Bioremediation-contaminants (Ch. 14)
Joonhong Park
May 27, 2014
History of Hazardous Chemicals
Synthetic detergents (Germany during World War II): Poor Biodegradability of Branched Alkyl Benzene Sulfonate (ABS) [Figure 14.1]
Pesticides: Silent Spring (Rachel Carson, 1962)
Polychlorinated biphenyls (PCBs) and halogenated hydrocarbon: probably cause about half of the environmental problems attributable to organic pollution in the world (Tiedje et al., 1993)
Natural occurring pollutants: BTEX (benzene, toluene, ethlybenzene, xylene), polycyclic Aromatic Hydrocarbons (PAHs), dioxins, heavy metals, radioactive matters/rays, asbestos etc.
Recalcitrant to Microbial degradation of Chemicals
Factors causing molecular recalcitrance
Martin Alexander (1965) described factors causing organic compounds to resist biodegradation in the environment, which he termed “molecular recalcitrance”:
1. A structural characteristic of the molecule prevents an enzyme from acting2. The compound is inaccessible, or unavailable.3. Some factor essential for growth is absent4. The environment is toxic5. Requisite enzymes are inactivated.6. The community of microorganisms present is unable to metabolize the
compound because of some physiological inadequacy.
Molecular Structure
Relationship between enzyme activation site and the chemical structure of a pollutant (cf. Quantitative Structure-Activity Relationship)
Electronic, hydrophobic and steric effects
Henry’s constant, KH: volatilization
Octanol-water partitioning constant, Kow: hydrophobicity, sorption
Solubility, Cs: bioavailability
Bioavailability
NAPLPhase
Or
SOM
water
Bacterium
C-water
C-NAPL
C-SOM
What if the aqueous concentration is lower than “threshold” forMicrobial biodegradation ?
Contaminant availability for biodegradation
Two phenomena limiting substrate availability for biodegradation
- Strong sorption to surfaces- Formation of a nonaqueous phase
Limited substrate availability is bad for biodegradation of a contaminant while is good for biodegradation when the compound is toxic to microorganisms.
Light NAPL (non-aqueous phase liquid) contamination
Capillary fringe
Water table
Groundwater Flow
Tank LNAPL
residual
LNAPLFree Phase
Dissolved LNAPL (plume)
Vapor from LNAPL
Dense NAPL contamination
Capillary fringe
Water table
Groundwater Flow
NAPL residual
LNAPLFree Phase
Vapor from NAPL
Dissolved NAPL (plume)
Groundwater Flow Direction
Bedrock
Clay Layer
Relative ease of cleaning-up of contaminated aquifers as a function of contaminant chemistry and hydrogeology (1=easiest; 4 = the most difficult)
Contaminant chemistry
Mobile,
Dissolved
(degrades/
Volatilizes)
Mobile,
Dissolved
Strongly sorbed, dissolved
(degrades/volatilizes)
Strongly sorbed, dissolved
Separate
Phase
LNAPL
Separate
Phase
DNAPL
Homogeneous,
single layer 1 1-2 2 2-3 2-3 3 Homogeneous,
multiple layer 1 1-2 2 2-3 2-3 3
Heterogeneous,
single layer 2 2 3 3 3 4 Heterogeneous,
multiple layer 2 2 3 3 3 4
Fractured 3 3 3 3 4 4
Hydrogeology
Microorganism presence
Even though a contaminant is known to be readily biodegradable, the absence of a suitable microbial population may be a limiting factor.
Bioaugmentation: - addition of biodegradation populations into contaminated fields.- The survival of foreign microbes in new environment is questionable.-Genetically modified organisms cannot be released into fields. (Genetically modified indigenous microbes? Digging contaminated soil into a field to be treated? Are they acceptable?)
Categories of environmental contaminants
Hydrocarbons: BTEX (low FW), PAHs (high FW)
Oxygenated hydrocarbons: alchohols, ketones, ethers, MTBE
Halogenated aliphatics: chlorinated ethenes, chlorinated ethanes (highly chlorinated vs. low chlorinated)
Halogenated aromatics: PCBs, chlorinated dioxins, chlorinated dibenzofurans (highly chlorinated) and other low chlorinated halogenated aromatics
Nitroaromatics: TNT, RDX, HMX
Metals: Cr. Cu, Ni, Pb, Hg, Cd, Zn etc.
Nonmetals: As, Se
Oxyanions: nitrate, (per)chlorate, phosphate
Radionuclides
See Table 14.1 and Table 14.2
Energy Metabolism versusCometabolism
Energy Metabolism: Respiration and Catabolism of a Pollutant => Resulting in Microbial Growth => sustainable biodegradation
Cometabolism: Fortuitously biodegraded => Little Microbial Growth => May not be sustainable
Absence of physiologically significant compounds
Electron donor.
Electron acceptor (e.g. oxygen limitation is common).
