Program
All Presentations (pdf)
Monday
8:15 Brent Means
10:10 James J. Gusek
12:40 Jonathan M. Dietz
2:15 Kimberly R. Weaver
4:00 Brent Means
Tuesday
8:45 Robert Kleinmann
9:15 Brent Means
9:30 James J. Gusek
10:00 Glenn C. Miller
10:30 Linda Ann Figueroa
12:40 Art Rose
1:10 Charles A. Cravotta III
1:40 Danielle M C Huminicki
2:50 Bernard Aube
3:20 Timothy K. Tsukamoto
3:50 Bradley R. Shultz
4:20 Kimberly R. Weaver
Wednesday
8:00 Linda Ann Figueroa
8:30 John Senko
9:00 Song Jin
10:10 Jonathan M. Dietz
10:40 Daryle H. Fish
12:40 John Chermak
1:10 Griff Wyatt
1:40 Dan Mueller
2:50 Sean C. Muller
3:20 Jack Adams
3:50 Roger Bason
3:50 Mark B. Carew
Thursday
8:00 Rep. John E. Peterson
8:30 Scott Sibley
9:00 Charles A. Cravotta III
9:30 Michael R. Silsbee
10:30 Lykourgos
Iordanidis
11:00 Mark Conedera
11:30 Barry Scheetz
1:25 William Benusa
1:55 Mike Sawayda
2:25 Susan J. Tewalt
3:25 Robert S. Hedin
3:55 Chad J. Penn
4:25 Ron Neufeld
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Wednesday 3:20 Dr. D. Jack Adams, Director, Modified and Activated
Carbon Technology Center,
University of Utah
Biological Selenium and Arsenic Reduction: An Overview
Author(s)
Jack Adams, Ph.D.
Director, Modified and Activated Carbon Technology
Center
University
of Utah
Metallurgical Engineering, 412 WBB
Salt Lake City, UT 84112
801-712-2760
jadams@mines.utah.edu
Terrence D. Chatwin
University of Utah
Ximena Diaz
University of Utah
Jan D. Miller
University of Utah
Abstract
Selenium and arsenic are common contaminants worldwide. Selenium
is periodically related to sulfur
and like sulfur, positively charged selenium forms soluble oxyanions.
The chemical characteristics of
selenium and arsenic are dominated by the fact that they readily
change oxidation states or chemical form
through chemical or biological reactions that are common in the environment.
Selenium most commonly
occurs in four oxidation states: SeO4
2-, SeO3
2-, Se 0, & Se 2-. Well aerated, alkaline surface waters contain
the majority of selenium as selenate. Negative and zero valences
are associated organic and elemental
selenium while positive valences are associated with mineralogy and
aqueous systems, with selenate being
more mobile than selenite. The EPA maximum contaminant level (MCL)
for selenium in drinking water is
50 parts of selenium per billion parts of water (50 ppb) and a maximum
contaminant level goal (MCLG) of
20 ppb. Recommended levels for aquatic wildlife is 2 ppb.
Arsenic may occur as a semi metallic element (As 0), arsenate (As4
3-), arsenite (As3
3-), or arsine (H3As).
Arsenate is the oxygenated pentavalent form of arsenic and is the
most abundant species in oxygenated
waters. The Environmental Protection Agency (EPA) has established
a Maximum Contaminant Level
(MCL) of 50 µg/L for arsenic in drinking water; this value
will change to a 10 ppb national standard in
2006. Both selenium and arsenic are difficult to remove to levels
that meet current drinking water and
discharge criteria. They are used as electron acceptors by microorganisms
transforming them to reduced
states, thus removing or stabilizing them. Many of these metal transformations
are coupled with the
cytochrome system and are an energy source under anaerobic conditions.
Microbial selenium transformations have been investigated for decades
and have been found to be a
common occurrence; microbial reduction of arsenic has not been studied
as extensively. Microbes
responsible for selenium and arsenic reduction have been isolated
from contaminated mining process and
waste waters, mining waste rock materials, agricultural soils and
drainages, petroleum refining and coalfired
power generation wastewaters, and domestic wastewater treatment facilities.
Selenium and arsenic
reducing microbes can be found in numerous genera including Alcaligenes,
Escherichia, Pseudomonas,
Bacillus, Desulfovibrio, Shewanella, Enterobacter, Thauera, and numerous
genera within Cyanobacteria
and the sulfate reducing bacteria. Metal and metalloid reducing microbes
are quite biquitous and can be
cultured from environmental samples using common techniques. Some
microbes are capable of direct
selenium reduction under aerobic conditions by metal-active enzymes,
possibly a detoxification mechanism. Similar reductions are thought
to occur among some of the arsenic reducing microorganisms.
Fundamental considerations are important for successful application
of selenium and arsenic biological
treatments and involve several steps starting with site characterization,
bioassessment and biotreatability
testing, and biotreatment monitoring. While many microbes are capable
of selenium and arsenic reduction,
specific site environmental characteristics need to be taken into
consideration for optimal metalloid
reduction at any specific site. In general, biotreatments typically
produce 1,000’s of times less sludge than
conventional precipitation technologies and can be employed in several
basic ways:
- Biostimulation through addition of nutrients that stimulate most
or many of the site indigenous
microbes
- Biostimulation through isolation of key site microbes, production
of these microbes followed by
reintroduction of this population back into the treatment
system
- Bioaugmentation or the introduction of new microbes, possibly
microbes already present at the site,
but known to have the biochemical systems needed to transform
the contaminant form present and
have high transformation efficiencies
- Bioaugmentation/Biostimulation or a combination
of both techniques that leads to a population of
both new and indigenous microbes.
Selenium and arsenic
reduction/sorption has been demonstrated in various waters
with live microbial
cells, microbial biomaterials, enzymes, and proteins that have
a high affinity for these metalloids. These
biomaterials can be immobilized and have been shown to rapidly
reduce or sorb selenium and arsenic and
various other metals and inorganic contaminants from various
environmental waters.
Presentation
Biography
Dr. Adams’ background is in molecular and applied environmental
microbiology and
environmental engineering. He has worked in environmental biotechnology
for about 30
years for state & federal government agencies and industry. Dr.
Adams’ headed U.S. Army
and U.S. Bureau of Mines Biotechnology Programs, directed the Bioremediation
Center at
Weber State University and is the current director of the Modified & Activated
Carbon
Technology Center at the University of Utah.
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