Final Exam Flashcards
(57 cards)
Describe how pH could affect the behaviour of cationic contaminants in soils?
High pH more binding
Describe how pH could affect the behaviour of anionic contaminants in soils?
High pH less binding/sorption
How does OM in soils affect the binding of cationic/anionic contaminants?
OM incr. cationic binding
How does OM in soils affect the binding of hydrophobic organic chemicals?
Because it has uncharged domains it affects hydrophobic chemicals.
Explain how increasing pH affects soil surface charge..
pH affects soil surface charge through de-protonation of OM and edges of clay minerals. If surface becoming more negative, the anionic containments get bound even less strongly so they get repelled from surface more. If pH is low and the negative charge is low, anions will bind more strongly.
What might control the bioavailability of a poly-aromatic hydrocarbon (PAH) in soil?
OM sorption of metals
What might control the bioavailability of PCBs in soil?
PCBs sorbed by uncharged OM
High Kow/benzine rings
Why do we analyse blank samples in the lab?
to determine any contamination or ambient concentrations in the laboratory that may affect/confound results.
Why do we filter and acidify water samples before metal analysis in the lab?
to remove particulate matter and to ensure non-degradation and also to ensure non-adsorption of the metals to the container
Replication gives us a good way to measure accuracy of chemical analyses? T/F
False
Replication gives us a good way to measure precision of chemical analyses? T/F
True
Using Cr as an example, explain how redox is important in affecting contaminant mobility in the soil.
Redox affects Cr
as Cr6 —> mobile & toxic
Cr3 - immobile and non-toxic
Using As as an example, explain how redox is important in affecting contaminant mobility in the soil
answer
Which of the following species of Cu is most toxic?
Cu-DOM
Cu0
Cu2+ —> free copper ion
CuCl3-
Explain how you might measure the partitioning coefficient for a metal in soil?
Contaminant in solution
mix with soil at incr. concentrations
measure
Calculate Kd
Kd kg/L = solid phase [contaminant]/solution phase [contaminant]
also can do;
total phase [contaminant]/solution phase [contaminant]
Explain how you might measure the pKa for a chemical?
Ka = products/reactants
pKa= -log(Ka)
or 1/2way dissociation point
perform titration to produce curve
equivalence point between two inflection points is pKa
Explain how you might measure the partitioning coefficient for a chemical in soil?
Contaminant in solution
mix with soil at incr. concentrations
measure
Calculate Kd
Kd kg/L = solid phase [contaminant]/solution phase [contaminant]
also can do;
total phase [contaminant]/solution phase [contaminant]
An organic acid has spilled at the Urrbrae Wetland. The chemical has a pKa of 9.2 and pH of water and sediments is 6.5. What form is contaminant likely to be in? Is it more likely to partition to water or to the sediment? Will it bioaccumulate easily?
What if pKa is 3.2 and pH is 7.0?
pKa>env= unionised/undissociated (uncharged)
pKa
Lead has spilled into a small farm dam, and the [Pb] is 0.6 mg/L. The sediment has a Kd value of 200 for Pb - what concentration do you expect in the sediment?
What if [Pb] is 6 mg/L?
Kd = solid/solution
200 = solid/6
=
Copper sulphate has been used in a small farm dam to control algae, and the [Cu2+] is 1 mg/L. The sediment has a Kd value of 500 for Cu2+ - what concentration do you expect in the sediment?
What measurements might you need to take on the water to determine the PEC to examine if a risk is potentially present?
Kd = solid/solution
500 = solid/1
= 500
Need to measure free Cu ion
Or can measure DOM in water, know total Free Cu. and use model to predict free Cu.
Analysing [Cu] in river waters or dam waters by inductively coupled plasma mass spectrometry is a good way to determine how toxic the Cu might be. T/F?
False - complexed by organic (Fe?) so not as free Cu
Using examples, discuss the differences between:
- Acute and chronic toxicity
- EC50 and NOEC
- Hazard quotient and PNEC
- Free metal cation and complexed metal cation
- Hydrophobic and hydrophilic
- Antagonistic and Synergistic
- Accuracy and precision
- Acute and chronic toxicity:
- EC50 and NOEC:
- Hazard quotient and PNEC:
- Free metal cation and complexed metal cation:
- Hydrophobic and hydrophilic: water-hating & water-loving
- Antagonistic and Synergistic: interaction between contaminant mixtures (incr.=synergistic, decr.=antagonistic)
- Accuracy and precision:
You have received sediment and soil samples from a client to analyse for inorganic element concentrations. The client would like to know total
concentrations for the following elements present in the samples at mg/kg
concentrations - iron, calcium, sodium, potassium, sulfur, manganese; and
µg/kg concentrations - cadmium, arsenic, copper and zinc. What information
can you supply to the client on the digestion and instrumental analysis
techniques that will be used to determine all these elemental concentrations?
Acid digestion - use strong acids to digest samples to get into correct form for ICP-OES for [high] or ICP-MS for [lower].
Also, expecting to see measures of contamination through analysis of blanks.
Use replication in the lab & accuracy assessment through digestion of a certified reference material (CRM).
If pesticides in water body - use HPLC, GSMS, LCMS.
If pesticide is difficult to make volatile during analysis, must use liquid chromatography and either UV detection or mass spectrometry detection.
If it is easily made volatile can use GC or MS or absorption UV/Infra-red
1st days lectures - davina. Analysis methods.
You have been asked to develop a risk assessment for contaminants in agricultural fertilisers. Describe the steps you would take to carry out this risk assessment.
First need to know:
1. what rates are fertiliser used
2. what are contaminants in the fertilisers being used
Need this to determine a Predicted Env. Concentration (PEC).
To do a risk assessment, need PEC and PNEC:
Go to literature and find ecotoxicity threshold values for those contaminants in those soil type/s. If rare/few toxicity data (e.g. Yttrium) might have to use assessment factor to come up with PNEC.
If get enough data can do species sensitivity distribution and use HC5 and do risk characterisation as a hazard quotient for all contaminants.
If HQ>1 = will have to look at reducing the primitive level in the fertiliser.
Do a risk pathway analysis also.