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Abstracts with Programs - Geological Society of America

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20-5 BTH 26 Lee, Charlotte I. [218773]<br />

HISTORICAL CLIMATE AND STREAMFLOW TRENDS OF THE GRAND TRAVERSE BAY<br />

REGION<br />

LEE, Charlotte I., <strong>Geological</strong> Sciences, Michigan State University, East Lansing, MI 48824,<br />

leechar3@msu.edu, MARTIN, Sherry L., Department <strong>of</strong> <strong>Geological</strong> Sciences, Michigan<br />

State University, 206 Natural Sciences Bldg, East Lansing, MI 48824, KENDALL, Anthony D.,<br />

Department <strong>of</strong> <strong>Geological</strong> Sciences, Michigan State University, 206 Natural Sciences Bldg,<br />

Michigan State University, East Lansing, MI 48824, and HYNDMAN, David W., Department <strong>of</strong><br />

<strong>Geological</strong> Sciences, Michigan State University, 206 Natural Science Building, East Lansing,<br />

MI 48824<br />

The natural environment <strong>of</strong> the Grand Traverse Bay Region is not only accredited by residents<br />

as a top contributing factor to a high quality <strong>of</strong> life, it contributes to the region’s economy through<br />

recreation and tourism. Water is an extremely important part <strong>of</strong> the natural environment, as well<br />

as human use, and can be affected by climatic conditions. Because <strong>of</strong> the strong economic<br />

link, it is vital to study the Grand Traverse Bay Region‘s water resources and climate to better<br />

understand the complex relationships between driving and response factors. This in turn will<br />

help stakeholders assess potential impacts that a continually changing climate could have<br />

on the precious water resources this region depends on. Analyzing data collected by stream<br />

gauging and climate monitoring stations over the past century in the Boardman and Charlevoix<br />

River Watersheds provides insight on streamflow, temperature, and precipitation trends <strong>of</strong> this<br />

region have shifted. Cross-examination <strong>of</strong> climate change driver and response trends along <strong>with</strong><br />

ecological and anthropological data can be used to assess the past, present, and possible future<br />

impacts <strong>of</strong> regional change in stream flow and climate.<br />

SESSION NO. 21, 1:30 PM<br />

Thursday, 2 May 2013<br />

T20. Applied Geology: Engineering, Environmental,<br />

Geotechnical and Hydrogeology (Posters)<br />

(Association <strong>of</strong> Environmental and Engineering<br />

Geologists)<br />

Schneider Hall, Courtyard<br />

21-1 BTH 27 Bouali, El Hachemi Y. [218213]<br />

THE STABILITY OF THE LAKE MICHIGAN BLUFFS IN ALLEGAN COUNTY, MICHIGAN, AND<br />

THE RELATIONSHIPS BETWEEN AIR TEMPERATURE, GROUNDWATER LEVELS, AND<br />

DOWNSLOPE DISPLACEMENT<br />

BOUALI, El Hachemi Y. 1 , KAUNDA, Rennie B. 2 , CHASE, Ronald B. 1 , and KEHEW, Alan E. 1 ,<br />

(1) Department <strong>of</strong> Geosciences, Western Michigan University, 1903 West Michigan Avenue,<br />

Kalamazoo, MI 49008, el.h.bouali@wmich.edu, (2) SRK Consulting (U.S.), Inc, Suite 3000,<br />

7175 West Jefferson Avenue, Lakewood, CO 80235<br />

Unstable bluffs composed <strong>of</strong> heterogeneous glacial sediments account for approximately 60<br />

percent <strong>of</strong> the Great Lakes shoreline. This instability has been attributed to toe erosion, soil<br />

saturation, surface water flow, and/or misguided human intervention. The U.S. Army Corps <strong>of</strong><br />

