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Lead Contamination in the Big River due to Historical Mining Activities -Channel Sediment -Floodplain Soils -Focus on Jefferson County Bob Pavlowsky Department of Geography, Geology, and Planning Ozarks Environmental and Water Resources Institute Missouri State University

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Lead Contamination in the Big River

due to Historical Mining Activities

-Channel Sediment

-Floodplain Soils

-Focus on Jefferson County

Bob Pavlowsky Department of Geography, Geology, and Planning

Ozarks Environmental and Water Resources Institute

Missouri State University

Big River Watershed (2,400 km2)

Historical Land UseCrops, Population, & Livestock

0

20

40

60

80

100

120

140

1840 1860 1880 1900 1920 1940 1960 1980 2000

Po

pu

lati

on

De

nsi

ty (

Pe

rso

ns/

km2

)

Jefferson County

St. Francois County

Washington County

0

5,000

10,000

15,000

20,000

25,000

30,000

35,000

1840 1860 1880 1900 1920 1940 1960 1980 2000

Co

un

t

Dairy Cattle

Other Cattle

Hogs

Livestock

0

5,000

10,000

15,000

20,000

25,000

30,000

35,000

40,000

45,000

50,000

0

200,000

400,000

600,000

800,000

1,000,000

1,200,000

1,400,000

1840 1860 1880 1900 1920 1940 1960 1980 2000

Ton

s P

rod

uce

d

Bu

she

ls P

rod

uce

d

Wheat (Bushels) Corn (Bushels) Dry Hay (Tons)

Peak land use disturbance

1880 to 1920

Large-scale mining from 1900 to 1972; peak in 1942National Mill

(1924)

Bonne Terre

Chat Pile

Leadwood

1937

Big River

Tailings Piles: Ca and Pb Size FractionationChat: fine gravel Tailings: sand Slimes: ultra-fines

21-25% Ca= Dolomite host rock High Pb in all sizes

Desloge Pile in 2010: Stabilized and Contained

Problem: Mining Sediment in the Big River

• Mine waste inputs to the natural river system

– Chat and Tailings deposited in channel and on floodplain

– Reworking by erosion and weathering (long-term effects???)

• 3 types of sediment concern (size and mill process)

– Chat- 4 to 16 mm or “fine gravel”

• Dry separation (gravity methods)

– Tailings- 0.06 to 0.2 mm or “fine sand”

• Wet separation (Shaking tables or flotation)

– Slimes- <32 um or “fine silt”

• Powdered rock

• Too fine for separation or efficient recovery

Concerns over soil

contamination due to

mining and other

industrial sources

Residential soil

problems in Jefferson

County

Red dots show

concentrations over

1,200 ppm Pb.

MC Barnhart

MC Barnhart

MC Barnhart

Leptodea leptodon (scaleshell) Lampsilis abrupta (pink mucket)

Cumberlandia monodon (spectaclecase)

Endangered Mussels are

threatened by:

1) Sediment-Pb toxicity

2) Channel instability

3) Sedimentation

Washington County Lead District

OBJECTIVES

1) What are Pb concentrations within historical

channel and floodplain deposits?

2) What is the longitudinal distribution of storage? How

much is still in the river?

3) What will happen in the future? Contamination or

Recovery?

Management plans (control and clean-up measures)

Valley Cross-section

What did we do?

171

172

173

174

175

176

177

178

179

0102030405060

Ele

vati

on

(m

)

Distance across channel looking downstream (m)

Site 6 - T8

172

172.5

173

173.5

174

174.5

175

0 100 200 300 400 500 600

Ele

vati

on

(m

)

Distance (m)

Longitudinal Profile - Site 6

T2 T3 T4 T5 T6 T7 T9T8T1

Sinuosity = 1.15Pool Slope = .003

Longitudinal Survey

Cross Section Survey

Blackwell At CC Bridge (R-km 115)

Blue- channel bottom and banks

Red- probe depth transect

Green-maximum probe depth

GlideGlide

Channel Sample units

High Bar Glide

Big River above Flat River at hwy 67

Thickness of Bed and Bar DepositsTile Probe Refusal

Floodplain Sampling

Floodplain Cut-banks

High FP above Flat-6m Low FP at Cherokee Landing-4m

---contact---

---contact---

0

500

1,000

1,500

2,000

2,500

0 25 50 75 100 125 150 175 200

Pb

pp

m

River Kilometer above the Meramec River

FWS 07 riffle slackwater

bulk

FWS 08 riffle slackwater bulk

MSU 09 bar <2mm

MSU 09 glide <2mm

MSU 09 Geo-mean

Probable Effect

128 ppm Pb

Big River Channel sed-PbContamination

171- Eaton Ck155- Flat R Ck116- Mill Ck

99- Min Fork34- Belews Ck

CHANNEL RESULTS

Selective transport of finer sediment Longitudinal size sorting of mining sediment occurs over channel distances of +/- 30 km

0

2

4

6

8

10

12

14

16

18

20

0 25 50 75 100 125 150 175 200

Ca

%

River Kilometer

B- Percent Calcium

<250 mm

1-2 mm

4-8 mm

“Pure” dolomite = 21.7% Ca & calcite = 40.1% Ca

Fines Sand Chat

um

Fine gravel or CHAT grain counting

Chat Grain Counts

0

20

40

60

80

100

0 25 50 75 100 125 150 175 200

Pe

rce

nt

of

Tota

l G

rain

s

River Kilometer

Chat Grain Counts (4-8 mm fraction)

