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Pollutants and environmental compartments

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Title: Pollutants and environmental compartments


1
Pollutants and environmental compartments
  • 1(ii)
  • Physico-chemical properties of pollutants and
    their influence on their behaviour in the
    environment

2
Aims
  • To provide overview of molecular properties of
    pollutants in the environment
  • Vapour pressure theoretical background,
    molecular interactions governing vapour pressure,
    availability of experimental vapour pressure data
    and estimation methods
  • Activity coefficient and solubility in water
    thermodynamic consideration, effect of
    temperature and solution composition on aqueous
    solubility and activity coefficients,
    availability of experimental data and estimation
    methods

3
Outcomes
  • Students will be able to
  • estimate relevant physico-chemical properties of
    pollutants from their structure
  • predict reactivity of pollutants and possible
    environmental behavior of pollutants

4
Vapour pressure
  • Definition
  • Pressure of a substance in equilibrium with its
    pure condensed (liquid or solid) phase pº
  • Why is it important?
  • Air/water partitioning
  • Air/solid partitioning
  • When is it important?
  • Spills
  • Pesticide application

5
  • Ranges of pº (atm)
  • PCBs 10-5 to 10-9
  • n-alkanes 100.2 to 10-16
  • n-C10H22 10-2.5
  • n-C20H42 10-9
  • benzene 10-0.9
  • toluene 10-1.42
  • ethylbenzene 10-1.90
  • propylbenzene 10-2.35
  • carbon tetrachloride 10-0.85
  • methane 102.44
  • Even though VP is low, gas phase may still be
    important.

6
  • Phase diagram and aggregate state

7
  • Thermodynamic considerations(deriving the vant
    Hoff equation)
  • In equilibrium the change in chemical potential
    in the two systems is equal

where S molar entropy and V molar volume
8
Liquid-vapor equlibrium
  • For a liquid vaporizing, the volume change can be
    assumed to be equal to the volume of gas
    produced, since the volume of the solid or liquid
    is negligible

where ?H12 ?Hvap (gas) or ?Hsub (solid)
energy required to convert one mole of liquid (or
solid) to gas without an increase in T
The vant Hoff equation
9
  • Integration assuming DHvap is constant over a
    given temperature range leads to
  • If the temperature range is enlarged DHvap is not
    constant

Antoine equation
10
Solid-vapor equilibrium
  • For sublimation
  • DHsub DHmelt (25) DHvap (75)
  • Still use liquid phase as reference
  • Hypothetical subcooled liquid liquid cooled
    below melting point without crystallizing

-log p -log p
compound pºs lt Pºl
1,4-dichlorobenzene 3.04 2.76
phenol 3.59 3.41
2255 PCB 7.60 6.64
22455 PCB 8.02 7.40
Important for solubility
11
Molecular interactions affecting vapor pressure
  • Moleculemolecule interactions in condensed phase
    (l or s) have greatest affect on VP
  • strong interactions lead to large DHvap, low VP
  • weak interactions lead to small DHvap, high VP
  • Intermolecular interactions can be classified
    into three types
  • van der Waals forces (nonpolar)
  • Polar forces
  • Hydrogen bonding

12
Vapor Pressure Estimation Technique
based on regression of lots of VP data, best fit
gives
H-bonding ability
size
polarizability
pressure in Pa, where
13
H-bonding ability
14
Refractive index
  • Refractive index (response to light) is a
    function of polarizability

15
Troutons rule
  • At their boiling points, most organic compounds
    have a similar entropy of vaporization
  • exception strongly polar or H-bonding compounds
  • Kistiakowskys expression gives slightly more
    accurate predictions
  • KF 1 for apolar and many monopolar compounds
  • For weakly bipolar compounds (e.g., esters,
    ketones, nitriles), KF 1.04
  • Primary amines KF 1.10, phenols KF 1.15,
    aliphatic alcohols KF 1.30
  • At Tb
  • So, if we know Tb, we can estimate ?Hvap (at the
    boiling point) fairly accurately.

16
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17
Estimating vapor pressure at other T
  • Important DHvap is not constant.
  • Especially if Tb is high (gt 100ºC), the estimate
    of DHvap from Trouton/Kistiakowsky may not be
    valid.
  • Empirically, DHvap is a function of the vapor
    pressure

18
  • From a data set of many compounds, Goss and
    Schwarzenbach (1999) get

19
  • Less empirically, assume DHvap is linearly
    proportional to T (i.e. assume that the heat
    capacity, ?vapCp is constant)
  • Substitution into the Clausius-Clapeyron equation
    and integration from Tb to T gives

20
  • Substitution
    in previous equation gives
  • Generally

21
  • Inserting Kistiakowskys expression, the
    following equation is obtained
  • KF is the Fishtine factor, usually 1, but
    sometimes as high as 1.3
  • OK for liquids with Tb lt 100 ºC
  • High MW compounds, need correction for
    intermolecular forces

(bar)
22
Aqueous Solubility
  • Equilibrium partitioning of a compound between
    its pure phase and water
  • Will lead us to Kow and Kaw

23
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24
Relationship between solubility and activity
coefficient
  • Organic liquid dissolving in water
  • At equilibrium

for the organic liquid phase
for the organic chemical in the aqueous phase
At saturation!
25
  • If we assume xiL 1 and giL 1
  • The relationship between solubility and activity
    coefficient is
  • The activity coefficient is the inverse of the
    mole fraction solubility

for liquids
or
26
  • Solids
  • additional energy is needed to melt the solid
    before it can be solubilized

