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Sustainable water supply in
Swedish coastal areas – possibilities
and challenges

Bosse Olofsson
Royal Institute of Technology, KTH
NGL Annual Meeting at Äspö 2013-11-07
• 50% of the world’s population concentrates to a 60km
wide coastal zone
• Huge water stress along the coastal zone
• Swedish coast stretches >2400km
Climate change (IPCC 2013)
•
•
•
•
•
•

Locally higher precipitation
>2oC increase in temperature to 2100
Dry periods occur more often
Longer dry periods
Most energy stored in sea
Sea level rise (>3.2 mm/year)
(IPCC 2013)
Swedish climate changes?

Model for precipitation and temperature changes until 2100
Source: Rossby Center, SMHI 2012
There are several model scenaries pointing towards similar direction
Climate change in Sweden 2050•
•
•
•
•
•

Increased prec.(but at least bigger variations)
Increased evapotranspiration
Longer vegetation season
Longer periods of drought
Increased competition of water
Increased costs for water treatment
Changed number of days
per year with drough to
2100

Days/year

Källa: SMHI 2013
We will need to store water for
much longer periods than today
The question is where?.....
Swedish specific coastal problems
Bare rock outcrops

Small reservoirs

Concentration of houses
Bad existing sewage systems

High hydraulic heterogeneity

Water chemical problems (Cl, Rn, U, F)

Rapid flows

Increasing water demand
Attractive environment
200 m

Fertilization
Pollution

Coastal erosion
Areas with scarcity of
groundwater in
sweden (for water
supply with sufficient
quantity and quality)

Clay
Sand

(SGU 2009)

Till
Rock

Sand and gravel
A bedrock with high storage
capacity but sensitive to
seawater intrusion
Shear fracture, partly coated with minerals
The flow possibility of each
fracture depends on its

•genesis
•weathering conditions
•mineral filling
•rock stresses

•From top

•From side
Kinematic
porosity in
different units

Bedrock (0.001-0.05%)
Clay (0.01-0.1%)
Till (3-5%)

Well

Sand (10-40%)
Water (100%)

Well

0.001 - 0.05%
Shear fractures
Usually we
have limited
amount of
data,
especially
high quality
data
Uses data from
•SGU
•SMHI
•Lantmäteriet
Example of method for increasing the storage
called”groundwater dams”
Groundwater recharge

Draining tubes

Bentonite or
plastic liner
Dug or drilled well

Bedrock
Clay
Till or sand and gravel
Development of
methods to clarify
suitable places for
localization of
subsurface dams

Figure 10. Vulnerable zones (encircled) of Boda-Kalvsvik.

Based on water
balances and
aquifer deliniation
in GIS
Topographic Wetness Index (TWI) of Boda-Kalvsvik.
Shortage of groundwater,
often leads to deterioration
of groundwater quality

• Natural

Rn

NO3-

Bacteria

geological conditions (e.g.
metals, pH, radon, alkalinity…)
• Induced changes(e.g. salinization)
Na+• Pollutants (e.g. cadmium)
Cl-

Rn

ClNa+

Na+ Cl-

Baltic Sea
Älgö – Stockholm archipelago
Water supply
Sewage

What is the impact from sewage infiltration?
Soil volume for infiltration for 1 family (ca 500 l/d)

Sand
(1-2 m3/d)

Till
(15-20 m3/d)

=> big problems in
exploitational areas.
How can we get
turnover time of 60
days?

Bedrock (1500-2000 m3/d)
Example 1: Nitrate and ammonium
Development of a risk assessment scenario at e.g Tynningö

Ramsö

Tynningö
Vulnerability of nitrate pollution of wells
Example 2: Radon, radium and uranium
N

län (n=5666) N

Stockholm county
Radon content in
wells in the county
of Stockholm

11%

Radon risk areas
calculated using
kriging.

27%

20km

40km

15%

nnar i Stockholms
666)

%

>1000

(White areas have
too few wells)

0km

20km

40km

500-1000
100-500
<100

>1000

47%
N=5666

500-1000
100-500
<100

Rn conc. (Bq/L)
0 to 100
100 to 500
500 to 1000
1000 to 64000

1000

Rn (Bq/L)

0km

500

100

0
Testing of method

(median value)

RV-value

(2209 wells)

A high correlation observed
between median radon
concentration and median
RV- value.

Each point is representative of an area of 25 x 25 km2
Prediction of radon content in drilled wells using GIS

RV-method

Prediktion 2209 wells

FRV > 0

: Low risk

-5 < FRV < 0 : Medium risk
FRV < -5

: High risk
Example 3: Prediction of groundwater quality in private wells at Gotland

(Pirnia & Olofsson 2013)
Prediction of groundwater quality

Based on statistical analysis (ANOVA, PCA) using chemical
data, geological and topographical data
(Pirnia & Olofsson 2013)
Future research need related to water
supply in hard rock areas
There is a strong need for robust assessment methods for
planning and decision support locally and regionally

• How to estimate storage and capacity without extensive
drilling

• How to get a measure of heterogeneity and
anisotropy without extensive test pumping
• How to characterize groundwater chemical quality,
origin and turnover time with limited amount of data
• How to deliniate bedrock aquifer extension and set
boarder conditions with sparce of data
• How to differentiate origin of compounds with many
different sources (chloride, radon, lead, arsenic)
Concluding strategy
• We are convinced that the
best way to develop models
and techniques for
generalized estimations of
groundwater resources
using sparce of data is to
develop and test such
models where there are lots
of data available, such as the
NGL (a.o stored in SICADA)
Thanks

