Dames & Moore, 1999 - USDA Forest Service
Dames & Moore, 1999 - USDA Forest Service Dames & Moore, 1999 - USDA Forest Service
H.\Holden\drafl final rirpt\S-7Whra\Tables\7-lg.xls 7/20199 TABLE 7.10 STATISTICAL ANALYSIS AND COMPARISON OF SURFACE WATER DATA FROM RAILROAD CREEK (DATA COLLECTED FROM STATION RCJ DOWNSTREAM 1991 - 1998) HOLDEN MINE RUFS DAMES 6 MOORE JOB NO. 17693405019 Parameters Total Metals [uaR;I Aluminum Arsenic '. Barium Beryllium ' Cadmium Calcium . Chromium . &PW Iron Lead Magnesium Manganese. Mercury ' Molybdenum' Nickel Potassium Selenium Silver Sod~um . Thallium Uranium Zinc Dissolved Metals (uak) Aluminum Arsenic Barium Beryllium Cadmium . Calcium Chromium Copper Iron . Lead. Magnesium' Manganese Mercury Molybdenum Nickel . Potassium . Selenium Silver Sodium .' Thallium Uranium Zinc 8 Analyses 20 14 17 17 20 50 17 53 37 54 50 20 8 8 18 50 9 18 50 8 5 54 23 15 2 1 2 1 24 21 21 24 21 24 21 2 1 8 11 23 21 8 22 21 12 8 24 STATISTICAL CALCULATIONS RCJ Approximate d of Detectloris Maximum Conc. Minimum Conc. Range of RL Distribution Mean Standard Deviation Median UCL (95%) 20 300 37 None Lognormal 1 53 74.11 150 201 11 0.76 0.32 1 Lognormal 0.48 0.13 048 0.54 17 10 5.01 None Neither 6.58 1.43 6,22 10 0 NA NA 0.04 - 1 NA NA NA N A NA 16 0.66 0.09 0.07 -0 11 Lognormal 0.26 0.19 0.16 0.45 50 9950 3800 None Lognormal 6059 1465 5818 6417 2 0.2 0.2 0.12 -5 NA NA N A 0.2 0.2 27 43.5 1.4 0.8 -10.5 Lognormal 8.28 9.05 5 12.85 37 23W) 40 None Lognormal 592 419 430 755 11 11 0.159 0.1 - 16.5 NA NA NA 3 11 50 1490 310 None Lognormal 731 232 695 790 20 26 6.46 None Lognormal 13.05 4.71 12.65 15.19 5 0.002 0.00014 0.1 Lognormal 0.08 0.03 0.0012 ('279) 8 0.68 0.47 None Lognormal , 0.55 0.06 0.55 0.6 12 0.6 0.4 10 Neither 1.98 2.20 0.55 0.6 43 870 140 500 - 533.5 Lognormal 492 174 51 9 547 0 NA NA 0.2- 1 NA NA ? N A NA 3 ' 0.2 0.03 0.04 - 0.2 NA NA NA 0 119 0.2 50 2100 520 None Lognormal 928 329 eEO 1004 1 1 1 0.04 - 1 N A NA NA 1 1 5 44 0 1 140 0.05 0 4 None 0.7 - 10 Lognormal Nether 0.07 28.9 0.02 27.93 006 22 0.1 140 16 90 3.2 6 - 30 Normal 37.77 28.5 40 47.97 8 0.31 0.18 1-2 Lognormal 0.46 0.30 0.31 0.66 21 0 18 16.2 NA 0.72 4.7 NA 0.07 None 0.04 - 4 0.2 - 1 Nether NA Lognormal 7.97 NA 0.28 3.57 NA 0.20 6 4 tJA 0 20 16.2 NA 0.41 18 10100 3830 WOO Lognormal 5981 2176 5600 6982 0 NA NA 0.2 -5 NA NA NA tJA NA 23 26.9 0.39 0.1 Lognormal 7.73 7.27 .2.7 19.62 20 1290 40 100 Lognormal 373 343 240 612 10 21 0.5 1520 0.04 420 02-1 None NA Neither NA 800 NA 344 0 098 6% 0.50 1520 20 26 3 5 0.9 Lognormal 11.96 5.7 9.97 18.49 4 0.00064 O.OMX)7 0.1 Lognormal 0.25 0.03 0.C25 (3954) 11 10 0.64 0.6 0.2 0.2 None 0.2 .10 Normal NA 0.48 NA 0.11 NA 0 il !; 1 0.54 0.6 11 0 930 N A 200 NA 500 0.2 - 1 Lognormal NA 417 NA 246 NA 250 t iA 531 NA 2 0.09 0.08 001 -02 NA NA NA 0 S85 0.09 21 0 3 1750 NA 0.07 400 NA 0.01 None 0.04 - 1 0.04 - 0.1 Lognormal NA N A . 