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Towards a Baltic Sea Region Strategy in Critical ... - Helsinki.fi

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CRITICAL INFRASTRUCTURE PROTECTION IN THE BALTIC SEA REGION<br />

of these areas is done by <strong>Region</strong>al Environment Centres and the high quality maps<br />

of the groundwater areas are the basis for protection.<br />

Concern<strong>in</strong>g groundwater protection, the most important are class I areas and<br />

especially groundwater works and the catchments around them. The studied Hanko<br />

aquifer is locally a very important groundwater area and belongs to class I. Also<br />

the groundwater areas that are potential for new groundwater works are signi<strong>fi</strong>cant<br />

for protection. In the Hanko aquifer the most important area for protection is the<br />

area of the Hopearanta water works. <strong>Sea</strong>rch<strong>in</strong>g for new water resources to supply<br />

Hanko could be done by drill<strong>in</strong>g new produc<strong>in</strong>g wells <strong>in</strong> a deeper location and<br />

further from the coast. The shallow groundwater aquifer is thickest <strong>in</strong> NW-SE<br />

trend from the L<strong>in</strong>dnäsudden area (Figure 6). Toward the ma<strong>in</strong>land, the thickness<br />

of the sand and gravel deposit is up to 58 m and the groundwater depth range<br />

between less than 3 and 12 m below the surface. Suf<strong>fi</strong>cient <strong>in</strong>formation of<br />

sedimentation pattern of the sand and gravel formations of the groundwater aquifer<br />

would support the best location for the new wells and optimize the groundwater<br />

supply <strong>in</strong> the long term.<br />

The use of arti<strong>fi</strong>cially recharged groundwater is <strong>in</strong>creas<strong>in</strong>g <strong>in</strong> many parts of<br />

F<strong>in</strong>land. However, the arti<strong>fi</strong>cial recharge could be very dif<strong>fi</strong>cult for the Hanko<br />

area, due to the lack of close water resources. This would cause a high <strong>in</strong>vestment<br />

for the Hanko Town.<br />

Crystall<strong>in</strong>e bedrock forms the basement of the younger deposits and is<br />

distributed throughout the Hanko pen<strong>in</strong>sula. The depth of bedrock varies from<br />

30m below sea level to the surface level. Groundwater <strong>in</strong> the bedrock is<br />

accumulated along the fracture zones. The drill<strong>in</strong>g operations to explore these<br />

groundwater resources are certa<strong>in</strong>ly more expensive than the shallow groundwater.<br />

Drilled bedrock groundwater wells <strong>in</strong> coastal areas also face the potential risk of<br />

the saltwater <strong>in</strong>trusion or relict salt water from the former Littor<strong>in</strong>a <strong>Sea</strong>.<br />

A plan concern<strong>in</strong>g groundwater protection <strong>in</strong> Hanko was prepared <strong>in</strong> 1997<br />

and was updated <strong>in</strong> 2005 (Harju 1997; Maa ja Vesi 2005). The plan was extensive<br />

and consists of a description of groundwater conditions, groundwater resources,<br />

potential risk functions and proposal for actions, groundwater quality, groundwater<br />

monitor<strong>in</strong>g, and recommendations <strong>in</strong> restrictions of land use, provisions for crisis<br />

and actions <strong>in</strong> emergency. It is aimed as a base plan and regular procedure for a<br />

groundwater protection practice.<br />

To protect shallow groundwater aquifers along the coastl<strong>in</strong>e, groundwater<br />

monitor<strong>in</strong>g is needed and this should be done for both of groundwater quantity and<br />

quality. The monitor<strong>in</strong>g of groundwater levels <strong>in</strong> shorel<strong>in</strong>e areas, especially <strong>in</strong> the<br />

area nearby the ma<strong>in</strong> water work also requires <strong>in</strong>formation on the sea level. As the<br />

shallow groundwater <strong>in</strong> Hanko area is vulnerable to the <strong>in</strong>trusion of seawater, a<br />

rout<strong>in</strong>e monitor<strong>in</strong>g will m<strong>in</strong>imize the risk, e.g. chloride is an <strong>in</strong>dicator of the<br />

<strong>in</strong>trusion of seawater. Monitor<strong>in</strong>g will keep the groundwater quality situation <strong>in</strong><br />

general updated. The remediation of groundwater is enormous and expensive<br />

work, so it is better to know the situation before the contam<strong>in</strong>ation reaches the<br />

water works’ wells. Moreover, the monitor<strong>in</strong>g will provide basic <strong>in</strong>formation of<br />

the groundwater condition and the groundwater budget balance between use,<br />

discharge and recharge and also on pump<strong>in</strong>g control. In Hanko the monitor<strong>in</strong>g of<br />

groundwater levels <strong>in</strong> observation wells around the water works is carried out, but<br />

the water quality <strong>in</strong> these wells is not monitored.<br />

210 NORDREGIO REPORT 2007:5

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