Biomagnification, Bioaccumulation, and Environmental Toxicants Flashcards
Ecotoxicology
study of the fate and effects of toxicants in an ecosystem
-distribution, degradation, eventual fate
matrices
atmosphere, lithosphere, hydrosphere, biosphere
Bioavailability
portion of a toxicant that can potentially be taken up by an organism
Bioaccumulation
concentration in an organism is higher than the concentration in the environment via absorption and ingestion
Bioconcentration
bioaccumulation by absorption only
Bioconcentration factor (BCF)
toxicant concentration in the whole organism or tissue to its concentration in the surrounding environment
-hydrophobic compounds
BCF less than 1
toxicant is actively excluded by the organism
BCF=1
toxicant exhibits no selectivity
BCF greater than 1
toxicant is accumulated within organism at higher quantity than in environment
Biomagnification
chemicals become increasingly concentrated at successively high trophic levels
-ratio of steady-state pollutant concentration in the organism
Trophic dilution
concentrations decrease with increasing trophic level
-rates of contaminant biotransformation and elimination exceed rates of ingestion and assimilation
breakdown in environment
-photolysis
-oxidation
-hydrolysis
(POPs don’t readily do the above 3)
-microbial metabolism
photolysis
high energy photons absorbed by a molecule resulting in the breaking or rearrangement of a covalent bond
oxidation
addition of oxygen
hydrolysis
- addition of water molecule
- common in aquatic systems
Microbial metabolism
- microbes have metabolism mechanisms that are not found in eukaryotic organisms
- non-halogenated pollutants can be broken down fairly rapidly
- dehalogenase enzymes can remove the chlorines form POPs and use remaining carbon backbone as a carbon source
- very slow process, only switch on these genes when they are starving
- occurs more readily in soil, POPs accumulate in the hydrosphere
Dirty Dozen
- banned or being phased out due to the Stockholm Convention of 2001
- Came into effect May 2004
- Very persistent in the environment and many are endocrine disruptors
- DDT and PCBs
Polyhalogenated Aromatic Hydrocarbons
- PCB, PCDD, PCDF
- Highly lipophilic, non-volatile, slow to break down, prone to biomagnification, potential for additive interactions
- Halogens bonded covalently to carbon are rare in nature, more difficult to deal with
Polychlorinated Biphenyls
- Class of compounds
- Slightly different chemical structures called isomers and congeners
- Toxic response depends on the properties of the chemical
- thermal stability, low flammability, low vapour pressure, low acute toxicity, but chronic health effects
- halogenation position affects toxicity (3rd or 4th most)
- Must combine with a specific receptor to initiate a reaction which leads to toxic effects
PCB numbering
- ring with fewest chlorines gets the dash
- 1 is always bonded carbon
- Ortho=next to the bond
- Meta=one over from the bond
- Para=across from the bond
- Multi-ortho congeners more likely to be coplanar and less toxic
- 2 in para position is most toxic