01.09.2015 Views

News letter Dam edition

News letter Dam edition

News letter Dam edition

SHOW MORE
SHOW LESS
  • No tags were found...

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

Ingeokring <strong>News</strong><strong>letter</strong><br />

8.2 Effects of dissolution below the canals and the irrigation<br />

area<br />

During the helicopter survey made in June 1986 it was observed<br />

that at many places where gypsum is present near<br />

the earth surface (for example near the camp site), sinkholes<br />

of varying size (0.1-3 m diameter) are present (Photos 5 and<br />

6).<br />

It may be expected that dissolution along the main canal<br />

and primary and secondary canals also could take place<br />

giving rise to leakage and surface subsidence.<br />

The situation below a canal can be analysed as follows<br />

(Figure 14, from James & Lupton (1978)):<br />

dM<br />

- = K dA(Cs<br />

- C)<br />

dt<br />

where M is the amount of gypsum dissolved at time t, A is<br />

the surface area of gypsum in contact with fresh water and C<br />

is the concentration of dissolved gypsum in the water (since<br />

this is constantly refreshed this may be taken as zero).<br />

The linear retreat of the gypsum surface below a canal may<br />

also be written as -dZ/dt (see Figure 14) and the amount of<br />

gypsum dissolved per unit of time:<br />

dM dZ<br />

- = .A.ρ<br />

dt dt<br />

Combining (6) and (7), taking C=0:<br />

dZ K d C s<br />

- =<br />

dt ρ<br />

Again K d and C s have to be estimated and depend on flow<br />

rate, temperature and concentration of sodium chloride in<br />

the groundwater.<br />

Example 1. In the case of a silt layer between massive gypsum<br />

and the canal (Figure 14):<br />

Take K d =10 -4 m/s and a low hydraulic gradient, then v~10 -5<br />

m/s. If the silt contains salts, then the groundwater may<br />

have dissolved sodium chloride (NaCl) in it and estimates of<br />

K d =5x10 -5 m/s and C s =10 kg/m 3 may apply. This gives<br />

(Equation 8):<br />

dZ -4<br />

5 × 10<br />

-<br />

- = = 2.16 × 10<br />

7<br />

dt 2320<br />

(6)<br />

(7)<br />

(8)<br />

= 6.8m / year<br />

Example 2. If no sodium chloride is present, then K d =10 -5 m/s<br />

and C s =2.5 kg/m 3 and<br />

dZ 2.5 × 10<br />

-<br />

- =<br />

= 1.08 × 10<br />

8<br />

dt 2320<br />

Example 3. If free flowing canal water is flowing directly<br />

over a gypsum rock surface, with a velocity of 0.5 m/s, then<br />

at 23 °C: K d =4x10 -5 m/s (James & Lupton, 1978). Since hardly<br />

any sodium chloride is present in Wabi Shebelle water,<br />

C s =2.5 kg/m 3 .<br />

-5<br />

-5<br />

dZ (4 × 10 ).(2.5)<br />

-<br />

- =<br />

= 4.3 × 10<br />

8<br />

dt 2320<br />

These values are high and show that protection against contact<br />

with fresh water is necessary. They also explain why<br />

sinkholes may develop rapidly in the wadis of the irrigation<br />

area during the rainy season, the only time when water is<br />

flowing over these areas. Consider a locality where silt containing<br />

some sodium chloride salts is present above gypsiferous<br />

rock (the conditions of example 1). Say a localised<br />

flow of water during the rainy period occurred for a period<br />

of two weeks, then a retreat of the underlying gypsum surface<br />

of 6.8 m/year x (2/52) = 0.26 m could occur. This is sufficient<br />

for a small sinkhole to develop (Photo 6).<br />

These calculations can be considered as examples. Comparable<br />

calculations for different rock types are shown in Table<br />

1. The calculated solution rates are regularly confirmed by<br />

observations and reported in literature (James et.al., 1981).<br />

Using actual site measurements of flow velocities and electrical<br />

conductivity measurements of the water and groundwater,<br />

these could be tailored to the real situation.<br />

8.3 Design of monitoring program<br />

= 0.34 m / year<br />

= 1.36m / year<br />

Before the actual construction starts, many data can be<br />

gathered and monitored that would aid in the refining of<br />

the prediction of dissolution behaviour of gypsiferous rocks<br />

and soils under hydraulic structures in the irrigation area.<br />

Monitoring of piezometric levels in the piezometric stations<br />

at the dam site, together with temperature and electrical<br />

conductivity measurements will give information on hydraulic<br />

conductivity and also whether there is any fluctuation of<br />

the salinity of the groundwater. Also the variation in C<br />

(solubility) over the site and in the irrigation area can be<br />

obtained this way (by similarly measuring the electrical conductivity<br />

of the groundwater in other boreholes).<br />

During and after construction it is highly advisable to monitor<br />

the groundwater, to be aware of any changes in conditions.<br />

After construction, the groundwater should be con-<br />

<strong>Dam</strong> <strong>edition</strong> | Double Issue 2007/2008 | 36

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!