Dames & Moore, 1999 - USDA Forest Service
Dames & Moore, 1999 - USDA Forest Service Dames & Moore, 1999 - USDA Forest Service
concentrations were not above MTCA levels. Iron ranged from 54,000 mgkg to 85,300 mg/kg, above background (24,100 mgkg). Aluminum ranged from 32,000 mgkg to 44,000 mgkg. A subsurface tailings sample, TP2-4 (5 to 10 fi bgs), was collected by the USBM in 1994. Barium, cadmium, copper, iron, lead, mercury, thallium, and zinc concentrations were above background; however MTCA levels were not exceeded with the exception of cadmium. Cadmium (16.2 mg/kg) was above the MTCA Method A level (2 mgkg). Iron (61,400 mgkg) was above background (24,100 mgkg). Aluminum concentrations were significantly greater in the samples collected by the USGS than those collected by the USBM. It was determined that the USGS samples were collected from the surface tailings at the toes of the tailings piles whereas the USBM and RI samples were collected on the top of the tailings piles. Additional metals detected at the toe of the slopes were above concentrations detected on the tops of the tailings piles. However, both of the data sets were considered when reviewing the data for PCOCs and comparing to the RI data. 5.2.6.2 RI Tailings Samples Surface and subsurface samples were collected during the RI from each tailings pile. The samples associated with each tailings pile is provided below. Surface Subsurface Tailings Pile 1 DMSS-I 1 DMSS-I2 DMSS-13 DMTP 1-2 DMTPI-3A DMTPI -3B DMTPI-4 Tailings Pile 3 DMSS-17 DMSS-I8 , DMSS- 19 DMTP3- I DMTP3-2 DMTP3-3A DMTP3-3B DMTP3-4A (7 feet bgs) DMTP3-4AX (Duplicate) DMTP3-4B (10 feet bgs) Sample locations are provided on Figure 5.2-1 and analytical data are summarized in Table 5.2-5. Samples were analyzed for metals only. Copper, iron, lead, molybdenum, and silver were above background in the surface samples collected; however, all concentrations were below available MTCA levels. Barium and zinc were above background in a limited number of samples, but well below MTCA levels. Iron ranged from 53,400 mgkg to 73,700 mgkg. The USBM data from surface samples collected from the tops of the tailings piles was compared to RI data. The data were similar in concentration and were well within an order of magnitude. The subsurface samples were collected between 2.5 and 5 feet bgs from test pits completed in tailings piles 1, 2, and 3, with the exception of sample DMTP3-4A that was collected at 7 feet bgs and sample DMTP3-4B that was collected at 10 feet bgs in tailings pile 3. Aluminum, barium, cadmium, chromium, copper, iron, lead, molybdenum, nickel, silver, thallium, uranium, and zinc were above background in one or more subsurface samples collected. Concentrations \U)M~SEA~\V~L~\C~MM~N\WP\WPDATA\~~~PORTSW~LDEN-~UUU-~.~OE 5- 1 1 17693-0OS-019Vuly 28.1999;11:09 AM;DRAFT FINAL RI REPORT Tailings Pile 2 DMSS- 14 DMSS-I5 DMSS-16 DMTP2-IA DMTP2- I B DMTP2-2
were below MTCA levels with the following exceptions: cadmium (21 mgkg) and copper (12,400 mgkg) in sample DMTPI-3B and cadmium (147 mgkg) and copper (16,500 mg/kg) in sample DMTP2- 1A. Iron ranged from 26,800 mgkg to 87,500 mgkg. Aluminum (29,700 m&g) was above background (20,900 mgkg) at one location (DMTP2- I A). The subsurface historical data (TP2-4 collected 5 to 10 ft bgs) was compared to the data collected at location DMTP2-2 (4 to 5 feet bgs) during the RI. Generally, the data were within an order of magnitude; however, concentrations of cadmium, lead, and zinc reported in the USBM sample were 20 to 40 times greater than the concentrations detected in the RI samples. Only cadmium levels in the USBM samples were above MTCA levels. Aluminum and iron are considered PCOCs in surface and subsurface tailings as it is above background; a MTCA level is not currently established. Cadmium and copper are considered PCOCs in subsurface tailings only. 5.2.7 