Save
Envsci. Contaminants
environmental fate
Save
Share
Learn
Content
Leaderboard
Share
Learn
Created by
ThoughtfulDog43480
Visit profile
Cards (15)
Environmental fate
Can be studied at different scales:
soil
aggregate, through
soil
profile, catchment scale (water) and long range transport (POPs)
View source
Up scaling environmental fate is very challenging
View source
Fate of organic contaminants after emission
1.
Distribution
between different
phases
2.
Transformation
/
degradation
by chemical/biological reactions
3.
Transport
within and between
compartment
(s)
View source
Environmental compartment
Made of 3 phases: gas-liquid-solid
View source
Partitioning coefficient
K1,2 = C1/C2,
Solid
to liquid. The higher the K1,2 coefficient, the more
chemical accumulates
in phase 1 relative to phase 2
View source
Partitioning constant
Henry constant
,
Koa
, Kow
View source
Octanol/water partition coefficient (Kow)
Measures hydrophobicity or
water hating.
If compound goes into
lipid
phase or water, indicates where it will be found in the environment. Higher Kow means higher water hating and more likely to partition into solid phases
View source
Solubility in water
Inverse
relationship with
Kow
: more hydrophobic, less soluble
View source
Distribution coefficients to environmental
solids
are proportional to
Kow
, so high Kow means high bioconcentration factor
View source
Transformation
All reactions in which
chemical bonds
are broken/formed, ideally up to
complete mineralisation
(e.g. CO2, CH4, H2O, SO4)
View source
Transformation processes
Abiotic
: no direct participation of organisms (chemical reactions, photolysis)
Biotic: biologically mediated, rate generally much
higher
, only process for complete
mineralisation
Redox: mediated by microorganisms gaining
energy
from
degradation
No
e- transfer
(e.g. hydrolysis)
View source
Requirements
for
biodegradation
Existence of organisms with degradation potential
Presence of specific degrader
(
s
)
Accessibility of target pollutants
Induction of appropriate degradative enzymes
Availability of appropriate e- acceptors
/
donors
Availability of nutrients
Adequate pH and buffering capacity
Adequate temperature
Absence of toxic or inhibitory substances
View source
DT50
(
half-life
)
Time
required for 50% of a substance to degrade, used as an example of degradation in
soil
View source
POPs have a
DT50
>
2 months
View source
Fate of chemicals in soils and surface water
High Kow
means
sticking to sediment
, high Henry's constant means volatilisation, soluble means travelling with water
View source