Print version. Sorption of PPCPs. Organic compounds in water and wastewater. Soonmi Kim. CEE 697z - Lecture #24

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Transcription:

Print version Sorption of PPCPs Organic compounds in water and wastewater Soonmi Kim

Outline Introduction Studies; sorption of PPCPs

Introduction Sorption? Sorption is a physical and chemical process by which one substance becomes attached to another Adsorption Accumulation of the molecular species at the surface rather than in the bulk of the solid or liquid Absorption Assimilation of molecular species throughout the bulk of the solid or liquid

Introduction

Introduction Wastewater treatment systems

Factors affecting Sorption 1) Sorbent properties 2) Sorbate properties 3) Solution properties

Factors affecting Sorption 1) Sorbents properties 2) Sorbate properties 3) Solution properties

Sorbents 1.Types of sorbent 1) Biosolids (Sludge) - Primary sludge - Secondary sludge 2) Soils - Sand - Silt - Clay 3) Coagulants - Al, Fe, or Mn complex 2. Surface area of sorbents

Factors affecting Sorption 1) Sorbent properties 2) Sorbate properties 3) Solution properties

Sorbate properties Molecular Weight (MW) - in general, as increase MW, solubility decreases, adsorption increases - as increase MW, diffusivity decreases, so rate of transport decreases - at very high MW, may exclude some compounds from small pores Polarity - in general, if more polar, more hydrophilic, less absorption (stronger interaction with polar H 2 O) - as more non-polar, more hydrophobic, more absorption (i.e. increase in aliphatic carbon chain length for carboxylic acids results in increased absorption) - number and type of substituent atoms or groups on organic carbon structure affects extent of absorption Dr. Tobiason; Physical CEE 697z &- Chemical Lecture #24 treatment processes

Factors affecting Sorption 1) Sorbents properties 2) Sorbate properties 3) Solution properties

Solution properties (cont.) ph - affects ionization of sorbate and surface of sorbent - in general, as ph decreases, sorption increases - uncharged sorbates adsorb more than charged (ionized) sorbates Ionic Strengh - in general, more sorption as ionic strength increases - better adsorption of DOC as increase Ca +2, Na + Temperature - extent of sorption increases as temperature decreases - rate of sorption decreases as temperature decreases Dr. Tobiason; Physical CEE 697z &- Chemical Lecture #24 treatment processes

Solution properties Competing sorbates - sorbate with stronger affinity (binding) for surface can displace sorbate with weaker affinity - most real waters involve mixtures of sorbates - changes in mixture can affect sorption - for a heterogeneous sorbate measured by a composite parameter such as TOC (or COD), extent of sorption can depend on initial concentration used in batch experiment Presence/absence of dissolved oxygen - sorption capacity increased in presence of O 2 (aq) Dr. Tobiason; Physical CEE 697z &- Chemical Lecture #24 treatment processes

Possible interactions W. J. Weber et al. Sorption CEE 697z phenomena - Lecture in #24 subsurface system(1991)

Outline Introduction Studies; sorption of PPCPs

Sorption coefficient (K d ) - The ratio of the concentrations of a compound in the sorbent phase and in the solution phase at equilibrium; Linear isotherm K d = C sorbed /C dissolved C sorbed : concentration of solbate in sorbent (μg/kg) C dissolved : concentration of solbate in solution (μg/l) q =Mass adsorbed / Mass of adsorbent Other isotherms Freundlich Langmuir

Standard methods for K d and K F determination 1) Column displacement studies 2) Batch sorption expreriments

Factors affecting determination of sorption coefficient 1. Phases associated sorption - Solid phase - PPCPs in aqueous phase - DOM (Dissolved organic Matter) in aqueous phase 2. PPCPs properties - Hydrophobic PPCPs - Non-hydrophobic ionisable PPCPs

K d in soils Yu Fang (2011)

Bo Pan (2009)

Sorption between PPCPs (VPs) and DOM Johannes Tolls(2001)

Hydrophobicity (Cont.) - Karickhoff (1979) reported that K d of environmental chemicals are strongly correlated to the organic carbon content (f oc (%)) - During(2002), Bowman(2002), Holthaus(2002), Loffredo(2006), Maskaoui(2007), and Uslu(2008) reported that both Freundlich sorption parameter K F and Linear sorption parameter K d of PPCPs are found to be positively related to organic carbon content - Most of PPCPs are moderately hydrophobic compounds (Bo Pan;2009) So, K OC = K d f oc K oc : organic carbon partition coefficient (L/kg) K d : linear sorption coefficient (L/kg) f oc : fraction of organic carbon (%)

Hydrophobicity (Cont.) - Franco(2008) and Karickhoff (1979) reported the K oc is correlated to the K ow (Octanol-water distribution coefficient) Log K ow = positive : Log K ow = negative : Hydrophobic Non-hydrophobic - Sablijic (1995) found that the K oc for non-hydrophobic and ionisible compounds is ph-dependent - And, Sablijic (1995) determined the correlation between the K oc and the K ow depending on physical and chemical properties of organic compouns

Aleksandar Sabljic (1995)

Sorption of ph-dependent non-hydrophobic PPCPs Schaffer (2012)

Fabrice Gritti (2009)

Sorption of ph-dependent non-hydrophobic PPCPs Schaffer (2012)

Sorption of ph-dependent non-hydrophobic PPCPs at ph = 8.23 Martinez-Hernandez (2014) Basic compounds : Highest K d by strong interactions with negativelycharged surface Acidic compounds : Moderate K d by ion exchange with cations on surface or physical interaction among polar molecules Neutral compounds : Lowest K d by negligible sorption affinity

K d in sludges Barret (2011)

K d in sludges Thomas A. Ternes (2004)

Removal of PPCPs in WWTP R. Salgado (2011)

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