Dames & Moore, 1999 - USDA Forest Service
Dames & Moore, 1999 - USDA Forest Service Dames & Moore, 1999 - USDA Forest Service
3 during the 1997 investigation indicate that water quality criteria for acute toxicity were exceeded during April (zinc) and May (copper and zinc). The relatively lower habitat quality and the presence of dissolved metals (primarily copper and zinc) at RC-3 may contribute to the reduced trout population as compared to CC-I; however, trout populations at RC-3 were greater than the upstream reference reach (RC-6/RC- 1) within Railroad Creek. The Company Creek reference station is not comparable to the RC-3 station on Railroad Creek for a number of reasons. The most significant being the proximity of the creek to the Stehekin River. which is a salmon spawning ground. In contrast, RC-3 is located immediately upstream of Lake Chelan which is a deep water body and not a fish spawning habitat. The stream substrate for Company Creek is also relatively high gradient with numerous large cobbles and boulders which provide excellent trout habitat, and is dissimilar from the RC-3 station. Consequently, the aquatic data collected at the Company Creek station are not considered directly comparable to those of the RC-3 station. Precipitation Affects on Benthic Macroinvertebrates It appears that periods of precipitation have an affect on the benthic macroinvertebrates results. The aquatic stations were sampled starting upstream at RC-6 and proceeded downstream to RC-3. After aquatic sampling at RC-10 was conducted, and before sampling at RC-3 was initiated, a storm event occurred which resulted in precipitation and increased stream flows in Railroad Creek. Afier the sampling was completed at RC-3, a series of additional benthic macroinvertebrate samples was collected at RC-6 within 24 hours of the precipitation event. The influence of precipitation affects on the benthic macroinvertebrates illustrates the variability and lack of precision for the benthic macroinvertebrate population estimating method employed. which is considered the scientific standard. Therefore, the data reflect the natural variability in the benthic macroinvertebrate communities of the Stehekin River drainage. 8.2.6.2 Terrestrial Biota and Wildlife The RI included an assessment of the terrestrial biota in the area of the Site. For wildlife purposes, the Site and surrounding area was regarded as five sub-areas based on cover type. These sub-areas consisted of the mine tailings, the north-facing slopes and old mine surface workings, the south-facing slopes, the riparian area upstream of the tailings, the riparian area downstream of the tailings, and the tailings themselves. The vegetation consisted of north-aspect coniferous forest in the area south of the mill and tailings piles, south-aspect coniferous forest and open areas to the north of Holden Village, upstream riparian habitat west of the baseball field and campground, downstream riparian east of tailings pile 3, and the tailings piles with sparse planted and volunteer coniferous trees, deciduous trees and shrubs, and various grasses, forbs, and sedges. Terrestrial wildlife observed on the Site was generally consistent with the surrounding area. All of the species were either observed andlor assumed to utilize the tailings piles at times. Potentially federal- and state-listed and candidate species potentially occurring in the vicinity of the Site include the Westslope cutthroat trout which is listed as a Species of Federal concern. This species of cutthroat trout is found in Railroad Creek. However, the Westslope cutthroat has not been listed as threatened and/or endangered. The peregrine falcon, bald eagle, northern spotted owl, gray wolf, grizzly bear, lynx are listed as Special Status Species and have been observed in the Railroad Creek watershed. \U~M-SEAI\VOLI\COMMOMWP\WDATA\W)5\REPORTSWOLDEN-2W\8-O doc 8-25 DAMES 17693-005-OI9Uuly 28. 1999:10:24 Ah4;DRAFT FMAL Rl REPORT & MOORE
8.3 SITE CONTAMINANT CHARACTERIZATION 8.3.1 Introduction Site surface and subsurface soil, surface water, groundwater, seeps, sediment, and flocculent were analyzed principally for organic compounds as outlined in the Draft Work Plan, and Sampling and Analysis Plans. Additional select areas and matrices were analyzed for organic compounds. This section summarizes the designation of potential compounds of concern (PCOC). The designation of a matrix as a PCOC indicates that it exceeds a regulatory standard for screening purposes only, but does not necessarily signify that the compound presents risk to human health and the environment. A complete discussion of the results of each sample matrix was previously provided in Section 5.0, and the results of the human health and ecological risk assessment are presented in Section 7.0. 8.3.2 Soil 8.3.2.1 Mine Support Area Maintenance Yard Surface Soils Arsenic, cadmium, copper, iron, lead, and total petroleum hydrocarbons were identified in five soil samples as PCOCs. Subsurface Soils Total petroleum hydrocarbons were identified in two subsurface samples as PCOCs. Lagoon Surface Soils Beryllium, iron, and total petroleum hydrocarbons were identified as PCOCs in one soil sample collected in the lagoon. Subsurface Soils Cadmium, copper, lead, iron, and total petroleum hydrocarbons were identified as PCOCs in ten subsurface soil samples collected in the lagoon. 8.3.2.2 Tailings Piles Surface Soils Iron was identified as a PCOC in nine surface soil samples collected from the tailings piles. \U~M~SEAI\V~LI\C~MM~MWP\WDATA\~~S\REP~RTSW~LDEN-~UU\~-~.~OE 8-26 17693405-019Uuly 28. 1999;10:24 AMDRAFT FINAL RI REPORT .
