corrosive species and scaling in wells at olkaria ... - Orkustofnun

corrosive species and scaling in wells at olkaria ... - Orkustofnun corrosive species and scaling in wells at olkaria ... - Orkustofnun

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D = HCl [ mHCl ] [ mHCl ] Temperature dependence is given by (Simonson and Palmer, 1993): log D HCl = -13.4944 – 934.466/T – 11.0029×logρ + 5.4847×logT where T = The temperature in Kelvin, as before; and ρ = The density of solvent (g/cm 3 ). l v LogHCl aqueous (ppm) logHCl aqueous (ppm) 1 0.1 0.01 0.001 0.0001 1E-005 10 100 1000 10000 100000 Chloride (ppm) FIGURE 18: Aquifer water HCl concentrations vs. aquifer water chloride concentrations of selected wells in the study areas 1 0.1 0.01 0.001 0.0001 1E-005 Olkaria East Olkaria West Olkaria North East Olkaria Domes Reykjanes Svartsengi Nesjavellir Olkaria East Olkaria West Olkaria North East Olkaria Domes Reykjanes Svartsengi Nesjavellir 5 6 7 8 pH FIGURE 19: Aquifer water HCl concentrations vs. aquifer water pH of selected wells in the study areas The density of the dilute waters from Olkaria and Nesjavellir was calculated using thermodynamic properties of water and steam given by the computer code TAFLA (Bjarnason and Björnsson, 1995). Densities for Reykjanes and Svartsengi brines were calculated using densities of saturated sodium chloride solutions provided by Potter and Brown (1977). The calculated concentrations of HCl in the aquifer waters of the study areas are presented in Table 4 of Appendix A and depicted in Figures 18, 19, 20 respectively as a function of aquifer water chloride concentrations, pH and temperature. The concentrations of HCl aq increases with increasing aquifer water Cl concentrations, decreasing aquifer water pH and increasing aquifer temperature. The water in producing aquifers of the Olkaria wells contain HCl in the range between ~ 1×10 -5 ppm and ~ 5×10 -4 ppm. The aquifer water HCl concentrations in Reykjanes and Svartsengi are much higher, ranging between ~0.32 and ~ 0.81 ppm and ~3×10 -2 and ~8×10 -2 ppm, respectively. At Nesjavellir, the HCl in the aquifer waters is in the range ~ 3×10 -5 - 5×10 -5 pm for the selected wells. There is a variation in HCl concentrations in the Olkaria well fluids of about an order of magnitude with the exception of fluid from one well, well OW-34 which has a slightly higher HCl concentration, than other Olkaria well fluids (Figure 18). At Olkaria, the variations in the HCl concentration can be attributed to the 24

