Title: Groundwater Geochemistry in the Alisadr, Hamedan, Western Iran
1Groundwater Geochemistry in the Alisadr,Hamedan,
Western Iran
Aida Asgary NDSU Geol 628 Geochemistry 2010
2Why Groundwater Quality is Important
- In arid and semi-arid regions, agriculture is
limited by the availibility of suitable
irrigation water. - Groundwater is the main source of irrigation and
drinking in these areas.
3Study Area
- Climate of study area is semi-arid.
- The area is characterized by predominance of
metamorphic rocks (sedimentary rocks) - Groundwater has been used for drinking,
agricultural and domestic purposes. - Hydrogeochemical investigation was carried out in
Alisadr area to identify groundwater
geochemistry and its suitability for irrigation
purposes.
4Study Area
5Fifty nine samples were selected.The
results show that major cations in order to
their concentrations are Ca, Mg2,Na,and
K.Among anions Co32-, Hco3, Cl-, and No3- have
the highest concentrations.Besed on dominant
cations and anions water types were found.
6Groundwater Quality, WHO Standards
- World Health Organization Standards
- Based on WHOs drinking water standards, limit
for No3 in drinking water is 50 mg/l. - Concentration of No3 in 15 of the samples were
above the standards. - High values of NO3 are results of agricultural
activities.
7Groundwater Quality, Total Hardness
- Hard water is the water that contains high levels
of dissolved calcium, magnesium. - Hardness 2.5(mg Ca/L) 4.1(mg Mg/L)
- The greater the amount of dissolved minerals in
the water, the harder it is. - mg/L Degree of Hardness. 0 - 75 Soft, 75 - 150
Moderately Hard, 150 - 300 Hard, 300 and up Very
Hard
8Groundwater Quality, Total Hardness
- Ways in which total hardness and water quality
are connected are - Household plumbing.
- Decrease in cleaning ability.
- Water heaters can become less efficient.
- Most of the water samples were in the categoray
of hard and very hardwater.
9Groundwater Quality, SAR
- The sodicity hazard of water is described by
Sodium Adsorption Ratio ( SAR). - High concentrations of Na are undesirable in
water because Na is adsorbed in to the soil
cation exchange sites, causing soil accumulations
to disperse, reducing its permeability.
10Groundwater Quality, SAR
Areas with high SAR, special management with
salinity control may be required, only plants
with good salt tolerance should be selected.
11The Origin of Species
- Compositional relations among dissolved species
can reveal the origin of species and the process
that generated the observed water compositions. - Possitive correlations indicates common resource.
12The Origin of Species
- Negative correlation between Ca and HCO3 shows
that Calcite (CaCO3) can not be the source of Ca. - Calcium and So4 ions in groundwater are provided
mostly by the dissolution of Gypsum(CaSO42H2O) - There is a strong correlation between Na and Cl
that may explain the dissolution of halite(NaCl)
in water can be the source. - Dissolution of Anorthite (CaAl2Si2O8) also can
contribute to Ca ions in groundwater.
13(No Transcript)
14Inverse Modeling
- Inverse modeling is used to estimate sets of
minerals and gases that account for the
differences in composition between the solutions.
At least two solution is needed, but we can add
as many as we want. - Inverse modeling can be used to predict the
changes that may occur in concentration of
elements in the flowpath, by indicating whether a
mineral will disolve or precipitate.
15Inverse Modeling
- Hypothesis
-
- In this study correlation ratios were used to
demonstrate possible origin of species, can
inverse modeling provide the same results?
16Inverse Modeling
-
- 5 water solution were chosen.
- Water solutions show increase in concentration of
elements, with emphasizes on elements that cause
quality problems for water.
17Inverse Modeling
-
INVERSE_MODELING 1 - -solutions
1 5 -
-uncertainty 0.5 0.5 - -phases
-
- Gypsum
- Calcite
- Anorthite
- Halite
-
- -balances
- pH
0.2 0.2 - -tolerance
1e-010 - -mineral_water
true
18Results of Inverse Modeling
- Positive mole transfers show dissolution of a
mineral, and negative mole transfers shows
precipitation of a mineral -
19- 1.
- Phase Mole Transfers Minimum
Maximum - Gypsum 9.770e-004 0.000e000
0.000e000 CaSO42H2O - Calcite -3.565e-004 0.000e000
0.000e000 CaCO3 - Anorthite 3.840e-005 0.000e000
0.000e000 CaAl2Si2O8 - Halite 1.797e-003
0.000e000 0.000e000 NaCl - 2.
- Phase Mole Transfers Minimum
Maximum - Calcite -3.565e-004
0.000e000 0.000e000 CaCO3 - Anorthite 3.840e-005 0.000e000
0.000e000 CaAl2Si2O8 - Halite 1.796e-003
0.000e000 0.000e000 NaCl - 3.
- Phase Mole Transfers Minimum
Maximum - Gypsum 9.770e-004 0.000e000
0.000e000 CaSO42H2O - Anorthite 1.336e-005 0.000e000
0.000e000 CaAl2Si2O8 - Halite 1.797e-003
0.000e000 0.000e000 NaC -
- 4.
20Results of Inverse Modeling
- Results indicates the dissolution of gypsum,
anorthite and halite and precipitation od
calcite. - Based on the results origin of species are found,
and they support the results in the article.
21Thank You