Title: HSRCS
1HSRC/SSW Research and OutreachActivities and
Capabilities
Danny Reible Chevron Professor of Chemical
Engineering Director, Hazardous Substance
Research Center/SSW Louisiana State
University Baton Rouge, LA 70803
2Hazardous Substance Research Center
South and Southwest
- Established under CERCLA
- Mission
- Research and Technology Transfer
- Contaminated sediments and dredged material
- Historically focused on in-situ processes and
risk management - Unique regional (46) hazardous substance
problems - Outreach
- Primarily regional in scope
- Driven by community interests and problems
LSU
Georgia Tech
Texas AM
Rice
3HSRC Contacts
4HSRC S/SW Programs
- Core funding from EPA
- 900 K per annum, 2001-2006
- 600 K research
- 300 K outreach
- Technology Transfer
- Technical Outreach Services to Communities
- Technical Assistance for Brownfields (TAB)
- 150 K per annum
- Other Federal Support
- Anacostia Capping Demonstration Program -5 M
(2001-2004) - Defense Threat Reduction Agency - 1.7 M
(1999-2001) - Louisiana Biotechnology Initiative
- 235 K per annum, 2002-2007
- 285 K capital, 2002-2003
5HSRC/SSW Outreach
- Goal (TOSC)To provide no-cost, non-advocate
technical assistance to communities in EPA
Regions 4 and 6 addressing issues of
environmental contamination. - Goal (TAB) To provide no-cost, non-advocate
technical assistance to communities and
municipalities in EPA Regions 4 and 6 addressing
redevelopment of environmentally contaminated
property.
6Why Outreach?
- Presidential and Congressional Commission on Risk
Assessment and Management - Provides framework more decision making
- Key point
- Engage stakeholders early and often
- Without stakeholder involvement decisions are
easily made but difficult to implement - With stakeholder involvement, decisions may be
difficult but implementation may be easier - Allowing us to finally complete the circle!!!
7Approach to Outreach Efforts
- Identify a community
- Success is dependent upon identifying appropriate
community - Community is not defined by its loudest
individuals - Develop a letter of agreement
- Identifies expectations and approach
- Negotiated and agreed upon jointly
- Basis for metrics of success The Yardstick
- Must be sufficiently detailed and specific to
provide useful metrics - Conduct outreach effort
- Continuously review and update objectives and
approach - Document changes as necessary, including updating
letter of agreement - Evaluate success in delivering outreach
objectives - Exit interviews with community
- Outreach team internal review
- Center administration and Outreach Advisory
Committee review
82002 TOSC Program
- First Year of TOSC II, Five-Year Funding Period
- Mix of traditional TOSC challenges with
multi-media assistance efforts - Meetings with EPA February in Dallas June in
Atlanta - State agencies marketing campaign
9Total TOSC Assistance Efforts By Year
10TOSC Region 4 Communities
- Holly Hill, SC
- Byron, GA
- Barnwell, SC
- Southern Pines, NC
- Davie, FL
- Albany, GA
- Rome, GA
- El Paso, TX
11TOSC Region 6 Communities
- Alsen (Baton Rouge), LA
- Corpus Christi, TX
- Shreveport, LA
- Amarillo, TX
- Las Cruces, NM
- Calcasieu Parish, LA
12TOSC Short-Term Assists
- Fogelsville, PA
- Landfill issue. Found TOSC through an
Environmental Update on landfills on TOSC
web-site - Georgia State Senator Campaign (brownfields)
- Louisville, KY (risk management plan)
- Memphis TN
- DeQuincy, LA (plant siting concerns)
- Region 6 Environmental Justice Listening Session
132002 TAB Program
- Projects becoming more complex
- Not just site assessments anymore
- Land-use planning and visioning requests are more
common - Economic development aspect still crucial
- Looking beyond TAB in order to provide assistance
14Total TAB Assistance Efforts by Year
15Region 4 TAB Communities
- Augusta, GA
- Macon, GA
- Spartanburg, SC
- Charleston, SC
- Jackson, MS
- Atlanta, GA
- Macon, GA
16Region 6 TAB Communities
- Lake Charles, LA
- West Monroe, LA
- Baton Rouge, LA
- Prairie View, TX
- Westwego, LA
17New Research
- Urban Reflux The 2000 Census and the Challenges
of Metro Growth Patterns - The Design and Use of Modeling Tools and Their
Application - Brownfields and Scale Factors in Research and
Urban Redevelopment
18TOSC/TAB Staffing
- Bob Schmitter, Ga Tech, Program Reg 4
Coordinator - Denise Rousseau Ford, LSU, Reg. 6 Coordinator
- Corey Fischer, Ga Tech
- Faith Stephens, LSU
- Tomeka Prioleau, LSU
- Mark Hodges, Ga Tech
- Claudia Huff, Ga Tech
19HSRC Research Why are contaminated sediments
difficult?