27
  • Gases
  • solubility commonly reported at 1 bar or 1 atm (1
    atm 1.013 bar)
  • O2 is an exception
  • the solubility of the hypothetical superheated
    liquid (which you might get from an estimation
    technique) may be calculated as

theoretical partial pressure of the gas at that
T (i.e. gt 1 atm)
Actual partial pressure of the gas in the system
28
  • Concentration dependence of g
  • g at saturation ? g at infinite dilution
  • However, for compounds with g gt 100 assume
  • g at saturation g at infinite dilution, i.e.
    solute molecules do not interact, even at
    saturation

29
Molecular picture of the dissolution process
  • The two most important driving forces in
    determining the extent of dissolution of a
    substance in any liquid solvent are
  • an increase in entropy of the system
  • compatibility of intermolecular forces.

30
  • Ideal liquids
  • For ideal liquids in dilute solution in water,
    the intermolecular attractive forces are
    identical, and ?Hmix 0. The molar free energy
    of solution is
  • ?Gs ,?Gmix Gibbs molar free energy of solution,
    mixing (kJ/mol)
  • T?Smix Temperature ? Entropy of mixing
    (kJ/mol)
  • R gas law constant (8.414 J/mol-K)
  • T temperature (K)
  • Xf, Xi solute mole fraction concentration
    final, initial
  • for dilute solutions mole fraction of solvent ? 1

31
  • Nonideal liquids
  • The intermolecular attractive forces are not
    normally equal in magnitude between organics and
    water
  • ?Ge Excess Gibbs free energy (kJ/mol)
  • ?He, ?Se Excess enthalpy and excess entropy
    (kJ/mol)
  • ?He intermolecular attractive forces cavity
    formation (solvation)
  • ?Se cavity formation (size) solvent
    restructuring mixing

32
  • For small molecules, enthalpy term is small ( 10
    kJ/mol)
  • Only for large molecules is enthalpy significant
    (positive)
  • Entropy term is generally unfavorable
  • Water forms a flickering crystal around the
    compound, which fixes both the orientation of the
    water and of the organic molecule

33
Solubility estimation techniques
  • Activity coefficients and water solubilities can
    be estimated a priori using molecular size,
    through molar volume (V, cm3/mol). Molar volumes
    can be approximated
  • Ni number of atoms of type i in j-th molecule
  • ai atomic volume of i-th atom in jth molecule
    (cm3/mol)
  • nj number of bonds in j-th molecule (all types)
  • Solubility can approximated using a LFER of the
    type

34
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35
  • This type of LFER is only applicable within a
    group of similar compounds

36
  • Another estimation technique universal valid
    for all compounds/classes/types

molar volume describes vdW forces
refractive index describes polarity
Vapour pressure
additional polarizability term
cavity term
H-bonding
37
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38
Factors Influencing Solubility in Water
  • Temperature
  • Salinity
  • pH
  • Dissolved organic matter (DOM)
  • Co-solvents

39
  • Temperature effects on solubility
  • Generally
  • as T ?, solubility ? for solids.
  • as T ?, solubility can ? or ? for liquids and
    gases.
  • BUT For some organic compounds, the sign of ?Hs
    changes therefore, opposite temperature effects
    exist for the same compound!
  • The influence of temperature on water solubility
    can be quantitatively described by the van't Hoff
    equation as

40
  • Solids
  • Liquids
  • Gases

41
  • The effect of salinity
  • As salinity increases, the solubility of neutral
    organic compounds decreases (activity coefficient
    increases)
  • Ks Setschenow salt constant (depends on the
    compound and the salt)

typical seawater salt 0.5M
42
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43
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44
  • The effect of pH
  • pH effect depends on the structure of the solute.
  • If the solute is subject to acid/base reactions
    then pH is vital in determining water solubility.
  • The ionized form has much higher solubility than
    the neutral form.
  • The apparent solubility is higher because it
    comprises both the ionized and neutral forms.
  • The intrinsic solubility of the neutral form is
    not affected.

45
  • The effect of DOM
  • DOM increases the apparent water solubility for
    hydrophobic compounds.
  • DOM serves as a site where organic compounds can
    partition, thereby enhancing water solubility.
  • Solubility in water in the presence of DOM is
    given by the relation
  • DOM concentration of DOM in water, kg/L
  • KDOM DOM/water partition coefficient
  • Again, the intrinsic solubility of the compound
    is not affected.

46
  • The effect of cosolvents
  • the presence of a co-solvent can increase the
    solubility of hydrophobic organic chemicals
  • co-solvents can completely change the solvation
    properties of water
  • examples
  • industrial wastewaters
  • gasohol
  • engineered systems for soil or groundwater
    remediation
  • HPLC

47
  • Solubility increases exponentially as cosolvent
    fraction increases.
  • Need 5-10 volume of cosolvent to see an effect.
  • Extent of solubility enhancement depends on type
    of cosolvent and solute
  • effect is greatest for large, nonpolar solutes
  • more organic cosolvents have greater effect
    propanolgtethanolgtmethanol

48
  • Bigger, more non-polar compounds are more
    affected by co-solvents
  • Different co-solvents behave differently,
    behavior is not always linear
  • We can develop linear relationships to describe
    the affect of co-solvents on solubility. These
    relationships depend on the type and size of the
    solute
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