility • CAU 110, Area 3 WMD U-3ax/bl Crater • CAU 111, Area 5 WMD Retired Mixed Waste Pits • CAU 112, Area 23 Hazardous Waste Trenches
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