Newest Viewed Downloaded

Release of bentonite colloids into freshwater: Present ideas Presentation at Workshop, June 13, 2007 Ivars Neretnieks Chemical Engineering and Technology KTH

Release of bentonite colloids into freshwater: Present ideas Presentation at Workshop, June 13, 2007 Ivars Neretnieks Chemical Engineering and Technology KTH

Swedish KBS-3 concept

Overview of talk

Background Bentonite gel/sol properties-Colloids 0:th order model for bentonite loss Forces acting on colloid particles Development of swelling and release model

Background and Introduction I

Bentonite buffer around waste canister forms a gel with water and swells Pore water ionic strength influnces Bentonite swelling pressure Low ionic strengths,

Background and Introduction II

Passing fresh GW carries away ions from pore water, PW At Bentonite/GW interface a balance is established between depletion by GW and dissolution of Ca- minerals Minerals with solubility >CCC will replenish PW concentration to maintain gel

High flowrates of meltwater

Fracture intersecting deposition hole

Physical erosion

Shear force Velocity of gel to Decreasing gel concentration. Also influenced by cat-ion in clay Shear force by flowing water on gel “Viscosity” of gel is strongly non-linear at low shear stress: Bingham Fluid

Chemical erosion

At low ionic strength repulsive forces expand the clay and release colloids Gel turns to sol and particles do not flocculate. Sol expands due to repulsive forces between particles, which are carried away by the seeping water

Transport processes at gel/GW interface

Impact of, CCC, Critical Coagulation Concentration

When porewater Ccation

Diffusion of Calcium to passing GW

Notion of Qeq

Water velocity Fracture aperture Diffusivity Water residence time at clay/water interface Qeq is used to visualise rate of mass transfer, mol/s of a solute from clay to seeping water Qeq is the equivalent flowrate, m3/s that carries a solute with the concentration at clay/water interface Obtained by solving the coupled flow and diffusion equations in a fracture

Potential consequences

When PW concentration in bulk clay can be replenished to >CCC from minerals the solubilisation is determined by rate of depletion of the mineral

Example of clay loss

Qeq=0.01 m3/a CCCC= 40 g Ca/m3 Cw=0 NCa=0.4 g Ca/a mCa=0.01 g Ca/g Clay NClay=40 g Clay/a 400 kg Clay/10 000 a

Is the zero’th order model too pessimistic or may it even be optimistic?

Assumption that clay can disperse into passing water What can gravity do? Can clay move sufficiently far into water to be carried away? Can clay particles be filtered in fracture and clog it? Can clay particles be filtered in accessory minerals left behind?

Impact of gravity

Clay in a sub-vertical fracture will be pulled downward in addition to repulsion forces due to electrical charges Could this happen even if PW concentration is above CCC?

Model idea same as for Qeq

Nion=Qeq*Cinterface: Rate of loss of ions Ions move in chemical potential field = Force to disperse Balanced by friction. Gives rate of diffusion Nclay into passing GW Colloids move in chemical potential field Gravity field Inter particle repulsion/attraction forces Balanced by friction. Gives rate of diffusion

Mats Jansson, Nuclear Chemistry, KTH

Mats Jansson Nuclear Chemistry, KTH

Showing 1 - 20 of 65 items Details

Name: 
neretnieks1
Author: 
N/A
Company: 
N/A
Description: 
Release of bentonite colloids into freshwater: Present ideas Presentation at Workshop, June 13, 2007 Ivars Neretnieks Chemical Engineering and Technology KTH
Tags: 
forc | clay | particl | water | model | gel | graviti | concentr
Created: 
6/3/2007 9:22:46 AM
Slides: 
65
Views: 
7
Downloads: 
3
Rating: 
0


Comment



Share this presentation
|

Comments

Share this presentation:

|
Sitemap