Engineers and Western Michigan University conducted a joint study between 1996 and 2008 that<br />

resulted in a temporal dataset allowing significant insight into the causes <strong>of</strong> bluff failure. Electronic<br />

instrumentation, installed in 2003 <strong>with</strong>in the bluffs <strong>of</strong> Lake Michigan, north <strong>of</strong> South Haven, MI,<br />

has led to data that grants explanations for the mechanisms and causes <strong>of</strong> failure. Instruments<br />

include subsurface arrays <strong>of</strong> in-situ inclinometers, vibrating wire piezometers, thermistors, and<br />

weather stations. Over the 12-year acquisition <strong>of</strong> displacement, groundwater, wave, precipitation,<br />

and temperature data, the damaging effects <strong>of</strong> groundwater activity, especially during times<br />

<strong>of</strong> freeze/thaw cycles, have been adequately observed. Groundwater was also discharged<br />

from vertical pumping wells during the winter seasons <strong>of</strong> 2003 and 2005. The vertical pumping<br />

wells were located in a dewatering site next to a (non-dewatered) control site. Downslope<br />

displacements were reduced by as much as 400 percent when compared to the control zone<br />

displacements during the dewatering times.<br />

Statistical evaluation <strong>of</strong> the data has emphasized the erosional effects during freeze/thaw<br />

cycles. Correlation and kernel density studies <strong>of</strong>: (1) air temperature versus downslope rotational<br />

displacement, (2) air temperature versus perched ground water potentiometric surface elevations,<br />

and (3) groundwater-level fluctuations verses downslope rotational displacements, have<br />

demonstrated instantaneous displacement activity when air temperatures cross 0° Celsius. The<br />

freezing <strong>of</strong> bluff surfaces produces a barrier to perched water discharge, which then raises pore<br />

pressures to produce a factor <strong>of</strong> safety <strong>of</strong> less than one; this results in simple shear displacement<br />

<strong>with</strong>in the bluff. As the frozen bluffs thaw there is a rapid discharge <strong>of</strong> stored groundwater, which<br />

creates an additional lagged downslope displacement that accompanies the increase <strong>of</strong> flow<br />

pressure. The second pulse <strong>of</strong> displacements tends to be back rotations that accompany block<br />

movements <strong>of</strong> coherent soil.<br />

21-2 BTH 28 Lightfoot, Randall E. [218233]<br />

ANALYZING THE STRUCTURAL PROPERTIES, GEOLOGIC CONDITIONS, AND FRIABILITY<br />

OF GARNET SANDS FROM FOUR MINE SOURCES AROUND THE WORLD: IMPLICATIONS<br />

FOR THE DRY-AIR ABRASIVE SAND BLAST-CLEANING INDUSTRY<br />

LIGHTFOOT, Randall E., Augustana College, 1411 Dahlgren Lane, Minooka, IL 60447,<br />

randalllightfoot09@augustana.edu<br />

Due to its relatively high specific gravity, chemical inertness, isometric geometry, nontoxicity,<br />

lack <strong>of</strong> crystalline silica, ability to be recycled, low friability, and high hardness, garnet sand<br />

(var. almandine–pyrope) is one <strong>of</strong> the leading non-metallic abrasive media being used in the<br />

dry-air abrasive sand blast-cleaning industry. The primary task <strong>of</strong> this industry is to blast-clean<br />

steel infrastructure, remove all mill-scale and rust/corrosion, while simultaneously preparing<br />

the steel for a top-coating, which increases the integrity and longevity <strong>of</strong> the steel. Marco<br />

Industries (Davenport, IA) has provided five garnet sand samples from four localities. Two <strong>of</strong><br />

the five samples are <strong>of</strong> hard rock origin while the remaining three samples were mined from<br />

fluvial systems. One hard rock garnet sample was mined from khondalites in the granulite belt<br />

<strong>of</strong> the North China Craton, Inner Mongolia, and the other from a meta-gabbro-derived garnetamphibolite<br />

from Gore Mountain, New York, U.S.A. Two <strong>of</strong> the three fluvial garnet sands were<br />