Wind-Blown Tailings Five surface soil samples (DMSS-20 through DMSS-24) that contained visual evidence of tailings were collected downwind of RC-2 during the RI and were analyzed for metals only. Sample locations are shown in Figure 5.2-5 and the data are summarized in Table 5.2-5. Barium, copper, iron, lead, molybdenum, silver, and zinc were above background levels in one or more samples collected. However, none of the concentrations were above available MTCA levels. Iron concentrations ranged from 24,100 mgkg to 66,200 mgkg. Iron is identified as a PCOC as it is above background and a MTCA level is not currently established. 5.2.8 Summary Site-specific background values for metal concentrations were statistically calculated from surface soil samples collected Specifically for area background assessment. Metals data collected from Holden Village, the baseball field, maintenance yard, lagoon, tailings piles, and windblown tailings were compared initially to background values. If concentrations 'were above background, the data were then compared to available MTCA A or MTCA B cleanup levels. Metal concentrations above background and MTCA cleanup levels were preliminarily selected as PCOCs and are summarized by location in Table 5.2-6. Exceptions to the PCOC assessment were cations (calcium, magnesium, potassium, and sodium), aluminum and iron. The cations are generally considered nutrient metals and MTCA does not provide , cleanup levels for these metals. Aluminum and iron were considered PCOCs if the results were above background as MTCA does not provide guidance for these metals. Organic analytical data from the surface and subsurface soil samples collected from the lagoon and maintenance yard were compared to MTCA Method A and Method B cleanup levels. Total petroleum hydrocarbon concentrations above MTCA cleanup levels were considered PCOCs in subsurface soil in the maintenance yard in a localized area and in surface/subsurface lagoon soils. Organic PCOCs are also summarized in Table 5.2-6. G:\WPDATAUXI~WORTSWOLDM-Z\RN~.~W 17693405-0 19Uuly 28, 1999; 1 1 :2 1 AM:DRAFT FINAL RI REPORT
- Page 384: DAMES & MOORE A DAMES 6. MOORE GROU
- Page 388 and 389: 1.80 - 1 .. --.- -- 0.9 1.60 - ! Po
- Page 390 and 391: Note: No data available for June 19
- Page 392: : g ; . - . .... . -._. ........ .
- Page 395 and 396: LEGEND ..-.-.-.-.- Freewater surfac
- Page 397: SOURCE: Base map inlbrmation from U
- Page 400: ' D. 7 . 0.8 D. 9 E.0 E. 1 E.2 E.3
- Page 404 and 405: C 0 % iil f 3192 - 3190 - 3188 3186
- Page 406: , -.I p./ ,/' i i .\ i i i -.-. i '
- Page 409: ~ob NO. 1769300~019 Infiltration to
- Page 412 and 413: Overland . Flow Areawest of Site Ov
- Page 414: ' SOURCE: Base map information from
- Page 417 and 418: D. 9 E.0 E.2 E.3 E.4 0.7 SOURCE: Ba
- Page 419 and 420: ...... -.: - - ........... 3790 ,.-
- Page 423 and 424: DRAFT FINAL Remedial Investigation
- Page 425 and 426: (RAOs) section of the Feasibility S
- Page 427 and 428: Also included in WAC 173-201A are p
- Page 429 and 430: MTCA defines the methods and descri
- Page 431 and 432: The historical data for samples col
- Page 433: groundwater was encountered at appr
- Page 437 and 438: sampling rounds, the field filter b
- Page 439 and 440: Department of Ecology samples colle
- Page 441 and 442: data sets where the total value was
- Page 443 and 444: 5.3.1.3 Summary Based on the statis
- Page 445 and 446: adjacent to the Site were not neces
- Page 447 and 448: RC-4 is located downstream of the p
- Page 449 and 450: RC-2 is'located immediately downstr
- Page 451 and 452: In May 1997, copper (21.5 pg5) in t
- Page 453 and 454: Data collected from upstream statio
- Page 455 and 456: of water exiting from the portal. S
- Page 457 and 458: 5.3.4.3 Historical Portal Drainage
- Page 459 and 460: parameters did not indicate seasona
- Page 461 and 462: The portal drainage was sampled at