variation in chloride concentration, pH and temperature. The chloride concentration in the aquifer waters at Olkaria varies between ~ 40 ppm and ~ 2000 ppm in the aquifer and the aquifer pH from ~ 6 to 8. Aquifer temperatures vary between ~ 200° and 300°C. The wide range in the concentrations of chloride, pH and temperatures at Olkaria contribute to the wide range of HCl aq concentrations. At Nesjavellir, HCl in the aquifer fluids is very low due to the very low chloride in the aquifer water, ~ 150 ppm and a pH of the aquifer fluids of ~ 8. Aquifer temperatures at Nesjavellir range between ~ 270° and 300°C for the wells studied. LogHCl aqueous (ppm) 1 0.1 0.01 0.001 0.0001 1E-005 Olkaria East Olkaria West Olkaria North East Olkaria Domes Reykjanes Svartsengi Nesjavellir The high HCl concentrations in the aquifer water in Reykjanes and Svartsengi are very high compared to those of Olkaria and Nesjavellir. The high HCl concentration in the aquifer water at Reykjanes and Svartsengi is a result of high chloride concentrations and low pH in the aquifer waters of these two fields. The chloride concentrations in the waters of these two fields are ~ 20,000 ppm and ~ 13,000 respectively and the pH of the aquifer water in the range of ~ 5.1 to ~5.6. Temperatures in Reykjanes range between 250° and 320°C. At Svartsengi the temperatures are almost homogenous, being in the narrow range of 235° and 240°C. 180 200 220 240 260 280 300 Temperatures °C FIGURE 20: Aquifer water HCl concentrations vs. aquifer temperature (°C) of selected wells in the study areas 100 10 1 0.1 OW-901 Olkaria Domes OW-301 Olkaria West OW-306 Olkaria West OW-20 Olkaria East OW-30 Olkaria East OW-714 Olkaria North East OW-34 Olkaria East OW-709 Olkaria North East SV-05 Svartsengi SV-11 Svartsengi RN-10 Reykjanes RN-11 Reykjanes NJ-14 Nesjavellir NJ-22 Nesjavellir Upon boiling the dissolved HCl is partly transferred to the steam that forms. The quantity transferred is affected by several parameters. The most important ones include changes in pH, which occur during boiling, and the temperature of the fluid mixture. Figure 21 shows how HCl concentrations in steam decrease during one step adiabatic boiling for all the wells considered in the present study. LogHCl in vapour (ppm) 0.01 0.001 0.0001 1E-005 1E-006 1E-007 1E-008 1E-009 Early steam is somewhat enriched in HCl relative to the source aquifer water. Upon continued boiling the cause of the decrease is largely due to an increase in pH upon boiling and by changes in the value taken by the HCl distribution coefficient. Because it is 80 120 160 200 240 280 320 Temperature °C FIGURE 21: HCl in vapour formed by several steps of single-step adiabatic boiling of selected wells in the study areas temperature dependent the distribution coefficient, is affected by the decrease in temperature when the fluids cool by adiabatic steam loss. Changes in the Cl content of the water, which are caused by steam formation, have small effect. The HCl concentrations in steam are ~ 10 3 -10 5 times more for Reykjanes 1E-010 25

vari<strong>at</strong>ion <strong>in</strong> chloride concentr<strong>at</strong>ion, pH<br />

<strong>and</strong> temper<strong>at</strong>ure. The chloride<br />

concentr<strong>at</strong>ion <strong>in</strong> the aquifer w<strong>at</strong>ers <strong>at</strong><br />

Olkaria varies between ~ 40 ppm <strong>and</strong> ~<br />

2000 ppm <strong>in</strong> the aquifer <strong>and</strong> the aquifer<br />

pH from ~ 6 to 8. Aquifer temper<strong>at</strong>ures<br />

vary between ~ 200° <strong>and</strong> 300°C. The<br />

wide range <strong>in</strong> the concentr<strong>at</strong>ions of<br />

chloride, pH <strong>and</strong> temper<strong>at</strong>ures <strong>at</strong><br />

Olkaria contribute to the wide range of<br />

HCl aq concentr<strong>at</strong>ions. At Nesjavellir,<br />

HCl <strong>in</strong> the aquifer fluids is very low due<br />

to the very low chloride <strong>in</strong> the aquifer<br />

w<strong>at</strong>er, ~ 150 ppm <strong>and</strong> a pH of the<br />

aquifer fluids of ~ 8. Aquifer<br />

temper<strong>at</strong>ures <strong>at</strong> Nesjavellir range<br />

between ~ 270° <strong>and</strong> 300°C for the <strong>wells</strong><br />

studied.<br />

LogHCl aqueous (ppm)<br />

1<br />

0.1<br />

0.01<br />

0.001<br />

0.0001<br />

1E-005<br />

Olkaria East<br />

Olkaria West<br />

Olkaria North East<br />

Olkaria Domes<br />

Reykjanes<br />

Svartsengi<br />

Nesjavellir<br />

The high HCl concentr<strong>at</strong>ions <strong>in</strong> the<br />

aquifer w<strong>at</strong>er <strong>in</strong> Reykjanes <strong>and</strong><br />