- Reside in highly variable, dynamic systems
- Normal variation in flows and storm events
- Significant source of uncertainty
- Sophisticated models but limited process
knowledge to drive them - Large volume of sediment
- Often greater than 1,000,000 m3
- Average Superfund site ex situ treatment -
- Large amounts of water
- Dredged solids content often in range of 1-10
- Often marginal contamination with incomplete
exposure pathways and uncertain risks
20Contaminated SedimentsWhy are they so important?
- Historical sources largely controlled
- Legacy of contaminated sediments as important
source - Continuing sources, however, limit potential
cleanup - Lack of disposal options is a major impediment to
harbor development - 95 of shipping trade passes through dredged
ports - Significant impediment to unrestricted usage of
waterways - Fish advisories throughout great lakes and other
areas - Widespread problem
- Of 21,000 national sediment sampling stations
(1996 survey) - 26 exhibit potential of adverse effects
- Additional 49 exhibiting intermediate
probability of adverse effects - About 30 of superfund sites involve contaminated
sediments
21Regional Sediment Issues Why are they important
in the Southern US?
- Contain 54 of nations wetlands
- Contain 45 of nations inland waters
- 46 of total on and off-site toxic releases
- 52 of surface water toxic discharges
- 35 of total number of river reaches intermediate
or high probability of adverse effects (national
average 26) - Large variety of lacustrine, riverine, estuarine,
and coastal marine sediments - Sensitive wetland habitat concerns about
invasive management options - Subject to large tropical storm events including
hurricanes
22Instrumentation Capabilities HSRC/SSW
- Analytical Capabilities
- GC/MS, GC, HPLC- Fluorescence/UV, LSC, TOC,
ICP-MS - Cooperative units XRF and XANES, XRT, gamma
emitter profiling - Field assessment capabilities
- Environmental monitoring and sampling systems
(e.g. multicorer, portable anemometry, acoustic
doppler profiler, sediment profiling camera) - Cooperative units research vessels, sonar
profiling - Biological assessment
- Accumulation, bioturbation, bioavailability
- Cooperative Units molecular biological
facilities
23Research and Assessment CapabilitiesHSRC/SSW
- Engineering Management of Contaminated Sites
- Modeling for chemical transport and fate
- In-house modeling tools
- Experience with 3rd party models
- In-situ management technologies evaluation and
development - Conventional and active capping of contaminated
sediments - Natural and enhanced recovery of soil and
sediment systems - Decision framework support
24Current Core Research Programs
- Bioavailability of Desorption Resistant
Contaminants - Evaluation of the kinetics and extent of the
availability of desorption-resistant contaminants
and the relationship to fate and accumulation - In-situ Containment and Treatment of Contaminated
Sediments - Development of innovative approaches to in-situ
containment, particularly the combination of
in-situ containment and treatment- active caps - Contaminant Losses during Sediment Resuspension
by Removal or Storm Events - Assess contaminant losses, particularly of
metals, as a result of exposure by dredging or
episodic storm events - Phytoremediation of Wetland and CDF Sediments
- Evaluate effectiveness of phytoremediation for
in-situ treatment in wetlands or to employ
confined disposal facilities as active treatment
facilities
25Bioavailability of Desorption-Resistant
Contaminants
- PIs D.D. Reible and J.W. Fleeger
- Evaluation of the kinetics and extent of the
availability of desorption-resistant contaminants
and the relationship to fate and accumulation - Desorption resistance well known
- Implications for availability less well known or
unknown - Deposit feeders have clear advantages in
assessing bioavailability - Preliminary work suggested porewater paradigm
valid - Can physico-chemical measurements predict
bioavailability? - Can we move toward a truly predictive estimate of
bioavailability by predicting physico-chemical
partitioning?
