8.7 freshwater/saltwater interaction in coastal aquifers

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8.7 Freshwater/Saltwa ter Interaction in coastal aquifers

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Page 1: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

8.7 Freshwater/Saltwater Interaction

in coastal aquifers

Page 2: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Coastal aquifers

Density difference,

zone of mixing (diffusion)

Interface

Saltwater front

Page 3: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Island in an ocean

Freshwater lens

Moving interface

Page 4: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Saltwater intrusion

Pumping of groundwater diverts groundwater from flowing toward sea seawater movement toward aquifer

Causes deterioration of water quality in coastal aquifers

Page 5: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Locating the Interface

Ghyben-Herzberg relation

Page 6: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Ghyben-Herzberg Relation

Weight of column of freshwater extending from water table to interface

weight of column of saltwater extending from sea level to the same depth

Hydrostatic conditions:

=

Page 7: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Ghyben-Herzberg Relation:

f = freshwater density = 1.0g/cm3

s = saltwater density = 1.025g/cm3

z = height of saltwater column hf = hydraulic head above sea level

hf + z = height of freshwater column

s f fgz g h z ( )

z hf

s ff

z h f40

Page 8: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Ghyben-Herzberg Relation:

The depth to the interface between freshwater and saltwater is approximately

40 times the height of the water table above sea level

z h f40

Page 9: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Position of the interface

xKz

Qs f

f

1

2

2( )

'

LKb

Qs f

f

1

2

2( )

'

x

Page 10: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Example 8.4

f = 1.0 g/cm3, s = 1.025 Water levels in two wells far from shoreline : 0.5 m , 1.0 m Distance between two wells = 1000 m

K = 10 m/d, b = 50 m

Calculate:1. Length of saltwater wedge2. Position of interface

Page 11: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Example 8.4, contd.

L

Page 12: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Example 8.4, solution

Discharge from aquifer to the sea per unit length of shoreline:

Q’ = Kb dh/dx

= (10 m/d)(50 m)(1.0 m -0.5 m)/1000 m

= 0.25 m3/d/m

Interface = = 0.5 z2

Length of protrusion = = 1250 m

xKz

Qs f

f

1

2

2( )

'

LKb

Qs f

f

1

2

2( )

'

Page 13: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Methods for limiting seawater intrusion

1. Controls on pumping: Reducing pumping rates Reducing number of pumped wells

2. Artificial recharge through ponds Using imported water or reclaimed wastewater

Page 14: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Methods for limiting seawater intrusion

3. Pumping trough barriers Using a series of pumped wells to remove

saltwater and form a potentiometric barrier

4. Freshwater injection To establish a seaward hydraulic gradient

Page 15: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Case study: saltwater intrusion control in Biscayne Aquifer, Florida

Page 16: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Upconing of Interface

zQ

Kdf

s f

'

( )

2

Q d K s f

fmax .

( )

0 6 2

Upconing = rise of interface as a result of groundwater pumping

Rise of interface (upconing) = z =

Maximum permitted pumping rate =Qmax

Page 17: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

Example 8.5

The distance from the base of a pumping well to the freshwater-saltwater interface is 100 m, the pumping rate is 3000 m3/day, and the hydraulic conductivity is 10 m/d.

What will be the position of the interface? What’s the maximum permitted pumping rate? --------------------SOLUTION------------------

Rise = z = (3000 m3/d)(1.0 g/cm3)/(2x3.1416)(100m)(10 m/d)(1.025 g/cm3 – 1.0 g/cm3)

= 13.26 m Q max = 4.7x103 m3/day

Page 18: 8.7 Freshwater/Saltwater Interaction in coastal aquifers

HW

8.4

8.5