Svartsengi are very high compared to<br />

those of Olkaria <strong>and</strong> Nesjavellir. The<br />

high HCl concentr<strong>at</strong>ion <strong>in</strong> the aquifer<br />

w<strong>at</strong>er <strong>at</strong> Reykjanes <strong>and</strong> Svartsengi is a result of<br />

high chloride concentr<strong>at</strong>ions <strong>and</strong> low pH <strong>in</strong> the<br />

aquifer w<strong>at</strong>ers of these two fields. The chloride<br />

concentr<strong>at</strong>ions <strong>in</strong> the w<strong>at</strong>ers of these two fields<br />

are ~ 20,000 ppm <strong>and</strong> ~ 13,000 respectively <strong>and</strong><br />

the pH of the aquifer w<strong>at</strong>er <strong>in</strong> the range of ~ 5.1<br />

to ~5.6. Temper<strong>at</strong>ures <strong>in</strong> Reykjanes range<br />

between 250° <strong>and</strong> 320°C. At Svartsengi the<br />

temper<strong>at</strong>ures are almost homogenous, be<strong>in</strong>g <strong>in</strong><br />

the narrow range of 235° <strong>and</strong> 240°C.<br />

180 200 220 240 260 280 300<br />

Temper<strong>at</strong>ures °C<br />

FIGURE 20: Aquifer w<strong>at</strong>er HCl concentr<strong>at</strong>ions vs.<br />

aquifer temper<strong>at</strong>ure (°C) of selected <strong>wells</strong><br />

<strong>in</strong> the study areas<br />

100<br />

10<br />

1<br />

0.1<br />

OW-901 Olkaria Domes<br />

OW-301 Olkaria West<br />

OW-306 Olkaria West<br />

OW-20 Olkaria East<br />

OW-30 Olkaria East<br />

OW-714 Olkaria North East<br />

OW-34 Olkaria East<br />

OW-709 Olkaria North East<br />

SV-05 Svartsengi<br />

SV-11 Svartsengi<br />

RN-10 Reykjanes<br />

RN-11 Reykjanes<br />

NJ-14 Nesjavellir<br />

NJ-22 Nesjavellir<br />

Upon boil<strong>in</strong>g the dissolved HCl is partly<br />

transferred to the steam th<strong>at</strong> forms. The quantity<br />

transferred is affected by several parameters.<br />

The most important ones <strong>in</strong>clude changes <strong>in</strong> pH,<br />

which occur dur<strong>in</strong>g boil<strong>in</strong>g, <strong>and</strong> the temper<strong>at</strong>ure<br />

of the fluid mixture. Figure 21 shows how HCl<br />

concentr<strong>at</strong>ions <strong>in</strong> steam decrease dur<strong>in</strong>g one step<br />

adiab<strong>at</strong>ic boil<strong>in</strong>g for all the <strong>wells</strong> considered <strong>in</strong><br />

the present study.<br />

LogHCl <strong>in</strong> vapour (ppm)<br />

0.01<br />

0.001<br />

0.0001<br />

1E-005<br />

1E-006<br />

1E-007<br />

1E-008<br />

1E-009<br />

Early steam is somewh<strong>at</strong> enriched <strong>in</strong> HCl<br />

rel<strong>at</strong>ive to the source aquifer w<strong>at</strong>er. Upon<br />

cont<strong>in</strong>ued boil<strong>in</strong>g the cause of the decrease is<br />

largely due to an <strong>in</strong>crease <strong>in</strong> pH upon boil<strong>in</strong>g<br />

<strong>and</strong> by changes <strong>in</strong> the value taken by the HCl<br />

distribution coefficient. Because it is<br />

80 120 160 200 240 280 320<br />

Temper<strong>at</strong>ure °C<br />

FIGURE 21: HCl <strong>in</strong> vapour formed by several<br />

steps of s<strong>in</strong>gle-step adiab<strong>at</strong>ic boil<strong>in</strong>g of<br />

selected <strong>wells</strong> <strong>in</strong> the study areas<br />

temper<strong>at</strong>ure dependent the distribution coefficient, is affected by the decrease <strong>in</strong> temper<strong>at</strong>ure when the<br />

fluids cool by adiab<strong>at</strong>ic steam loss. Changes <strong>in</strong> the Cl content of the w<strong>at</strong>er, which are caused by steam<br />

form<strong>at</strong>ion, have small effect. The HCl concentr<strong>at</strong>ions <strong>in</strong> steam are ~ 10 3 -10 5 times more for Reykjanes<br />

1E-010<br />

25

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