Dames & Moore, 1999 - USDA Forest Service

Dames & Moore, 1999 - USDA Forest Service Dames & Moore, 1999 - USDA Forest Service

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9.2.4.1 Portal Drainage The chemical loading analyses completed during the RI accounted for the overland flow and groundwater loading sources of dissolved metals to Railroad Creek. Conclusions associated with the water quality and chemical loading of component inflow sources including the portal drainage, groundwater, the waste rock piles, mill building, Copper Creek diversion and seeps SP-12 and SP-23 are provided below. Water quality measured at P-1 (main portal)'and P-5 (confluence with Railroad Creek) as overland flow indicates that metals presented in the following table were above regulatory surface and groundwater quality regulatory levels. Surface Water Criteria Groundwater Criteria Locations P- 1 P-5 P-1 , July 1997 Cd, Cu, Pb, Zn, pH C4 Cu, Pb. Zn, pH Cd, Cu, Pb, Zn, SO4, PH These dissolved metals concentrations are influenced by seasonal changes in groundwater flow discharging from the main portal. The loading analysis reflects these differences. MayIJune - The portal drainage discharge flows were as high as approximately 3.5 cubic feet per second (cfs) in ~a~ 1997 and approximately 1.8 cfs in May 1998, and accounts for more than 65 percent of the load of dissolved cadmium, copper, and zinc to the creek during the spring snowmelt period. OctoberISeptember - Discharge flow rates were measured as low as approximately 0.10 cfs. The drainage accounts for less than 1 percent of the copper load, and approximately one-third of the cadmium and zinc load to Railroad Creek. The portal drainage overland flow represents the primary source of dissolved copper, cadmium and zinc to Railroad Creek during spring conditions; however during the fall, the concentrations of these metals is greatly reduced. 9.2.4.2 Groundwater May 1997 C4 Cu, Pb, Zn, pH Cd, Cu, Pb, Zn, pH As, Be, Cb Cu, Pb, Zn, SO,, pH September 1997 Cd, Cu, Zn cd, zn, pH Cd, SO4, TDS The groundwater geochemistry in the east and west portions of the Site is different due to the different source rock types (mine ore deposit versus tailings) and differences in oxygen availability and water flow. Groundwater data from monitoring wells and expressed as seeps and springs were used to evaluate groundwater quality associated with the Site, particularly for the west side of the Site.' Groundwater underlying the Site is not currently being used as drinking water. West Portion of the Site May 1998 Cd, Cu, Pb, Zn, pH Cd, Cu, Pb, Zn, pH Cd, Cu, Fc. Pb, Zn, SO,, TDS, pH The west portion of the site includes the following source areas: underground mine and Honeymoon Heights, portal drainage, west waste rock piles, and the mill building. Groundwater monitoring wells are not present in these areas; therefore, seep water quality was used to evaluate groundwater quality exceedances, source G:\WPDATA\WSWPORTSWO~DM-ZUU\~-O~~~~~ 9-4 17693-00S-019Uuly 28. 1999;10:07 AM;DRAFT FINAL RI REPORT ' I

areas and loading to Railroad Creek. Concentrations of cadmium, copper, and zinc were above the MTCA Method B levels in groundwater in the western portal of the site. Portal Drainage Groundwater infiltrating from the portal drainage overland flow is a component of the unaccounted load (groundwater) of copper, cadmium and zinc to Railroad Creek. Waste Rock Piles Several seeps flow seasonally from near the base of west and east waste rock piles. Two seeps, SP-6 and SP- 15W contain concentrations of cadmium, copper, zinc, beryllium and manganese above the MTCA groundwater levels. Seeps SP-6 and SP-15W account from less than 2 percent of the cadmium, copper and zinc loading to Railroad Creek measured at RC-2. Seep SP- 1 1 contained arsenic and SP- I OE contained iron above groundwater threshold levels. Mill Building One primary seep, SP-7, flows se,asonally from the abandoned mill building and contained cadmium, copper and zinc above MTCA groundwater levels. The seep accounts for less than 2 percent of the cadmium, 4 percent of the copper, and 2 percent of the zinc loading to Railroad Creek as measured at RC-2. Seeps SP-12 and SP-23 Seeps SP-12 and SP-23 are assumed to represent Honeymoon Heights drainage and flow seasonally from the south bank of Railroad Creek to the west of the portal drainage. These seeps contain copper, cadmium, and zinc concentrations above MTCA groundwater levels. The two seeps combined account for approximately 8 percent of the cadmium, 31 percent of the copper, and 7 percent of the zinc loading to Railroad Creek as measured at RC-2. The loading analysis hrther demonstrates that overland flow from the 1500-level main portal is the primary source area contributing dissolved cadmium, copper, and zinc concentrations to Railroad Creek. Source areas including the waste rock piles, mill building, Honeymoon Heights drainage, and groundwater infiltrating from the 1500-level main portal overland flow also contribute metals, primarily copper, cadmium and zinc to Railroad Creek, but represent significantly lower load sources as compared to the overland from the 1500-level main portal. Based on the physical characteristics of the west portion of the site, a high likelihood exists that infiltration of overland flow from the 1500-level main portal contributes to dissolved copper, cadmium and zinc to groundwater in the western portion of the site as well as to groundwater beneath the tailings piles. East Portion of the Site The east portion of the Site includes the tailings piles and Copper Creek diversion. The groundwater underlying the portion of the Site east of the Copper Creek diversion, including tailings piles 1, 2, and 3. Groundwater bellow the tailings piles contains concentrations of arsenic, cadmium, beryllium, copper, lead, manganese, zinc, and iron above MTCA groundwater levels. Cadmium, copper and zinc were not identified in water within the tailings which indicates that these constituents most likely originate from the western portion of the site. O:\WPDATAUX)mPORTSWOLDEN-2WO.doc 9-5 17693-005-019Uuly 28. 1999:10:07 AM:DRAFT FINAL R1 REPORT

