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silo 3 - U.S. Department of Energy

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-- f ' ..<br />

Silos Project Environmental Monitoring Plan<br />

40000-PL-0010<br />

______ 0-69-. _- August 29, __ 2002<br />

l<br />

/<br />

1 The existing IEMP TLD monitoring network will be modified in late 2002 to take into account<br />

2 the pending relocation <strong>of</strong> the wastes stored in the K-65 <strong>silo</strong>s. As necessary, current TLD<br />

3 locations will be adjusted and new TLD locations added to adequately characterize and monitor<br />

4 the direct radiation in the vicinity <strong>of</strong> the AWR project and the site fenceline. The following<br />

5 new TLD locations are planned for the Silos area:<br />

6 0 Location 43 located on the western side <strong>of</strong> the Silos, near the KNW-A radon monitor,<br />

7 0 Location 44 located on the western side <strong>of</strong> the Silos, near the KSW-A radon monitor.<br />

8 Location 45 located on the southern side <strong>of</strong> the Silos, near the KSO radon monitor<br />

9 0 Location 46 located on the project boundary south on the transfer tank area building<br />

10 0 Location 47 located on the project boundary south <strong>of</strong> the planned location <strong>of</strong> the Silos 1<br />

11 and 2 remediation facility<br />

12<br />

13<br />

14<br />

15<br />

The <strong>silo</strong> area dirpct radiation monitoring locations (TLDs) are shown in Attachment A. Due to<br />

project construction activities, it may be necessary to re-locate TLDs. Changes in monitoring<br />

locations will be documented and approved through the DCN process<br />

16 3.3 Wastewater Monitoring<br />

17 All wastewater from the Silo 3 Project, AWR Project, and Silos 1 and 2 Project will be<br />

I 8 discharged to the FEMP Advanced Wastewater Treatment ( A M ) facility, after sampling to<br />

19 confirm that it is acceptable for transfer. Expected wastewater streams from Silos Project<br />

20 activities will be appropriately incorporated into the FEMP NPDES permit. Given the expected<br />

21 characteristics <strong>of</strong> the wastewater, and the discharge criteria for the AWWT, no wastewater<br />

22 unacceptable for transfer to the AWWT is expected to be generated. If analytical results for<br />

23 a particular batch <strong>of</strong> wastewater are found to be unacceptable, the batch will be managed on<br />

24 a case-by-case basis at the direction <strong>of</strong> AWWT operations. The specific disposition <strong>of</strong> the<br />

25 wastewater will be dependant upon factors including the amount, and specific characteristics<br />

26 <strong>of</strong> the batch <strong>of</strong> wastewater and upon current and planned AWWT operations at the time the<br />

27 AWR wastewater is generated. Details on the disposition <strong>of</strong> wastewater from each project<br />

28<br />

29<br />

30<br />

are provided in the Environmental Control Plan included in each project's Remedial Design<br />

-<br />

Package.<br />

31 Groundwater Monitoring<br />

32<br />

33<br />

34<br />

35<br />

36<br />

.- 37<br />

Groundwater monitoring is currently managed by the Aquifer Restoration Project (ARP). The<br />

ARP provides the monitoring necessary to identify the effect <strong>of</strong> FEMP remediation activities.<br />

This monitoring is adequate for assessing potential impacts on groundwater quality due to the<br />

Silo 3 and AWR projects. In the event that collection <strong>of</strong> groundwater samples is needed to<br />

support the projects (or to assess any incidental releases), ARP managers will be notified to<br />

coordinate the appropriate groundwater monitoring activity.<br />

6 <strong>of</strong> 7

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