groundwater chemistry in faryab river water provides...

5
NORPLAN Course 2.1. Hydrochemical data interpretation. Lecture 8 June 2014 David Banks, Holymoor Consultancy Ltd. / NORPLAN 1 Groundwater chemistry in Faryab by: David Banks, Hydrogeologistand thermogeologist NORAD supported project in MRRD: Capacity Building and Institutional Cooperation in the field of Hydrogeology for Faryab Province , Afghanistan NORPLAN River water provides clear evidence of evapoconcentration Maimana River 0 100 200 300 400 500 600 700 800 0.00 0.02 0.04 0.06 0.08 0.10 0.12 0.14 0.16 Latitude north from origin (°) Electrical conductivity- field (µS/cm) 0 0.2 0.4 0.6 0.8 1 1.2 1.4 1.6 1.8 2 2.2 2.4 Discharge (m3/s) Electrical conductivity (µS/cm) Discharge (m3/s) River water provides clear evidence of evapoconcentration River water provides clear evidence of evapoconcentration Maimana River 0.9 1 1.1 1.2 1.3 1.4 1.5 1.6 1.7 0 0.02 0.04 0.06 0.08 0.1 0.12 0.14 0.16 Latitude north from origin (°) Concentration factor Ca Mg Na K Cl SO4 Br Sr Li B As Se U Cl Na Br SO4 Mg Sr B Se U Li K Ca As Maimana River -8.2 -8.1 -8.0 -7.9 -7.8 -7.7 -7.6 -7.5 0.00 0.02 0.04 0.06 0.08 0.10 0.12 0.14 0.16 Latitude from origin (north) δ18O (‰) -47.8 -47.6 -47.4 -47.2 -47 -46.8 -46.6 -46.4 -46.2 δ2H (‰) Maimana δ18O Maimana δ2H

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NORPLAN Course 2.1. Hydrochemical data interpretation.

Lecture 8

June 2014

David Banks, Holymoor Consultancy Ltd. / NORPLAN 1

Groundwater chemistry in Faryabby: David Banks, Hydrogeologist and thermogeologist

NORAD supported project in MRRD:Capacity Building and Institutional Cooperation in the field of Hydrogeology for Faryab

Province , Afghanistan

NORPLAN

River water provides clear evidence

of evapoconcentration

Maimana River

0

100

200

300

400

500

600

700

800

0.00 0.02 0.04 0.06 0.08 0.10 0.12 0.14 0.16Latitude north from origin (°)

Ele

ctr

ica

l co

nd

uc

tiv

ity

- fi

eld

S/

cm)

0

0.2

0.4

0.6

0.8

1

1.2

1.4

1.6

1.8

2

2.2

2.4

Dis

cha

rge

(m

3/s

)

Electrical conductivity (µS/cm) Discharge (m3/s)

River water provides clear

evidence of

evapoconcentration

River water provides clear

evidence of

evapoconcentration

Maimana River

0.9

1

1.1

1.2

1.3

1.4

1.5

1.6

1.7

0 0.02 0.04 0.06 0.08 0.1 0.12 0.14 0.16

Latitude north from origin (°)

Co

nce

ntr

ati

on

fa

cto

r

Ca

Mg

Na

K

Cl

SO4

Br

Sr

Li

B

As

Se

U

Cl

Na

Br

SO4

Mg

Sr

B

Se

U

Li

K

Ca

As

Maimana River

-8.2

-8.1

-8.0

-7.9

-7.8

-7.7

-7.6

-7.5

0.00 0.02 0.04 0.06 0.08 0.10 0.12 0.14 0.16

Latitude from origin (north)

δ1

8O

(‰

)

-47.8

-47.6

-47.4

-47.2

-47

-46.8

-46.6

-46.4

-46.2

δ2

H (

‰)

Maimana δ18O Maimana δ2H

NORPLAN Course 2.1. Hydrochemical data interpretation.

Lecture 8

June 2014

David Banks, Holymoor Consultancy Ltd. / NORPLAN 2

and stable isotopes provide clear evidence

of evapoconcentration

-80

-75

-70

-65

-60

-55

-50

-45

-40

-11 -10 -9 -8 -7 -6

δ18O (‰)

δ2

H (

‰)

Shirin Tagab River

Maimana River

Andkhoi groundwater

Bilchiragh groundwater

Gurziwan groundwater

Khani Chahar Baghgroundwater

Kohistan groundwater

Qaramqol groundwater

Qaysar groundwater

Qurgan groundwater

Shirin Tagab

River

Maimana River

Maimana

rainfall

Evaporation

Salinity

Salinity profiles appear

to show potential for

infiltration of fresher

river water into aquifers

...and this is confirmed by maps

Maimana area

Islam Qala area

Arsenic (As)

Only a single sample from Faryab exceededthe WHO (2011) guideline of 10 µg/L,from Khani Chahar Bagh district. Thenext highest concentration is a singlesample at 5.1 µg/L in Qurgan district.