26In-situ Containment and Treatment of Contaminated
Sediments
- PIs KT Valsaraj, M. Wiesner, B. Edge
- Development of innovative approaches to in-situ
containment and/or treatment- active caps - Conventional capping effective tool for physical
separating contaminants, armoring underlying
sediments and reducing contaminant flux - Innovative caps may be effective tool in niche
applications where conventional caps are
problematic - Innovative caps may have poor placement
properties- an improved understanding of
depositional processes may assist (M. Wiesner) - Innovative caps may exhibit marginal stability
we need a modeling tool capable of assessing that
stability (B. Edge) - What are the real advantages of an innovative cap
we need experimental assessment and modeling
tools capable of predicting effectiveness (KT
Valsaraj)
27Contaminant Losses during Sediment Resuspension
- PIs M. Tomson and L. Thibodeaux
- Assess contaminant losses, particularly of
metals, as a result of exposure by dredging or
episodic storm events - Storm or dredging events tend to move sediments
from stable anaerobic environment to aerobic,
exposed environment - Release of hydrophobic organics relatively
insensitive to physicochemical state (e.g. redox
conditions) of sediments - Metals expected to be influenced to a much
greater degree - What are the fundamental processes and can we
describe and predict their behavior? (M. Tomson) - What are the implications of these processes and
behavior on real storm and dredging events? (L.
Thibodeaux)
28Phytoremediation of Wetland and CDF Sediments
- PIs J. Pardue, C. Theegala (Southern
University) - Evaluate effectiveness of phytoremediation for
in-situ treatment in wetlands or to employ
confined disposal facilities as active treatment
facilities - If sediment removal is planned, phytoremediation
may represent one of the few cost-effective means
of managing the contaminants beyond simple
storage - If the contaminated sediments lie in a sensitive
wetland, phytoremediation may be the only means
of managing the contaminants without destroying
the wetland - To what extent do plants mobilize and take up
contaminants? - To what extent do plants decontaminate the
sediments?
29Related Research Programs
- Natural and enhanced recovery of contaminated
sediments - Identification and assessment of mechanisms
- Development of modeling tools
- Contaminant losses from confined disposal
facilities - Seepage, leachate losses (D. Reible)
- Model development effort with LSU Computer
Science - Volatile losses (KT Valsaraj and L. Thibodeaux)
- Extensive process and mechanism evaluation
- Various models developed in cooperative effort
with USACE - Field validation in planning (Chicago CDF)
- Sediment cap design and evaluation
- Apatite reactive barrier for metal control
(w/Univ New Hampshire) - Spectroscopic tools for characterization of cap
effectiveness - Site specific support activities
- Anacostia Active Capping Demonstration Program
30Capping with a Reactive Barrier
- Apatites Ca5(PO4)3OH
- Subject to isomorphic substitution
- Pb5(PO4)3OH
- Cd5(PO4)3OH
- Reduces migration of metal species
- Employing X-Ray Fluorescence to evaluate in
cooperative effort between D. Reible, C. Willson
and Univ of New Hampshire
31Characterization of Cap Effectiveness
- XANES (X-Ray Adsorption Near Edge Spectroscopy)
- XANES sensitive to oxidation state
- Chromium
- XANES differentiation of Cr(III) and Cr(VI)
- Cr(VI) of much more environmentally significance
- Differentiation not possible by conventional
analytical techniques due to rapid conversion
(e.g. by ICP-MS) - Effort to further define state and mobility of
metal contaminants - XRT (X-Ray Tomography)
- Define sediment structure at the pore level
- Employed by C. Willson and K. Thompson for
nonaqueous phase liquids in soils , now
evaluating reactive barriers as caps
32Site Specific Cap Support
- Thea Foss Waterway, WA
- Assessing cap placement for containment of a NAPL
seep - Pine Street Canal, VT
- Design of a cap over extremely soft sediments
- San Francisco Bay, CA (3 sites)
- Design of cap for refinery sludges, coastal
sediments and metal contaminated slough - Fox River, WI
- Evaluation and design of dredging and capping
alternatives - Calcasieu Estuary, LA
- Design of a cap over soft sediments employing
dredged material
33Innovative Cap Demonstration - Anacostia
- Sand caps easy to place and effective
- Contain sediment
- Retard contaminant migration
- Physically separate organisms from contamination
- Greater effectiveness possible with active caps
- Encourage fate processes such as sequestration or
degradation of contaminants beneath cap - Discourage recontamination of cap
34Demonstration Site Anacostia River
- Two potential study areas identified adjacent to
Navy Yard - First site has elevated PCBs and metals 1
- Second site is primarily PAHs 2
- Some seepage, free phase at depth at second site
- Funding