Inducing agent (e.g. presence of toluene is needed to induce toluene oxygenase expression)
Carbon, nitrogen and phosphorus sources
Trace metals (e.g. Fe is needed for oxygenase)
60
50
40
30
20
10
0
-10
-20
-30
-40
-50
-60
-70
-80
∆Go’
(kJ/e- eq)
0.25CO2 + H+ + e- = (1/24)C6H12O6 + 0.25H2O (Glucose/CO2)
H+ + e- = 0.5H2 (Hydrogen/H+)
1/6CO2 + H+ + e- = (1/12)CH3CH2OH + 0.25H2O (Ethanol/CO2)
1/8CO2 + 1/8 HCO3- + H+ + e-
= 1/8 CH3OO- + 3/8H2O (Acetate/CO2)
1/8 CO2 + H+ + e- = 1/8 CH4 + 0.25H2O (methane/CO2)
1/8 SO42- + 19/16H+ + e-
= 1/16 H2S + 1/16 HS- + 0.5H2O (sulfide/sulfate)
1/5 NO3- + 6/5H+ + e- = 1/10 N2 + 3/5H2O (N2/Nitrate)
Fe3+ + e- = Fe2+ (Fe[II]/Fe[III])
1/4O2 + H+ + e- = 0.5H2O (H2O/O2)
½ CCl2CCl2 + ½ H+ + e- = ½ CHClCCl2 + ½ Cl- (PCE)
ElectronDonors
ElectronAcceptors
S-min, CSTR and PFR
Travel Time through a Reactor
S(m
g/
L)
CSTR
PFR
S-min
Scope and characteristics of contaminants
• Category of Contaminants
Category of compounds Examples Prevalent uses
Aromatic hydrocarbons
Oxygenated hydrocarbons
Hydrocarbons with specific elements
Other hydrocarbons
Metals and cations
Nonmetals and anions
Microorganisms
Radionuclides
Benzene,
toluene etc.
Phenol
acetone etc.
TCE
1,1,1 TCA
2,4-D
Kerosen, gasoline, lignin…
Iron
Chromium
arsenic
Chloride, sulfate, ammonia
Bacteria, viruses
Uranium238, tritium, radium226
Dyestuffs
solvents
Paints
Solvents
Solvents
Munitions
pesticides
Fuels
Alloys
Electrical and electronics
Fertilizers, Foodadditives
Medical applications
Degree of Halogenation vs. Biodegradation
C C
Cl
Cl
Cl
Cl
C C
Cl
Cl
H
Cl C C
H
Cl
Cl
H
C C
Cl
Cl
H
H
C C
H
H
Cl
H
C C
H
H
H
H
Tetrachloroethene(Perchloroethene, PCE)
Trichloroethene(TCE, Cs = 1,100 mg/L)
cis-Dichloroethene(cDCE)
trans-Dichloroethene(tDCE)
monochloroethene(vinyl chloride, 발암물질 )
ethene
가장 산화됨
가장 환원됨
Monochlorinated Polychlorinated0.25 4
Degree of Chlorination
So
rpti
on
on
to S
ub
surf
ace
Mat
eria
l
Deg
rad
atio
n R
ateSorption
Reductive dechlorination
Aerobic degradation
BiodegradabilityThe apliphatic and aromatic hydrocarons are readily biodegradable by a
range of aerobic bacteria and fungi. The key is that molecular O2 is needed to activate the molecules via initial oxygenation reactions.
Evidence of anaerobic biodegradation of aromatic hydrocarbons is growing. Anaerobic biodegradation rates are slower than aerobic rates, but they can be important when fast kinetics are not essential.
Most halogenated aliphatics can be reductively dehalogenated, although the rate appears to slow as the halogen substituens are removed.
Highly chlorinate aromatics, including PCBs, can be reductively dehalogenated to less halogenated species.
Lightly halogenated aromatics can be aerobically biodegraded via initial oxygenation reactions.
Many of the common organic contaminants show inhibitory effects on microorganism growth and metabolism. Due to their strongly hydrophobic nature, many of the inhibitory responses are caused by intereactions with the cell membrane. In some cases, intermediate products of metabolism can be more toxic than the original contaminant.
Scope and characteristics of contaminants
• Organic compounds - most often amenable to bioremediation
- the most detected in groundwater
- Many of them are hydrophobic (log Kow >1) and less soluble (solubility < 10,000 mg/l) Ex. PAH, PCB => Significance?