SESSION NO. 21<br />

mined from the Thamirabarani River feeding into Bengal Bay, Eastern India, and the other from<br />

the Hutt River emptying into Port Gregory, Western Australia. X-ray fluorescence spectroscopy,<br />

scanning electron microscopy, and grain size analysis methods were used to determine bulk<br />

and trace element compositions, change in geometry, percent degradation, percent dusting, and<br />

friability <strong>of</strong> each garnet sample. In order <strong>of</strong> increasing friability, the sample rank: 1: NY-garnet<br />

sample, 2: India (1) garnet sample, 3: India (2) garnet sample, 4: Australia garnet sample, and<br />

5: Mongolia garnet sample. Data show that the superior garnet sand <strong>with</strong> the lowest friability is<br />

from Gore Mountain and the most inferior, highest friability, is from Mongolia. Another rank was<br />

assigned to each garnet in terms <strong>of</strong> increasing dust created during one blast operation, <strong>with</strong><br />

particles ranging from 1 to 100 μm in diameter. India (2) garnet sand created 7.7% dust, New<br />

York garnet sand created 8.9% dust, India (1) garnet sand created 12.7% dust, garnet sand from<br />

Australia created 14.4% dust and garnet from Mongolia created 26.8% dust. The percentages<br />

show how much <strong>of</strong> the garnet sand degraded after one blast operation, and provide insight about<br />

the friability <strong>of</strong> each garnet sand.<br />

21-3 BTH 29 Baratta, Vanessa M. [218415]<br />

THE EFFECTS OF FREEZE-THAW CYCLES AND STORMWATER RUNOFF INPUT ON THREE<br />

BIOSWALE SOIL MIXTURES<br />

BARATTA, Vanessa M., Geoscience, University <strong>of</strong> Iowa, Iowa City, IA 52242,<br />

vanessa-baratta@uiowa.edu, BETTIS, E. Arthur III, Geoscience, University <strong>of</strong> Iowa,<br />

121 Trowbridge Hall, Iowa City, IA 52242, WARD, Adam S., Department <strong>of</strong> Geoscience,<br />

University <strong>of</strong> Iowa, 121 Trowbridge Hall, Iowa City, IA 52240, and WEIRICH, Frank,<br />

Department <strong>of</strong> Geosciences, University <strong>of</strong> Iowa, 121 Trowbridge Hall, Iowa City, IA 52242<br />

Urbanization and the growth <strong>of</strong> suburbs are world-wide phenomena. One product <strong>of</strong> this<br />

development is a dramatic increase in impermeable surfaces and a consequent increase in<br />

stormwater run<strong>of</strong>f. Bioretention cells (biocells) are one best management practice frequently<br />

used to mitigate the impacts <strong>of</strong> urban stormwater run<strong>of</strong>f. To ensure that a biocell will continue to<br />

perform adequately in the long term, it is imperative that the varieties <strong>of</strong> conditions it will sustain<br />

through time are considered during its initial design. Although biocells are frequently used for<br />

stormwater management, very few quantitative data exist on how they perform through time and<br />

in varied physical environments. In regions <strong>with</strong> seasonal freeze-thaw cycles, it is important to<br />

understand the physical effects <strong>of</strong> freeze-thaw cycles on biocell materials so that the integrity<br />

<strong>of</strong> the design will not be compromised by seasonal change. This project utilizes manufactured<br />

laboratory columns to investigate the effects <strong>of</strong> freeze-thaw cycles and run<strong>of</strong>f sediment input on<br />

the infiltration capacity <strong>of</strong> three different biosoil mixtures. These tests will provide an analog for<br />

long-term changes in biocell infiltration rates due to seasonal variations, which will provide critical<br />

data on which soil mixture would be best implemented in geographic regions susceptible to<br />

freeze-thaw activity. Furthermore these results will inform design standards for biocells to insure<br />

their long-term use.<br />

21-4 BTH 30 Erich, Kyla J. [218479]<br />

WOLF CREEK DAM: A CASE STUDY OF FOUNDATION REMEDIATION FOR DAMS BUILT ON<br />

KARST FOUNDATIONS<br />

ERICH, Kyla J., Missouri University <strong>of</strong> Science and Technology, Rolla, MO 65409,<br />