- Page 1102 and 1103: TABLE 7.2.3-16 DOSES TO RED-TAILED
- Page 1104 and 1105: TABLE 7.2.3-18 DOSES TO BAT HOLDEN
- Page 1106 and 1107: TABLE 7.2.4-2a HAZARD QUOTIENTS FOR
- Page 1108 and 1109: TABLE 7.2.4-2D a HAZARD QUOTIENTS F
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- Page 1120 and 1121: TABLE 7.2.4-14 HAZARD QUOTIENTS FOR
- Page 1122 and 1123: Figure 7.0-2 HDA~VE~~LMOORE RAILROA
- Page 1124 and 1125: I SOURCE RELEASE EXPOSURE . MECHANI
- Page 1126 and 1127: MEDIA FIGURE 7.1-3 FLOW CHART ILLUS
- Page 1128 and 1129: I I 8.1 INTRODUCTION 8.0 DISCUSSION
- Page 1130 and 1131: 8.2.2 Geology 8.2.2.1 Railroad Cree
- Page 1132 and 1133: The bedrock in the mine has been ma
- Page 1134 and 1135: Railroad Creek and Copper Creek. Th
- Page 1136 and 1137: where Railroad Creek flows directly
- Page 1138 and 1139: A 500-year event was not analyzed,
- Page 1140 and 1141: i flow associated with two seeps ad
- Page 1142 and 1143: Western Portion of Site Undermound
- Page 1144 and 1145: native soil is of higher permeabili
- Page 1146 and 1147: Macroinvertebrate sampling included
- Page 1148 and 1149: Above Tenmile Creek Confluence (RC-
- Page 1150 and 1151: Reference Reaches - Stehekin River
- Page 1154 and 1155: Subsurface Soils Cadmium, copper, a
- Page 1156 and 1157: Station' RC-4 RC-7 RC-2 RC-5 RC-10
- Page 1158 and 1159: 8.3.4.1 Western Portion of Site Dur
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- Page 1162 and 1163: I . During The water from the west
- Page 1164 and 1165: a The Copper Creek diversion accoun
- Page 1166 and 1167: 8.5.2.1 Trout An intem~ediate poten
- Page 1168 and 1169: i SOURCE: Walten et al., 1992 USGS
- Page 1170 and 1171: SOURCE: Base map information from U
- Page 1172 and 1173: NOTE: This cross section is general
- Page 1174 and 1175: D.7 D. 8 D. 9 E.0 SOURCE: Base map
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- Page 1178 and 1179: 9.2.4.1 Portal Drainage The chemica
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- Page 1186 and 1187: SOURCE: USGS Topographic Map, State
- Page 1189 and 1190: SOURCE: Base map information from U
- Page 1191 and 1192: 10.0 PROJECT SCHEDULE The, schedule
- Page 1193 and 1194: I ATSDR. 1990. Toxicological profil
- Page 1195 and 1196: Dames & Moore, 1998b. Phase I11 Rem
- Page 1197 and 1198: Ebbutt,%F. 1956. Letter Report to V
- Page 1199 and 1200: ';i 1 Products, Shale-oils and Soot
- Page 1201 and 1202: Leland, H.V. and J.L. Carter. 1984.