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Sustainable coastal water challenges

  • 1. Sustainable water supply in Swedish coastal areas – possibilities and challenges Bosse Olofsson Royal Institute of Technology, KTH NGL Annual Meeting at Äspö 2013-11-07
  • 2. • 50% of the world’s population concentrates to a 60km wide coastal zone • Huge water stress along the coastal zone • Swedish coast stretches >2400km
  • 3. Climate change (IPCC 2013) • • • • • • Locally higher precipitation >2oC increase in temperature to 2100 Dry periods occur more often Longer dry periods Most energy stored in sea Sea level rise (>3.2 mm/year) (IPCC 2013)
  • 4. Swedish climate changes? Model for precipitation and temperature changes until 2100 Source: Rossby Center, SMHI 2012 There are several model scenaries pointing towards similar direction
  • 5. Climate change in Sweden 2050• • • • • • Increased prec.(but at least bigger variations) Increased evapotranspiration Longer vegetation season Longer periods of drought Increased competition of water Increased costs for water treatment
  • 6. Changed number of days per year with drough to 2100 Days/year Källa: SMHI 2013
  • 7. We will need to store water for much longer periods than today The question is where?.....
  • 8. Swedish specific coastal problems Bare rock outcrops Small reservoirs Concentration of houses Bad existing sewage systems High hydraulic heterogeneity Water chemical problems (Cl, Rn, U, F) Rapid flows Increasing water demand Attractive environment 200 m Fertilization Pollution Coastal erosion
  • 9. Areas with scarcity of groundwater in sweden (for water supply with sufficient quantity and quality) Clay Sand (SGU 2009) Till Rock Sand and gravel
  • 10. A bedrock with high storage capacity but sensitive to seawater intrusion
  • 11. Shear fracture, partly coated with minerals The flow possibility of each fracture depends on its •genesis •weathering conditions •mineral filling •rock stresses •From top •From side
  • 12. Kinematic porosity in different units Bedrock (0.001-0.05%) Clay (0.01-0.1%) Till (3-5%) Well Sand (10-40%) Water (100%) Well 0.001 - 0.05% Shear fractures
  • 13. Usually we have limited amount of data, especially high quality data Uses data from •SGU •SMHI •Lantmäteriet
  • 14. Example of method for increasing the storage called”groundwater dams” Groundwater recharge Draining tubes Bentonite or plastic liner Dug or drilled well Bedrock Clay Till or sand and gravel
  • 15.
  • 16. Development of methods to clarify suitable places for localization of subsurface dams Figure 10. Vulnerable zones (encircled) of Boda-Kalvsvik. Based on water balances and aquifer deliniation in GIS Topographic Wetness Index (TWI) of Boda-Kalvsvik.
  • 17. Shortage of groundwater, often leads to deterioration of groundwater quality • Natural Rn NO3- Bacteria geological conditions (e.g. metals, pH, radon, alkalinity…) • Induced changes(e.g. salinization) Na+• Pollutants (e.g. cadmium) Cl- Rn ClNa+ Na+ Cl- Baltic Sea
  • 18. Älgö – Stockholm archipelago Water supply Sewage What is the impact from sewage infiltration?
  • 19. Soil volume for infiltration for 1 family (ca 500 l/d) Sand (1-2 m3/d) Till (15-20 m3/d) => big problems in exploitational areas. How can we get turnover time of 60 days? Bedrock (1500-2000 m3/d)
  • 20. Example 1: Nitrate and ammonium Development of a risk assessment scenario at e.g Tynningö Ramsö Tynningö
  • 21. Vulnerability of nitrate pollution of wells
  • 22. Example 2: Radon, radium and uranium N län (n=5666) N Stockholm county Radon content in wells in the county of Stockholm 11% Radon risk areas calculated using kriging. 27% 20km 40km 15% nnar i Stockholms 666) % >1000 (White areas have too few wells) 0km 20km 40km 500-1000 100-500 <100 >1000 47% N=5666 500-1000 100-500 <100 Rn conc. (Bq/L) 0 to 100 100 to 500 500 to 1000 1000 to 64000 1000 Rn (Bq/L) 0km 500 100 0
  • 23. Testing of method (median value) RV-value (2209 wells) A high correlation observed between median radon concentration and median RV- value. Each point is representative of an area of 25 x 25 km2
  • 24. Prediction of radon content in drilled wells using GIS RV-method Prediktion 2209 wells FRV > 0 : Low risk -5 < FRV < 0 : Medium risk FRV < -5 : High risk
  • 25. Example 3: Prediction of groundwater quality in private wells at Gotland (Pirnia & Olofsson 2013)
  • 26. Prediction of groundwater quality Based on statistical analysis (ANOVA, PCA) using chemical data, geological and topographical data (Pirnia & Olofsson 2013)
  • 27. Future research need related to water supply in hard rock areas There is a strong need for robust assessment methods for planning and decision support locally and regionally • How to estimate storage and capacity without extensive drilling • How to get a measure of heterogeneity and anisotropy without extensive test pumping • How to characterize groundwater chemical quality, origin and turnover time with limited amount of data • How to deliniate bedrock aquifer extension and set boarder conditions with sparce of data • How to differentiate origin of compounds with many different sources (chloride, radon, lead, arsenic)
  • 28. Concluding strategy • We are convinced that the best way to develop models and techniques for generalized estimations of groundwater resources using sparce of data is to develop and test such models where there are lots of data available, such as the NGL (a.o stored in SICADA)