There is a slight tendency to increasingconcentrations of arsenic ingroundwater to the north.

Arsenic

EC 1998 Directive:< 10 µg/L

WHO (2011): Provisional guideline< 10 µg/L

25-percentile in Faryab = 0.46 µg/L (N=132)

50-percentile in Faryab = 0.70 µg/L (N=132)

90-percentile in Faryab = 1.31 µg/L (N=132)

NORPLAN Course 2.1. Hydrochemical data interpretation.

Lecture 8

June 2014

David Banks, Holymoor Consultancy Ltd. / NORPLAN 3

Antimony

(Sb)

The antimony concentrations in the 132 groundwater samples from Faryab do notapproach concentrations warranting health concern. The maximum recorded was0.52 µg/L from a dug well in Andkhoi region. There is a weak tendency toincreasing concentrations towards the north.

Antimony

EC 1998 Directive:< 5 µg/L

WHO (2011): Guideline < 20 µg/L

25-percentile in Faryab = 0.07 µg/L (N=132)

50-percentile in Faryab = 0.10 µg/L (N=132)

90-percentile in Faryab = 0.25 µg/L (N=132)Barium (Ba)

There is a clear trend to decreasing concentrations of barium in groundwater to thenorth. It is believed that this is related to suppression of barium solubility bybarite (BaSO4) saturation. The highest recorded barium concentration in Faryab is218 µg/L, in a dug well in Kohistan.

Barium

EC 1998 Directive:No limit set

WHO (2011): Guideline < 700 µg/L

25-percentile in Faryab = 14 µg/L (N=132)

50-percentile in Faryab = 18 µg/L (N=132)

90-percentile in Faryab = 52 µg/L (N=132)

Boron (B)� 14 of the 132 groundwaters sampled in Faryab exceed the recommended WHO

(2011) Guideline value of 2400 µg/L, which is set from a human health perspective. The highest concentration of 7760 µg/L was from a groundwater from Andkhoi district.

� Boron can be toxic to some plant species in smaller concentrations, making high-boron water unsuitable for irrigation of some species. For example, water containing more than 300 µg/L can be phytotoxic to sensitive plants such as avocado, bean or apple (Nable et al. 1997).

Boron

EC 1998 Directive:< 1000 µg/L

WHO (2011): Guideline < 2400 µg/L

25-percentile in Faryab = 178 µg/L (N=132)

50-percentile in Faryab = 859 µg/L (N=132)

90-percentile in Faryab = 2474 µg/L (N=132)

Chromium

(Cr)� The highest recorded chromium concentration in Faryab is 37 µg/L, from a dug well in

Bilchiragh, below the WHO provisional health-based Guideline level of 50 µg/L.

� There is no clear geographical trend in the chromium concentrations, both Bilchiragh and Khani Chahar Bagh districts exhibit median chromium concentrations well above most other districts.

Chromium

EC 1998 Directive:< 50 µg/L

WHO (2011): Provisional guideline< 50 µg/L

25-percentile in Faryab = 0.49 µg/L (N=132)

50-percentile in Faryab = 1.52 µg/L (N=132)

90-percentile in Faryab = 10.9 µg/L (N=132)

NORPLAN Course 2.1. Hydrochemical data interpretation.

Lecture 8

June 2014

David Banks, Holymoor Consultancy Ltd. / NORPLAN 4

Fluoride (F-)

� In Faryab, the range of fluoride concentrations in groundwater is largely within an optimum window.

� Only six of the 132 samples exceed the WHO Guideline concentration of 1.5 mg/L, with the highest value of 2.3 mg/L occurring in a dug well in Qurgandistrict.

Fluoride

EC 1998 Directive:< 1.5 mg/L

WHO (2011): Guideline < 1.5 mg/L

25-percentile in Faryab = 0.3 mg/L (N=127 samples above dl)

50-percentile in Faryab = 0.56 mg/L (N=127 samples above dl)

90-percentile in Faryab = 1.13 mg/L (N=127 samples above dl)

Nitrate (NO3-)

� 20 of the 132 (15%) Faryab groundwater samples exhibited nitrate concentrations exceeding 50 mg/L. The highest value was an enormous 1147 mg/L from a dug well in Andkhoi, although a worrying 9 out of 132 samples exhibited nitrate concentrations in excess of 100 mg/L.