- Some are volatile (KH > 10-3 atm-m3/mol)
Synthetic organic contaminants reported to be most frequently found in drinking-water wells (Council on Environmental Quality, 1981)trichloroethene (TCE), toluene, 1,1,1-trichloroethane, acetone, methylene chloride, dioxane, ethyl benzene, tetrachloroethene, cyclohexane, chloroform,
di-n-butyl-phthalate, carbon tetrachloride, benzene, 1,2-dichloroethene,
ethylene dibromide, xylene, isopropyl benzene, 1,1-dichloroethene, 1,2-dichloroethane, bis phthalate, dibromochloropropane, trifluorotrichloroethane, dibromochloromethane, vinly chloride, chloromethane, butyl benzly-phthalate, gamma-BHC (lindane),
1,1,2-trichloroethane, bromoform, 1,1-dichloroethane, alpha-BHC, parthion, delta-BHC
Mixtures of organic compounds
- In many instances, the original contamination was a mixture of related components that co-exist normally in a commercial product
- PCBs (Arochlor1242 has 42% chlorine overall but contains biphenyl congeners having 1 through 6 Cl substituents with 80% having 3, 4, or 5 Cl substituents)
- PAHs (in tars, asphalts, and petroleum sludges)- Various petroleum distillation fractions
Boiling range of fraction(oC) # of C per molecule Use
<20
20-60
60-100
40-200
175-325
250-400
Nonvolatile liquids
Nonvolatile solids
C1-C4
C5-C6
C6-C7
C5-C10
C12-C18
C12 and higher
C20 and higher
C20 and higher
Natural gas
Pet. Ether, solvents
Solvents
Gasoline
Kerosene and jet fuel
Diesel oil
Grease
Parffin was, asphalt
Hydrocarbon composition of gasoline components
• (Hill and Moxey, 1960)
1 1 1 1
3 3 3 3 52 2
4444
55
Straight-run Thermal-cracked Catalytic reformed Catalytic cracked
1: n-alkanes 2:alkenes 3: aromatics 4:isoalkanes 5:cycloalkanes
Troublesome BTEX: benzene (2-5% v/v), toluene(6-7% v/v), ethylbenzene(5% v/v), and xylenes (6-7% v/v) => their relatively high solubility causes them to be the prime water pollutants among the compounds in gasoline.
More complications – Additives: antiknock compds, antioxidants, metal deactivator,Antirust agent, antipreignition agents, upper cylinder lubricants, alcohols, and oxygenates (MTBE => a big problem!)
Mixtures created by codisposal- A common situation of codisposal: the mixture of organic and
inorganic materials in sanitary landfills and in their leachates
Compound
/Parameter
Representative range (mg/L)
Compound
/Parameter
Representative range (mg/L)
K+
Na +
Ca 2+
Mg 2+
Cl-
SO42-
Alkalinity
Fe(total)
Mn
Cu
Ni
200-1200
200-1200
100-3000
100-1500
300-3000
10-1000
500-10000
1-1000
0.01-100
<10
0.01-1
Zn
Pb
Hg
NO3-
NH4+
P as PO4
Organic nitrogen
Total Diss. Org. C
COD
Total Diss. Solids
pH
1-100
<5
<0.2
0.1-10
10-1000
1-100
10-1000
10-1000
1000-90000
5000-40000
4.8
Freeze and Cherry, 1979; Rittmann et al., 1994
Mixtures created by codisposal-Volatile and nonvolatile organic compounds and trace metals found in
groundwater at an air force base (US, CA)
- Chemical-manufacturing facilities: long-term, mixture, very low solubility sludges, unacceptable products, other residues => “gumbo”
Compound Representative range (mg/L)
Compound Representative range (mg/L)
1,1-dichloroethene
Acetone
Methyl ethyl ketone
1,1,1-TCA
TCE
Methyl isobutyl ketone
Vinyl chloride
Dichlorobenzene
Benzene
60
35
25
12
11
5
3.7
2.5
0.17
0.68
Phenols
Tetrachloroethane
t-1,2-dichloroethene
Chromium
Nickel
Zinc
Lead (Pb)
Selenium
Cadmium
0.5
0.07
0.2
0.12
0.10
0.073
0.093
0.049
0.012
Pitra and McKenzie, 1990; Rittmann et al., 1994
Mixtures created by codisposal- US Department of Energy (DOE) sites are unique in that the
contamination of the subsurface often involves complex mixtures of organic and inorganic chemicals, including short- and long-lived radionuclides (USDOE, 1990)
- The degree of complexation with the chelators controls the mobility of the radionuclides, while the biodegradation of the chelators is affected by their complexation to the heavy metals.
Inorganic species Organic species
Radionuclides (plutonium, americium, thorium, uranium, technetium, strontium, cesium-134,137, cobalt-60, europium-152, 154, nickel-63, iodine-129, neptunium-237, radium)
Metals (lead, nickel, chromium, copper, mercury, silver, bismuth, palladium, aluminum)
Others (carbon-nitrogen compounds, nitrite, nitrate)
Organic contaminants (chlorinated hydrocarbons, methyl ethyl ketone, cyclohexanone, tetraphenyl boron, PCBs, PAHs, tributyl phosphate, toluene, benzene, kerosen)
Facilitators (aliphatic organic acids, chelating agents, aromatic acids, solvent, diluent, and chelate radiolysis fragments)