935 NA NA 399 NA NA &XI t!A 0 57 1117 NA 0.07 23 98 13 2 Lwnormal 42 6 26.7 :;8 68.25 SWMical Notes: (Statistical calculations were performed using Washington Department of Ecology's MTCAStat Excel V 5 Macro (Module 2.1). downloaded from their web site.) Madmum and minimum concentrations are based on detected dues only. Range of reporting limits (RL) are based on results reported as not deteded. Distribution is determ~ned based on the MTCA stat program by analyzing the data through the W-TesP or 'D'Agostino's test". Where data is not lognormally nor normally distributed. the distribution is noted as *Neither. When approximate distribution is reported as-neithef, the madmum concentration is reported as the 95% UCL and is presented in BOLD font. ! If UCL is repofled in brackets (UCL value). this indicates that the calculated resun from MTCAStal was reported to be unusually high. Therefore, the calculated 95% UCL is suspect. The mean is an arithmetii mean if data are normally distributed or if distribution is indicated as 'Neithef. The reported m n for lognormally distributed data is a lognormal mean. Statistical analysis was not performed on data sets where 50% or greater of the results were reported as not detected. Otly m;?dmum and minimum concentrations are reported, if applicable. For these data sets. a calculated median is based an detected mlues only. Page 4 of 4 TABLE 7.10 STATISTICAL ANALYSIS 6 COMPARISON OF WATER QUALlTY DATA (DOWNSTREAM) FROM RCJ
TABLE 7.14 STATISTICAL ANALYSIS AND COMPARISON OF CHEMICAL DATA FROM GROUNDWATER SEEPAGE HOUJEN MINE RllFS DAAmS & MOORE JOB NO. 11693405019 Data Notes: J -Estimated Value. U - Parameter was analyzed for, but not detected above the reporting limit shown. UJ - Parameter was analyzed for. but nol detected. Detection limit is an estimated value. .: . .+ . :.:.:
- Page 933 and 934: Little Brown Bat The little brown b
- Page 935 and 936: Since none of the UCL concentration
- Page 937 and 938: , Hazard quotients for osprey consu
- Page 939 and 940: appropriate metric for protection o
- Page 941 and 942: Table 7.2.4-1 1A shows that red-tai
- Page 943 and 944: 7.2.5 SOURCES OF UNCERTAINTY Limita
- Page 945 and 946: laboratory studies to field exposur
- Page 947 and 948: I I tailings piles difficult. Likew
- Page 949 and 950: other mine sites where plants &re s
- Page 951 and 952: TABLE 7.0-1 . KEY OF SITE FEATURES
- Page 953 and 954: TABLE 7.0-1 KEY OF SITE FEATURES 8
- Page 955 and 956: TABLE 7.0-1 KEY OF SITE FEATURES 8
- Page 957 and 958: ' TABLE 7.18 STATISTICAL ANALYSJS A
- Page 959 and 960: TABLE 7.14 STAnSTlCAL EVALUATION AN
- Page 961 and 962: TABLE 7.14 STATISTICAL EVALUATION A
- Page 963 and 964: TABLE 7.14 STATISTICAL EVALUATION A
- Page 965 and 966: TABLE 7.14 COMPARISON OF SEDIMENTAR
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- Page 969 and 970: TABLE 7.14 SURFACE WATER AREA BACKG
- Page 971 and 972: H.Wolden\drafl final rirpt\S-7WhraU
- Page 973 and 974: TABLE 7.1-E SURFACE WATER AREA BACK
- Page 975: TABLE T.1-F STATISTICAL ANALYSIS AN
- Page 978 and 979: TABLE 7.1 -F STATISTICAL ANALYSIS A
- Page 980: H.Wolden\dratl hnal rirpnsrpns7Whra
- Page 983: TABLE 7.10 STATISTICAL ANALYSIS AND
- Page 987 and 988: TABLE 7.144 STATISTICAL ANALYSIS AN
- Page 989 and 990: TABLE 7.14 STATISTICAL ANALYSIS AND
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- Page 993 and 994: Xluo sanlm pawlap uo paseq aJe suo!