9.2.4.1 Portal Drainage<br />

The chemical loading analyses completed during the RI accounted for the overland flow and<br />

groundwater loading sources of dissolved metals to Railroad Creek.<br />

Conclusions associated with the water quality and chemical loading of component inflow<br />

sources including the portal drainage, groundwater, the waste rock piles, mill building, Copper<br />

Creek diversion and seeps SP-12 and SP-23 are provided below.<br />

Water quality measured at P-1 (main portal)'and P-5 (confluence with Railroad Creek) as overland flow<br />

indicates that metals presented in the following table were above regulatory surface and groundwater quality<br />

regulatory levels.<br />

Surface<br />

Water<br />

Criteria<br />

Groundwater<br />

Criteria<br />

Locations<br />

P- 1<br />

P-5<br />

P-1<br />

, July 1997<br />

Cd, Cu, Pb, Zn, pH<br />

C4 Cu, Pb. Zn, pH<br />

Cd, Cu, Pb, Zn, SO4,<br />

PH<br />

These dissolved metals concentrations are influenced by seasonal changes in groundwater flow discharging<br />

from the main portal. The loading analysis reflects these differences.<br />

MayIJune - The portal drainage discharge flows were as high as approximately 3.5 cubic feet<br />

per second (cfs) in ~a~ 1997 and approximately 1.8 cfs in May 1998, and accounts for more<br />

than 65 percent of the load of dissolved cadmium, copper, and zinc to the creek during the<br />

spring snowmelt period.<br />

OctoberISeptember - Discharge flow rates were measured as low as approximately 0.10 cfs.<br />

The drainage accounts for less than 1 percent of the copper load, and approximately one-third<br />

of the cadmium and zinc load to Railroad Creek.<br />

The portal drainage overland flow represents the primary source of dissolved copper, cadmium and zinc to<br />

Railroad Creek during spring conditions; however during the fall, the concentrations of these metals is<br />

greatly reduced.<br />

9.2.4.2 Groundwater<br />

May 1997<br />

C4 Cu, Pb, Zn, pH<br />

Cd, Cu, Pb, Zn, pH<br />

As, Be, Cb Cu, Pb, Zn,<br />

SO,, pH<br />

September 1997<br />

Cd, Cu, Zn<br />

cd, zn, pH<br />

Cd, SO4, TDS<br />

The groundwater geochemistry in the east and west portions of the Site is different due to the different source<br />

rock types (mine ore deposit versus tailings) and differences in oxygen availability and water flow.<br />

Groundwater data from monitoring wells and expressed as seeps and springs were used to evaluate<br />

groundwater quality associated with the Site, particularly for the west side of the Site.' Groundwater<br />

underlying the Site is not currently being used as drinking water.<br />

West Portion of the Site<br />

May 1998<br />

Cd, Cu, Pb, Zn, pH<br />

Cd, Cu, Pb, Zn, pH<br />

Cd, Cu, Fc. Pb, Zn, SO,,<br />

TDS, pH<br />

The west portion of the site includes the following source areas: underground mine and Honeymoon Heights,<br />

portal drainage, west waste rock piles, and the mill building. Groundwater monitoring wells are not present<br />

in these areas; therefore, seep water quality was used to evaluate groundwater quality exceedances, source<br />

G:\WPDATA\WSWPORTSWO~DM-ZUU\~-O~~~~~ 9-4<br />

17693-00S-019Uuly 28. <strong>1999</strong>;10:07 AM;DRAFT FINAL RI REPORT<br />

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I

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