Chips Trend

Natural Trend

Chips-Trib

Natural-Trib

Flat R Ck

Natural (chert/feldspars)=

200-600 ppm Pb

Dolomite Chips=

800-5,400 ppm Pb

Contrasting size-Pb relationship between

proximal and distal channel segments(last mine drains to the Big River at R-km 135)

0

1000

2000

3000

4000

5000

6000

0 25 50 75 100 125 150 175 200

Pb

pp

m

River Kilometer

E- ppm Lead

<250 mm

1-2 mm

4-8 mm Fines

Fines

um

Unit Channel Storage (sand and fine gravel)m3/100 m

Big River above Mineral Fork: 2,566 +/- 25% (2s) m3/100 m

--TRIBUTARIES--

up---------- MAINSTEM ----------------------------------------------- down

D

D

D

bD

b

D = us of dam

b = thalweg breach

Contaminated

---Old Topsoil contact---

Uncontaminated

FLOODPLAIN RESULTS

Washington State Park Valley Transect

Washington State park valley Transect

162

164

166

168

170

172

174

176

0 50 100 150 200 250 300

Ele

vati

on

(m

ab

ove

msl

)

Valley Distance (m)

>400 ppm Pb

Max Pb

Gravel

Refusal

Surface

0

5,000

10,000

15,000

1 2 3 4 5 6 7 8

Pb

(p

pm

)

Core #

Surface Pb

Max Pb

Morse Mill Park on the Big RiverPb profiles at R-km 50

112

113

114

115

116

117

118

119

120

121

122

123

124

125

126

0 50 100 150 200 250 300 350 400 450 500 550

Ele

vati

on

(m

)

Distance (m)

Core 8 Core 9 Core 10

Core 15 Core 14

Core 13

Core 16

0

50

100

150

200

250

300

350

400

0 2,000 4,000 6,000

Dep

th (

cm)

Pb (ppm)

T-2 Core 8 - Morse Mill

0

50

100

150

200

250

300

350

400

0 2,000 4,000 6,000

Dep

th (

cm)

Pb (ppm)

T-2 Core 9 - Morse Mill

0

50

100

150

200

250

300

350

400

0 2,000 4,000 6,000

Dep

th (

cm)

Pb (ppm)

T-2 Core 10 - Morse Mill

0

50

100

150

200

250

300

350

400

0 2,000 4,000 6,000D

epth

(cm

)Pb (ppm)

T-2 Core 15 - Morse Mill

0

50

100

150

200

250

300

350

400

0 2,000 4,000 6,000

Dep

th (

cm)

Pb (ppm)

T-2 Core 14 - Morse Mill

0

50

100

150

200

250

300

350

400

0 2,000 4,000 6,000

Dep

th (

cm)

Pb (ppm)

T-2 Core 13 - Morse Mill

0

50

100

150

200

250

300

350

400

0 100 200 300 400 500

Dep

th (

cm)

Pb (ppm)

T-2 Core 16 - Morse Mill

High Pb concentrations extend far downstream

Mining Area

St. Francois Co.

R-km 171 to 135

Recent FP surface deposits decrease in Pb

Concentration below mining areas

0

500

1,000

1,500

2,000

2,500

3,000

0.0 5.0 10.0 15.0 20.0 25.0

Pb

Con

cen

trati

on

(p

pm

)

River km above Meramec River (0=mouth, 24.2= Byrnesville Gage)

Lower Big River Sediment Contamination

Bank Sample

Bar Sample

Bed Sample

Terrestrial PEC =400 ppm

Aquatic PEC =128 ppm

Floodplain Storage PotentialAreas in km2 by county

(Source: USDS Soil Survey and aerial photographs)

Haymond / Wilbur Kaintuck

Jefferson Co. (Lower) St. Francois Co. (middle)

Total Segment

Storage

Unit Channel

Storage

decreases

downstream

Unit floodplain storage increases downstream

Total by segment

Storage by unit length

St. Francois Co. (middle) Jefferson Co. (Lower)

1) Total Pb Storage

in Alluvial Deposits

= 230,000 Mg

2) St. Francois Co.

Floodplain 26.7%

(Channel 1.1% )

3) Jefferson Co.

Floodplain 71.6%

(Channel 0.6% )

4) About 1/3 of

tailings Pb

remaining in the

District is stored in

alluvial deposits of

the Big River.

Lower Big River

•Over the past 70 years, the

lower Big River has been

relatively stable, but disturbance

reaches represent ~32% of study

reach

R-km

Bank Erosion is a source of present day Pb contamination

Floodplain Mapping Using USDA Soil Series

Contaminated Deposits

Highest Pb Concentrations

Gold bars show higher

elevation terrace deposits that

are not contaminated.

Moderate & thin

Moderate &

thick

Screening-level

Indicator of

Floodplain Soil Risk

USDA-NRCS

Soil Survey

Floodplain Contamination

•Terrestrial Contamination

>400 ppm

Conclusions

Location Sediment Volume (%)

County In-Channel Floodplain

St. Francois 1.5% 19.7%

Jefferson 2.6% 76.2%

Total Sediment Volume = 90,461,000 m3

Location Pb Mass (%)

County In-Channel Floodplain

St. Francois 1.1% 26.7%

Jefferson 0.6% 71.6%

Total Pb Mass = 230,000 Mg

1) Channel Pb metal mass

Almost 2x more stored in

channel segments in St.

Francois Co (higher Pb

conc.)

2) Historical Floodplain

Storage Largest sink by

far at >95%. Over 70% in

Jefferson Co. due to

thicker deposits, higher

concentrations, and larger

FP areas.