270 likes | 333 Views
Explore the role of colloids in groundwater transport, including attachment mechanisms and filtration processes. Understand the challenges to DLVO theory and the implications for stabilizing colloidal suspensions. Learn about straining, mass transfer equations, and how sorbed species influence colloid stability.
E N D
Colloid Transport and Colloid-Facilitated Transportin Groundwater Introduction DLVO Theory Stabilization/Transport/Aggregation/Filtration Applications B.C. Williams, 2009
Colloids Defined • Particles with diameters < 10 micron, < 0.45 μ • Mineral – detrital(as deposited) or autigenic (from matrix) • Layer silicates • Silica Rich Particles • Iron oxides • Organic – e.g. humic macromolecules • Humic macromolecules • Biocolloids – bacteria and viruses
Groundwater Transport in General • Usual conceptual model for groundwater transport as follows: • Dissolved phase • Adsorbed phase (onto soil/rock matrix) • How a given chemical partitions into these two phases is represented by the partition coefficient, Kd.
Groundwater Transport Including Colloid-Facilitated Transport • Three phases • Dissolved phase • Adsorbed phase (onto soil/rock matrix) • Adsorbed onto mobile particles
Terminology – Mechanisms for Retention • Attachment – adhesion – sorption • Function of collision, collector efficiency, sticking efficiency • Mechanical filtration – complete retention of particles that are larger than all of the soil pores (formation of filter cake) • Straining – physical trapping in geometric corners • Particles can be smaller than smallest pore openings • Requires grain-grain contact • Only occurs in some fraction of soil pore space, transport occurs elsewhere
Strained versus Mechanically Filtered dp/d50 .005
Background • Clean-bed Filtration Theory • Depends on mechanism of attachment / detachment • Deviation from Clean Bed Filtration Theory • Unfavorable attachment condition; neg-neg • Fine sand and large colloids (dp/d50 .005)
Explanations for Deviation from CFT • Attachment w/ porous media charge variability – Johnson and Elimelech, 1995 • Attachment w/ heterogeneity in surface charge characteristics of colloids – Li et al, 2004 • Attachment w/ deposition of colloids in a secondary energy minimum – Tufenkji et al. 2003, Redman et al., 2004 • All of the above – Tufenkji and Elimelech, 2005 • Attachment w/ straining – Foppen et al, 2005, Bradford et al, 2006a, b
Theory (cont.) Aqueous Phase Colloid Mass Balance Equation- Bradford et al., 2003 Where: θw = volumetric water content [-] t = time [T] C = colloid concentration in the aqueous phase [N L-3] JT = total colloid flux [N L-2 T-1] EattSW = colloid attachment mass transfer between solid/water phases [N L-3 T-1] EstrSW = colloid straining mass transfer between solid/water phases [N L-3 T-1]
Colloid-Facilitated Groundwater Transport Solid matrix mobile colloid Adsorbed Dissolved
DLVO TheoryDerjaguin, Landau, Verwey, Overbeek • The stabilityof a homogeneous colloidal suspension depends upon (stability=dispersed) • Van der Waals attractive forces (promote aggregation) http://en.wikipedia.org/wiki/Van_der_Waals_force • Electrostatic repulsive forces that drive particles apart • If electrostatic dominates, particles are electrostatically stabilized (dispersed)
Figures to Explain DLVO • Colloid DLVO Theory – • http://www.malvern.com/LabEng/industry/colloids/dlvo_theory.htm • Good figures including ionic strength definition http://wefcol.vub.ac.be/wefcol/lectures/hanoi/h1.pdf
DLVO - stabilized • Colloids are stabilized (in suspension) when: • Double layers expand (by decreasing electrolyte concentration, decreasing ionic strength • Net particle charge 0 • Colloids coagulate/aggregate when: • Double layer shrinks because of increasing ionic strength
Challenges to DLVO • Hot controversy in literature on whether spheres of like charge always repel. Experimental evidence that colloidal electrostatic interactions include a long-ranged attractive component. • http://physics.nyu.edu/grierlab/gold13b/node1.html • http://physics.nyu.edu/grierlab/publications.html
Stabilization – and sorbable species • Sorbed species can influence surface charge, and therefore stability (end of DLVO discussion) • Sorbed species can also be mobilized if the colloid is mobilized through the soil/rock matrix (colloid-facilitated transport!)
Colloid Transport in General(Saturated and Unsaturated GW) • Detachment / Mobilization / Suspension • Transport • Aggregation / Filtration / Straining
Detachment/Mobilization/Suspension • Colloids can detach from matrix • Biogeochemical weathering • Precipitation from solution (thermodyn’) • Biocolloids or humics flushed from shallow zones • If cementing agents dissolve • If stable aggregates deflocculate
Transport • More likely if colloid is neg’. charged, because most soil/rock matrices are neg’. • Transport optimal if: • Slow interpore transport rate – few collisions with side surfaces • High velocities in preferential pathways • In preferential pathways, may have faster travel times than ambient gw flows
Stabilization/Aggregation • Aggregation occurs depending upon charge, and when double layer shrinks due to increasing ionic strength
Filtering / Straining • Physical filtering – due to size, geometry • Physicochemical straining – surface chemical attraction to matrix • Cementation agents (iron oxides, carbonates, silica)
Applications • Many engineering ramifications of passage versus filtration • Colloid-facilitated transport – how a low-solubility (strongly-sorbed!) contaminant can travel miles from the source
Engineering Applications • Wastewater – sand filters – removal is good, too-small particles clog • Roads – clogging of drain filters force buildup failure • Dams – matrix piping erosion 26% of earth dam failures ref: Reddi, 1997
Engineering Applications, cont. • Petroleum Extraction – permeability reduction termed “formation damage” • Slurry Walls – very fines filtered by fines is considered a benefit • Lining of Lakes/Reservoirs – ditto ref: Reddi, 1997
Colloid-Facilitated Transport • When a highly sorptive contaminant (constituent) is adsorbed onto colloids • Contaminant of interest must have as high or higher affinity to sorb as other possible constituents • Colloid may have “patches” of surface coatings (ferric, aluminum or manganese oxyhydroxides) that are best sites
Colloid Transport in the Unsaturated Zone • Colloids may be strained, or retarded, if moisture content reduced so that water films have thickness less than colloid diameter • Colloids may sorb to the air/water interface • Called partitioning – same Kd.concept
References Johnson, P.R., Sun, N., and Elimelech, M., 1996. “Colloid Transport in Geochemically Heterogeneous Porous Media”, Environmental Science and Technology, 30, 3284-3293. Reddi, L. N., 1997. Particle Transport in Soils: Review of Significant Processes in Infrastructure Systems. J. Infrastructure Systems. 3, 78-86. McCarthy, J.F., Zachara, J.M., 1989. “Subsurface Transport of Contaminants”. Environmental Science and Technology, 23, 496-502. Wan, J. T.K. Tokunaga, 1998. "Measuring partition coefficients of colloids at air-water interfaces", Environ. Sci. Technol, 32, p3293-3298, Wan, J., Wilson, J.L., 1994. Colloid transport in unsaturated porous media. Water Resources Research. 30, 857-864.