- 2.25 MM (Phase 1)
- 2.75 MM (Phase 2)
Washington DC
Tidal Basin
2
1
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36Cap Technologies Under Evaluation
- Aquablok for control of seepage and advective
contaminant transport - Zero-valent iron to encourage dechlorination and
metal reduction - Phosphate mineral (Apatite) to encourage sorption
and reaction of metals - BionSoil to encourage degradation of organic
contaminants - Natural organic sorbent to encourage
sorption-related retardation (reduction in
advective-diffusive transport) - Other technologies undergoing feasibility
evaluation - CETCO (needlepunched mat)
- Coke/Carbon
37Capping Demonstration Schedule(Revised)
- Technology Evaluations (Initial Phase) Jul/Dec
2002 - Studies currently ongoing at LSU and
collaborating institutions - Site Characterization Jan-Apr 2003
- Phase 1 Geophysical Investigation (Jan 2003)
- Phase 2 Geotechnical and Chemical Assessment (Feb
2003) - Phase 3 Biological Assessment (Apr 2003)
- Cap Design Jan/Jun 2003
- Cap Placement Jul/Aug 2003
- Cap Evaluation Aug 2003/Sept 2004
38Louisiana Biotechnology Initiative
- Goal
- Enhance fundamental understanding and practical
application of biological systems for remediation
of environmental contaminants and treatment of
industrial wastes - Approach
- Select, enrich, and manipulate the members of a
microbial consortia to attain specific, desirable
characteristics that minimize the uncertainty
accompanying design and operation of waste
treatment systems and environmental remediation
strategies - Molecular biology tools allow the detection of
specific organisms, track the expression of
specific genes, and characterize microbial
populations - Key technical leads
- Fred Rainey, Department of Biological Sciences
- Bill Moe, Department of Civil and Environmental
Engineering
39Louisiana Biotechnology InitiativeProjects
- Assessment/Enhancement of Biological Processes in
Remediation of Contaminated Sediments (D. Reible) - Characterize microbial community inhabiting
biologically active zone and influence of benthic
organisms on that community - Identify genetic markers that indicate potential
for bioremediation in benthic organisms - Characterization of Reductively Dechlorinating
Microbial Populations (J. Pardue) - Investigate factors controlling the spatial and
temporal distribution, selection and enrichment
of Dehalococcoides sp., a specific strain of
which is the only known degrader of
tetrachloroethene (PCE) to ethene - Field laboratory Petroprocessors Superfund Site
40Louisiana Biotechnology Initiative Projects
- Characterization of Microbial Populations
Responsible for Target Organics in Industrial
Wastewater Treatment (W. Moe) - Modeling effort to link experimental observations
and molecular characterization of microbial
populations with treatment process performance - Collaborative effort with BASF
- Biofiltration for Treatment of Gas-Phase VOC
Contaminants (W. Moe) - Application of selective pressures to manipulate
the selection and enrichment, physiological
state, and spatial distribution of biofilters
microbial consortia - Collaborative effort with Honeywell Corp.
41HSRC/SSW Technology Transfer
- GoalTo widely disseminate research findings and
technical expertise to interested communities
with regards to hazardous substance/sediments
remediation research.
42HSRC/SSW Technology Transfer (Traditional
Activities)
- Technology transfer
- Website
- Electronic newsletters
- Quarterly email notification Are you on the
email list? - Printed publications
- Research Briefs
- Environmental Updates
- Workshops/facilitated meetings
- Contaminated Sediments Working Group (web-based)
- Audio/video research presentations
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45HSRC Web Highlights
- Allows all HSRC accomplishments to be viewed in a
single frame a portal to each center web site. - 590,000 hits on site since March 2000
- Currently averaging 559/day, 200,000/yr
- Archive of research abstracts from all centers
- Online archive of key center publications
- Growing library of HSRC audio presentations
- Interactive map of HSRC outreach sites, with
retrievable community information embedded - Created several technology-specific web sites.
46HSRC/SSW Technology Transfer (Five Center
Support)
- Centerpoint
- Summary of successes of past centers
- New centers research focuses and themes
- Outreach activities
47Advanced Study Institutes In situ Assessment and
Remediation
- NATO ASI
- Prague, May 24 June 2, 2001
- Approximately 100 lecturers and students
- Book in final stages of preparation
- NSF Pan-American Advanced Studies Institute
- Rio de Janeiro, July 22-August 3, 2002
- Organization currently underway
- 75-100 lecturers and students (half from US)
48HSRC/SSWTechnology Transfer Personnel
- Leigh McCook, Georgia Tech, Associate Director
- Mark Hodges, Georgia Tech
- Therese Turman, Georgia Tech
- Jim Demmers, Georgia Tech