- Page 463 and 464: and sodium were not evaluated as th
- Page 465 and 466: preliminary report 1997). Sample lo
- Page 467 and 468: time frame. The concentration of ea
- Page 469 and 470: 5.4.2.4 Waste Rock Piies Seep sampl
- Page 471 and 472: Seep data were compared to MTCA gro
- Page 473 and 474: The data for seeps associated with
- Page 475 and 476: in wells TP1- 1A. TPl-2A, TPI-3A, T
- Page 477 and 478: 5.4.2.8 Lucerne Well The well at th
- Page 479 and 480: Ninemile Creek) with a correspondin
- Page 482 and 483: During the mine reclamation activit
were below MTCA levels with the following exceptions: cadmium (21 mgkg) and copper (12,400<br />
mgkg) in sample DMTPI-3B and cadmium (147 mgkg) and copper (16,500 mg/kg) in sample DMTP2-<br />
1A. Iron ranged from 26,800 mgkg to 87,500 mgkg. Aluminum (29,700 m&g) was above background<br />
(20,900 mgkg) at one location (DMTP2- I A).<br />
The subsurface historical data (TP2-4 collected 5 to 10 ft bgs) was compared to the data collected at<br />
location DMTP2-2 (4 to 5 feet bgs) during the RI. Generally, the data were within an order of magnitude;<br />
however, concentrations of cadmium, lead, and zinc reported in the USBM sample were 20 to 40 times<br />
greater than the concentrations detected in the RI samples. Only cadmium levels in the USBM samples<br />
were above MTCA levels.<br />
Aluminum and iron are considered PCOCs in surface and subsurface tailings as it is above background; a<br />
MTCA level is not currently established. Cadmium and copper are considered PCOCs in subsurface<br />
tailings only.<br />
5.2.7 Wind-Blown Tailings<br />
Five surface soil samples (DMSS-20 through DMSS-24) that contained visual evidence of tailings were<br />
collected downwind of RC-2 during the RI and were analyzed for metals only. Sample locations are shown<br />
in Figure 5.2-5 and the data are summarized in Table 5.2-5.<br />
Barium, copper, iron, lead, molybdenum, silver, and zinc were above background levels in one or more<br />
samples collected. However, none of the concentrations were above available MTCA levels. Iron<br />
concentrations ranged from 24,100 mgkg to 66,200 mgkg.<br />
Iron is identified as a PCOC as it is above background and a MTCA level is not currently established.<br />
5.2.8 Summary<br />
Site-specific background values for metal concentrations were statistically calculated from surface soil<br />
samples collected Specifically for area background assessment. Metals data collected from Holden<br />
Village, the baseball field, maintenance yard, lagoon, tailings piles, and windblown tailings were<br />
compared initially to background values. If concentrations 'were above background, the data were then<br />
compared to available MTCA A or MTCA B cleanup levels. Metal concentrations above background and<br />
MTCA cleanup levels were preliminarily selected as PCOCs and are summarized by location in Table<br />
5.2-6. Exceptions to the PCOC assessment were cations (calcium, magnesium, potassium, and sodium),<br />
aluminum and iron. The cations are generally considered nutrient metals and MTCA does not provide ,<br />
cleanup levels for these metals. Aluminum and iron were considered PCOCs if the results were above<br />
background as MTCA does not provide guidance for these metals.<br />
Organic analytical data from the surface and subsurface soil samples collected from the lagoon and<br />
maintenance yard were compared to MTCA Method A and Method B cleanup levels. Total petroleum<br />
hydrocarbon concentrations above MTCA cleanup levels were considered PCOCs in subsurface soil in<br />
the maintenance yard in a localized area and in surface/subsurface lagoon soils. Organic PCOCs are also<br />
summarized in Table 5.2-6.<br />
G:\WPDATAUXI~WORTSWOLDM-Z\RN~.~W<br />
17693405-0 19Uuly 28, <strong>1999</strong>; 1 1 :2 1 AM:DRAFT FINAL RI REPORT