- Page 995 and 996: TABLE 7.14 STAllSllCM ANALYSIS AND
- Page 997 and 998: TABLE 7.1 J MSTORKM AJR MONITORING
- Page 999 and 1000: TABLE 7.1-1 AREA AND NATURAL BACKGR
- Page 1002 and 1003: TABLE 7.1-4 TOXICITY CRITERIA AND B
- Page 1004 and 1005: TABLE 7.14 HUMAN HEALTH SCREENING O
- Page 1006 and 1007: TABLE 7.14 HUMAN HEALTH SCREENING O
- Page 1008 and 1009: TABLE 7.1-10 HUMAN HEALTH SCREENING
- Page 1011 and 1012: TABLE 7.1-13 HUMAN HEALTH SCREENING
- Page 1013 and 1014: TABLE 7.1-15 HUMN HEALTH SCREENING
- Page 1015 and 1016: TABLE 7.1-17 HUMAN HEALTH SCREENING
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- Page 1025 and 1026: TABLE 7.1-27 HUMAN HEALTH SCREENING
- Page 1027 and 1028: TABLE 7.1-29 HUMANHEALTHSCREENINGOF
- Page 1029: TABLE 7.1-31 HUMAN HEALTH SCREENING
- Page 1032 and 1033: TABLE 7.1-34 HUMAN HEALTH SCREENING
H.\Holden\drafl final rirpt\S-7Whra\Tables\7-lg.xls<br />
7/20199<br />
TABLE 7.10<br />
STATISTICAL ANALYSIS AND COMPARISON OF SURFACE WATER DATA FROM RAILROAD CREEK<br />
(DATA COLLECTED FROM STATION RCJ DOWNSTREAM 1991 - 1998)<br />
HOLDEN MINE RUFS<br />
DAMES 6 MOORE JOB NO. 17693405019<br />
Parameters<br />
Total Metals [uaR;I<br />
Aluminum<br />
Arsenic '.<br />
Barium<br />
Beryllium '<br />
Cadmium<br />
Calcium .<br />
Chromium .<br />
&PW<br />
Iron<br />
Lead<br />
Magnesium<br />
Manganese.<br />
Mercury '<br />
Molybdenum'<br />
Nickel<br />
Potassium<br />
Selenium<br />
Silver<br />
Sod~um .<br />
Thallium<br />
Uranium<br />
Zinc<br />
Dissolved Metals (uak)<br />
Aluminum<br />
Arsenic<br />
Barium<br />
Beryllium<br />
Cadmium .<br />
Calcium<br />
Chromium<br />
Copper<br />
Iron .<br />
Lead.<br />
Magnesium'<br />
Manganese<br />
Mercury<br />
Molybdenum<br />
Nickel .<br />
Potassium .<br />
Selenium<br />
Silver<br />
Sodium .'<br />
Thallium<br />
Uranium<br />
Zinc<br />
8 Analyses<br />
20<br />
14<br />
17<br />
17<br />
20<br />
50<br />
17<br />
53<br />
37<br />
54<br />
50<br />
20<br />
8<br />
8<br />
18<br />
50<br />
9<br />
18<br />
50<br />
8<br />
5<br />
54<br />
23<br />
15<br />
2 1<br />
2 1<br />
24<br />
21<br />
21<br />
24<br />
21<br />
24<br />
21<br />
2 1<br />
8<br />
11<br />
23<br />
21<br />
8<br />
22<br />
21<br />
12<br />
8<br />
24<br />
STATISTICAL CALCULATIONS RCJ<br />
Approximate<br />
d of Detectloris Maximum Conc. Minimum Conc. Range of RL Distribution Mean Standard Deviation Median<br />
UCL (95%)<br />
20 300 37 None Lognormal 1 53 74.11 150 201<br />
11 0.76 0.32 1 Lognormal 0.48 0.13 048 0.54<br />
17 10 5.01 None Neither 6.58 1.43 6,22 10<br />
0 NA NA 0.04 - 1 NA NA NA N A NA<br />
16 0.66 0.09 0.07 -0 11 Lognormal 0.26 0.19 0.16 0.45<br />
50 9950 3800 None Lognormal 6059 1465 5818 6417<br />
2 0.2 0.2 0.12 -5 NA NA N A 0.2 0.2<br />
27 43.5 1.4 0.8 -10.5 Lognormal 8.28 9.05 5 12.85<br />
37 23W) 40 None Lognormal 592 419 430 755<br />
11 11 0.159 0.1 - 16.5 NA NA NA 3 11<br />
50 1490 310 None Lognormal 731 232 695 790<br />
20 26 6.46 None Lognormal 13.05 4.71 12.65 15.19<br />
5 0.002 0.00014 0.1 Lognormal 0.08 0.03 0.0012 ('279)<br />
8 0.68 0.47 None Lognormal , 0.55 0.06 0.55 0.6<br />
12 0.6 0.4 10 Neither 1.98 2.20 0.55 0.6<br />
43 870 140 500 - 533.5 Lognormal 492 174 51 9 547<br />
0 NA NA 0.2- 1 NA NA ? N A NA<br />
3 ' 0.2 0.03 0.04 - 0.2 NA NA NA 0 119 0.2<br />