kje6f4@mail.mst.edu<br />

Wolf Creek Dam was completed in 1952 as a 5,736 ft long and 258 ft high combination<br />

embankment-concrete gravity dam. Its storage capacity <strong>of</strong> 6 million acre feet makes it the ninth<br />

largest reservoir in the nation. The dam was built on a heavily karstified limestone foundation and<br />

began exhibiting signs <strong>of</strong> excess foundation seepage in late 1967. This led to extensive corrective<br />

work beneath the earthen core <strong>of</strong> the right abutment embankment to reduce underseepage. In<br />

2006 an independent assessment by the Dam Safety Action Classification Peer Review Panel<br />

recommended that Wolf Creek Dam exhibited “Urgent and Compelling” foundation seepage<br />

issues that required immediate attention. This classification triggered the most complex dam<br />

foundation remediation project <strong>of</strong> any dam in the world, <strong>with</strong> an estimated total cost <strong>of</strong> $594<br />

million, requiring six years <strong>of</strong> construction. The drilling and grouting techniques being applied<br />

insitu beneath the embankment section will likely establish new standards <strong>of</strong> practice for<br />

remediation and foundation beneficiation for hydraulic structures built on karst sites, specifically<br />

embedded barrier walls.<br />

21-5 BTH 31 Crane, Renee [218684]<br />

ALLOWING TIME FOR ACTIVATED CARBON CONDITIONING IN CONTAMINATED SOILS<br />

INCREASES THE EFFECTIVENESS OF STABILIZATION/SOLIDIFICATION<br />

CRANE, Renee, 1070 Claymoor Drive, Apartment 2A, Kalamazoo, MI 49009,<br />

renee.e.crane@wmich.edu and CASSIDY, Daniel, Geosciences, Western Michigan<br />

University, Kalamazoo, MI 49008<br />

Stabilization and Solidification (S/S) can be a cost-effective remediation tool for contaminated<br />

soils and sediments, and is considered an accepted technology by the US EPA. S/S involves<br />

mixing amendments into the contaminated material which reduce the leachability <strong>of</strong> the<br />

contaminants. Though originally designed for inorganic contaminants, S/S is increasingly being<br />

used for sites contaminated <strong>with</strong> organic compounds.<br />

Two amendments commonly used for organics are Portland cement (or other pozzolanics<br />

like quick lime or fly ash) and powdered activated carbon (PAC). Cementing agents reduce the<br />

leaching <strong>of</strong> organic contaminants by reducing the permeability <strong>of</strong> leachate, and by encapsulating<br />

soil particles to which contaminants are adsorbed. The PAC serves as surface area to which<br />

organic contaminants adsorb very strongly. Ideally, PAC should be given time to adsorb<br />

contaminants before cementing agents are added, called PAC conditioning. However, in practice<br />

both amendments are typically added at the same time to reduce costs. Laboratory studies<br />

conducted on phenol suggest that there is no benefit by allowing PAC conditioning before adding<br />

cementing agents. However, these studies were done on soils artificially contaminated <strong>with</strong><br />

phenols, whereas aged contaminated soils tend to behave quite differently. Moreover, phenols are<br />

not very common contaminants <strong>of</strong> soils.<br />

We will present results from laboratory studies on 6 different soils <strong>with</strong> aged contamination<br />

from BTEX (i.e., benzene, toluene, ethyl benzenes, and xylenes). The studies measured leaching<br />

(using the synthetic precipitation leaching procedure, or SPLP) in soils amended <strong>with</strong> PAC and<br />

Portland cement simultaneously, and compared PAC conditioning times <strong>of</strong> 1 month, 3 months,<br />

6 months, 9 months, and 1 year. Results demonstrate that pre-treatment <strong>with</strong> PAC before<br />

cement dosing dramatically reduces leaching and increases the effectiveness <strong>of</strong> S/S for organic<br />

contaminants.<br />

2013 GSA North-Central Section Meeting 51

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