3 during the 1997 investigation indicate that water quality criteria for acute toxicity were exceeded during<br />
April (zinc) and May (copper and zinc). The relatively lower habitat quality and the presence of<br />
dissolved metals (primarily copper and zinc) at RC-3 may contribute to the reduced trout population as<br />
compared to CC-I; however, trout populations at RC-3 were greater than the upstream reference reach<br />
(RC-6/RC- 1) within Railroad Creek.<br />
The Company Creek reference station is not comparable to the RC-3 station on Railroad Creek for a number<br />
of reasons. The most significant being the proximity of the creek to the Stehekin River. which is a salmon<br />
spawning ground. In contrast, RC-3 is located immediately upstream of Lake Chelan which is a deep water<br />
body and not a fish spawning habitat. The stream substrate for Company Creek is also relatively high<br />
gradient with numerous large cobbles and boulders which provide excellent trout habitat, and is dissimilar<br />
from the RC-3 station. Consequently, the aquatic data collected at the Company Creek station are not<br />
considered directly comparable to those of the RC-3 station.<br />
Precipitation Affects on Benthic Macroinvertebrates<br />
It appears that periods of precipitation have an affect on the benthic macroinvertebrates results. The aquatic<br />
stations were sampled starting upstream at RC-6 and proceeded downstream to RC-3. After aquatic<br />
sampling at RC-10 was conducted, and before sampling at RC-3 was initiated, a storm event occurred which<br />
resulted in precipitation and increased stream flows in Railroad Creek. Afier the sampling was completed at<br />
RC-3, a series of additional benthic macroinvertebrate samples was collected at RC-6 within 24 hours of the<br />
precipitation event. The influence of precipitation affects on the benthic macroinvertebrates illustrates the<br />
variability and lack of precision for the benthic macroinvertebrate population estimating method employed.<br />
which is considered the scientific standard. Therefore, the data reflect the natural variability in the benthic<br />
macroinvertebrate communities of the Stehekin River drainage.<br />
8.2.6.2 Terrestrial Biota and Wildlife<br />
The RI included an assessment of the terrestrial biota in the area of the Site. For wildlife purposes, the Site<br />
and surrounding area was regarded as five sub-areas based on cover type. These sub-areas consisted of the<br />
mine tailings, the north-facing slopes and old mine surface workings, the south-facing slopes, the riparian<br />
area upstream of the tailings, the riparian area downstream of the tailings, and the tailings themselves.<br />
The vegetation consisted of north-aspect coniferous forest in the area south of the mill and tailings piles,<br />
south-aspect coniferous forest and open areas to the north of Holden Village, upstream riparian habitat west<br />
of the baseball field and campground, downstream riparian east of tailings pile 3, and the tailings piles with<br />
sparse planted and volunteer coniferous trees, deciduous trees and shrubs, and various grasses, forbs, and<br />
sedges.<br />
Terrestrial wildlife observed on the Site was generally consistent with the surrounding area. All of the<br />
species were either observed andlor assumed to utilize the tailings piles at times.<br />
Potentially federal- and state-listed and candidate species potentially occurring in the vicinity of the Site<br />
include the Westslope cutthroat trout which is listed as a Species of Federal concern. This species of<br />
cutthroat trout is found in Railroad Creek. However, the Westslope cutthroat has not been listed as<br />
threatened and/or endangered. The peregrine falcon, bald eagle, northern spotted owl, gray wolf, grizzly<br />
bear, lynx are listed as Special Status Species and have been observed in the Railroad Creek watershed.<br />
\U~M-SEAI\VOLI\COMMOMWP\WDATA\W)5\REPORTSWOLDEN-2W\8-O doc 8-25 DAMES<br />
17693-005-OI9Uuly 28. <strong>1999</strong>:10:24 Ah4;DRAFT FMAL Rl REPORT<br />
& MOORE