50 2100 520 None Lognormal 928 329 eEO 1004<br />
1 1 1 0.04 - 1 N A NA NA 1 1<br />
5<br />
44<br />
0 1<br />
140<br />
0.05<br />
0 4<br />
None<br />
0.7 - 10<br />
Lognormal<br />
Nether<br />
0.07<br />
28.9<br />
0.02<br />
27.93<br />
006<br />
22<br />
0.1<br />
140<br />
16 90 3.2 6 - 30 Normal 37.77 28.5 40 47.97<br />
8 0.31 0.18 1-2 Lognormal 0.46 0.30 0.31 0.66<br />
21<br />
0<br />
18<br />
16.2<br />
NA<br />
0.72<br />
4.7<br />
NA<br />
0.07<br />
None<br />
0.04 - 4<br />
0.2 - 1<br />
Nether<br />
NA<br />
Lognormal<br />
7.97<br />
NA<br />
0.28<br />
3.57<br />
NA<br />
0.20<br />
6 4<br />
tJA<br />
0 20<br />
16.2<br />
NA<br />
0.41<br />
18 10100 3830 WOO Lognormal 5981 2176 5600 6982<br />
0 NA NA 0.2 -5 NA NA NA tJA NA<br />
23 26.9 0.39 0.1 Lognormal 7.73 7.27 .2.7 19.62<br />
20 1290 40 100 Lognormal<br />
373 343 240 612<br />
10<br />
21<br />
0.5<br />
1520<br />
0.04<br />
420<br />
02-1<br />
None<br />
NA<br />
Neither<br />
NA<br />
800<br />
NA<br />
344<br />
0 098<br />
6%<br />
0.50<br />
1520<br />
20 26 3 5 0.9 Lognormal 11.96 5.7 9.97 18.49<br />
4 0.00064 O.OMX)7 0.1 Lognormal 0.25 0.03 0.C25 (3954)<br />
11<br />
10<br />
0.64<br />
0.6<br />
0.2<br />
0.2<br />
None<br />
0.2 .10<br />
Normal<br />
NA<br />
0.48<br />
NA<br />
0.11<br />
NA<br />
0 il<br />
!; 1<br />
0.54<br />
0.6<br />
11<br />
0<br />
930<br />
N A<br />
200<br />
NA<br />
500<br />
0.2 - 1<br />
Lognormal<br />
NA<br />
417<br />
NA<br />
246<br />
NA<br />
250<br />
t iA<br />
531<br />
NA<br />
2 0.09 0.08 001 -02 NA NA NA 0 S85 0.09<br />
21<br />
0<br />
3<br />
1750<br />
NA<br />
0.07<br />
400<br />
NA<br />
0.01<br />
None<br />
0.04 - 1<br />
0.04 - 0.1<br />
Lognormal<br />
NA<br />
N A .<br />
935<br />
NA<br />
NA<br />
399<br />
NA<br />
NA<br />
&XI<br />
t!A<br />
0 57<br />
1117<br />
NA<br />
0.07<br />
23 98 13 2 Lwnormal 42 6 26.7 :;8 68.25<br />
SWMical Notes: (Statistical calculations were performed using Washington Department of Ecology's MTCAStat Excel V 5 Macro (Module 2.1). downloaded from their web site.)<br />
Madmum and minimum concentrations are based on detected dues only.<br />
Range of reporting limits (RL) are based on results reported as not deteded.<br />
Distribution is determ~ned based on the MTCA stat program by analyzing the data through the W-TesP or 'D'Agostino's test". Where data is not lognormally nor normally distributed. the distribution is noted as *Neither.<br />
When approximate distribution is reported as-neithef, the madmum concentration is reported as the 95% UCL and is presented in BOLD font. !<br />
If UCL is repofled in brackets (UCL value). this indicates that the calculated resun from MTCAStal was reported to be unusually high. Therefore, the calculated 95% UCL is suspect.<br />
The mean is an arithmetii mean if data are normally distributed or if distribution is indicated as 'Neithef. The reported m n for lognormally distributed data is a lognormal mean.<br />
Statistical analysis was not performed on data sets where 50% or greater of the results were reported as not detected. Otly m;?dmum and minimum concentrations are reported, if applicable.<br />
For these data sets. a calculated median is based an detected mlues only.<br />
Page 4 of 4<br />
TABLE 7.10<br />
STATISTICAL ANALYSIS 6 COMPARISON OF<br />
WATER QUALlTY DATA (DOWNSTREAM)<br />
FROM RCJ