- Page 1 and 2: 4 'Hydrochemistry and energy storag
- Page 6 and 7: 4 Corrosion 5 Some conclusions Refe
- Page 8 and 9: AUTHORS 0. Andersson VIAK AB P.O. B
- Page 10 and 11: INTRODUCTION J.W. Lyklema This volu
- Page 12 and 13: THE INTERNATIONAL ENERGY AGENCY AND
- Page 14 and 15: 3 THE IEA The International Energy
- Page 16 and 17: In addition to projects in the doma
- Page 18 and 19: THE RELATION BETWEEN AQUIFER THERNl
- Page 20 and 21: 3 VIABILITY ATES systems contribute
- Page 22 and 23: Figure 4 Temperature fluctuations o
- Page 24 and 25: 10°C between two cycles. We have t
- Page 26: groundwater quality so seriously th
- Page 29 and 30: developed within Annex VI (Environm
- Page 31 and 32: carbonate phase, the use of a high-
- Page 33 and 34: generally contain sufficient organi
- Page 35 and 36: precipitation from solutions at nea
- Page 37 and 38: of the water for storage. These tre
- Page 39 and 40: the higher ATES temperatures. There
- Page 41 and 42: One of our research objectives is t
- Page 43 and 44: COUDRAIN-RIBSTEIN, A. and GOBLET, P
- Page 45 and 46: SPOSITO, G, and LeVESQUE, C.S. ; 19
- Page 47 and 48: saturation with respect to calcite
- Page 49 and 50: system would influence the hydroche
- Page 51 and 52: columns were heated from 11°C to 9
- Page 53 and 54:
(Table 2), clearly shows that the i
- Page 55 and 56:
Plate 1: CaC03 grain from first cen
- Page 57 and 58:
decrease in ca2+ activity, to reach
- Page 59 and 60:
y thermodynamic equilibrium calcula
- Page 61 and 62:
HOLM, T.R., EISENREICH, S.J., ROSEN
- Page 63 and 64:
INTRODUCTION The use of aquifers fo
- Page 65 and 66:
As can be seen "cloggingn has been
- Page 67 and 68:
specific capacity of the well and c
- Page 69 and 70:
the water being injected. The reaso
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Figure 5 Simplified stability diagr
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3.4 Clogging by organic slime Clogg
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4 CORROSION 4.1 Forms of corrosion
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When halogens are known to be prese
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available on the market. SOME CONCL
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BIOGEOCHEMICAL ASPECTS OF AQUIFER T
- Page 84 and 85:
In accordance with Figure 1 mangane
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at a neutral pH is kinetically dete
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of such biocides used against desul
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HYDROGEOCHEMICAL TRANSPORT MODELLIN
- Page 92 and 93:
The complexity of the models with a
- Page 94 and 95:
The comparison shows that inclusion
- Page 96 and 97:
the component O2 (Oxygen) has been
- Page 98 and 99:
The results of a recent solubility
- Page 100 and 101:
The neutral "exchangeable" complex
- Page 102 and 103:
SrC12 elution of Delft sediment, sh
- Page 104 and 105:
The saturation ratios can be used i
- Page 106 and 107:
Recovered water in the long term te
- Page 108 and 109:
Cumulat~ve Flow (103m3) Cumulative
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Dissolution of silicates is in much
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KIRKNER, D.J., and REEVES, H.; 1988
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WATER TREATMENT AND ENVIRONMENTAL E
- Page 116 and 117:
Table 1 Ove~iew of chemical treatme
- Page 118 and 119:
calculated with a computer model th
- Page 120:
Figure 1 Schematic representation o
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addition shows an increase in neces
- Page 125 and 126:
Table 4 summarizes the primary envi
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wsts for this overdimensioning may
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_? Primary circuit Figure 7 Reactor
- Page 131:
Problems with iron precipitation ca
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RESEARCH ON HYDROCHEMISTRY AND WATE
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ANNEX XI L - -1 I Figure 1 Relation
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stores. F. To test selected water t
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(Fe, Ca, Mg) solid solutions. The p
- Page 142 and 143:
corrosion and scaling rates under d
- Page 144:
the industry. For this treatment no
- Page 149 and 150:
Water nuisance. Proceedings of Tech
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No. 36 No. 37 No. 38 Urban storm wa