� The samples exceeding the WHO (2011) guideline value almost all came from the four northern districts around Andkhoi.

Nitrate

EC 1998 Directive:<50 mg/L (as NO3-)

WHO (2011): Guideline value <50 mg/L (as NO3-)

25-percentile in Faryab = 9.0 mg/L (N=132)

50-percentile in Faryab = 13.8 mg/L (N=132)

90-percentile in Faryab = 62mg/L (N=132)

Potassium

(K)� When potassium is plotted against nitrate, it is found that the highest potassium

concentrations tend to coincide with the highest nitrate concentrations. It is unclear if this is simply a reflection of mutual evapoconcentrative effects or whether it is due to a common derivation in infiltrating sewage effluent (for example) - or, quite possibly, both.

0.1

1

10

100

1000

10000

0.1 1 10 100 1000

Potassium (mg/L)

Nitr

ate

(m

g/L

)

Potassium

EC 1998 Directive:No guideline set

WHO (2011): Occurs at concentrationswell below those of health concern

25-percentile in Faryab = 4.2mg/L (N=132)

50-percentile in Faryab = 12.1 mg/L (N=132)

90-percentile in Faryab = 44mg/L (N=132)

Selenium

(Se)� Of the 132 Faryab groundwater samples, four samples (3%) exceed the WHO (2011)

provisional guideline of 40µg/L, while 30 samples (23%) exceed the EC limit of 10 µg/L. The highest concentrations are typically from the four northern districts and also from Bilchiragh.

� The highest individual value of 98 µg/L was, however, from a spring in Gurziwan district.

Selenium

EC 1998 Directive:<10 µg/L

WHO (2011): Provisional guideline<40 µg/L

25-percentile in Faryab = 0.8 µg/L (N=132)

50-percentile in Faryab = 4.8 µg/L (N=132)

90-percentile in Faryab = 14.8 µg/L (N=132)

NORPLAN Course 2.1. Hydrochemical data interpretation.

Lecture 8

June 2014

David Banks, Holymoor Consultancy Ltd. / NORPLAN 5

Silicon

Si = 0.3321T + 3.0054

R2 = 0.0711

0

5

10

15

20

25

30

35

40

45

10 12 14 16 18 20 22 24 26 28

Temperature (°C)

Sili

con (

mg

/L)

Si = 1.104Ln(Na) + 2.9869

R2 = 0.1629

0

5

10

15

20

25

30

35

40

45

1 10 100 1000 10000

Sodium (mg/L)

Sili

con (

mg

/L)

Faryab samples typically contain 5-10 mg/L Si. Concentrations significantly in excess of 10 mg/L only occur in a few locations in the northern districts, especially in Qurgan and Khani ChaharBagh.There is a weak correlation between silicon concentration and temperature and a slightly stronger one with sodium concentration.

Uranium (U)� In Faryab, 26 of 132 samples (20%) exceed the WHO (2011) provisional guideline value of 30

µg/L, exclusively in the northern districts. The highest recorded uranium concentration was 62 µg/L from dug wells in Qurgan and Andkhoi.

Uranium

EC 1998 Directive:No guidelineprovided

WHO (2011): Provisional guideline<30 µg/L

25-percentile in Faryab = 3.7 µg/L (N=132)

50-percentile in Faryab = 16.2 µg/L (N=132)

90-percentile in Faryab = 41 µg/L (N=132)

Uranium (U)

Sulphate = 61.214 U - 28.521

R2 = 0.8092

Chloride = 23.623 U + 95.576

R2 = 0.4909

0

1000

2000

3000

4000

5000

6000

0 10 20 30 40 50 60 70Uranium (µg/L)

Su

lph

ate

or

ch

lori

de

(m

g/L

)

Sulphate correlation

Chloride correlation

Possible complexation with sulphate

Correlation with salinityMuch of the hydrochemistry of Faryab is driven by evapoconcentrative

processes (and possibly, dissolution of evaporite minerals)....

A correlation coefficient of +1 indicates a perfect positive correlation

A correlation coefficient of 0 indicates no correlation

A correlation coefficient of -1 indicates a perfect negative correlation

-0.5

-0.4

-0.3

-0.2

-0.1

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

EC Mg Na Cl SO4 Br Li U Ca B Sr Rb 18O HCO3 K Y Sb F NO3 2H Se As Ba

Parameter

Co

rrela

tio

n c

oeff

icie

nt

(r)

EC

Cl