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

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CHAPTER VI: WATER<br />

<strong>in</strong>habitant was then 240 L/d, <strong>in</strong>clud<strong>in</strong>g the <strong>in</strong>dustry. About 60 % of the<br />

groundwater consumption is approximated as household use (SYKE 2007). The<br />

average price of raw water and use payment was 2.30 EUR/m 3 <strong>in</strong> 2001. The<br />

approximated price for water for one person per month was approximately 13<br />

EUR. This <strong>fi</strong>gure excluded the payments of basic charge and payments of<br />

<strong>in</strong>struments, which vary <strong>in</strong> different municipalities. The water system pipel<strong>in</strong>e<br />

network <strong>in</strong> F<strong>in</strong>land comprises of 83,614 km, of which plastic pipes amount to<br />

72,206 km, iron pipes 8,382 km and pipes of other materials 3,026 km (SYKE<br />

2007).<br />

milj.m 3 /a<br />

500<br />

450<br />

400<br />

350<br />

300<br />

250<br />

200<br />

150<br />

100<br />

50<br />

0<br />

1970 1974 1978 1982 1986 1990 1994 1998 2010<br />

(Estimated)<br />

Ground water Surface water Total<br />

(+arti<strong>fi</strong>cial recharge)<br />

Figure VI—2 Amount of water distributed by public water works <strong>in</strong> F<strong>in</strong>land dur<strong>in</strong>g years 1970<br />

– 2001 (milj.m 3 /a). (Modi<strong>fi</strong>ed from SYKE 2007)<br />

Groundwater quality <strong>in</strong> its natural state is usually of high quality <strong>in</strong> F<strong>in</strong>land.<br />

F<strong>in</strong>nish groundwater is generally of the Ca-HCO 3 type, which is typical for<br />

glaciated areas, with low concentrations of electrolytes, and low pH, alkal<strong>in</strong>ity,<br />

calcium and magnesium. Occasionally, especially <strong>in</strong> spr<strong>in</strong>g time the KMnO 4<br />

numbers are high and alum<strong>in</strong>ium and iron values are <strong>in</strong>creased (Lahermo et al.<br />

1999, Backman 2004). Groundwater quality depends on geological, anthropogenic,<br />

climatic, and mar<strong>in</strong>e factors. In some areas the groundwater can conta<strong>in</strong> high<br />

concentrations of harmful elements such as nickel, manganese, arsenic, fluor<strong>in</strong>e or<br />

radon of geological orig<strong>in</strong>. Human activities <strong>in</strong> some agricultural areas lead to an<br />

<strong>in</strong>crease <strong>in</strong> nitrate and potassium concentrations and de-ic<strong>in</strong>g of roads causes<br />

contam<strong>in</strong>ation <strong>in</strong> some aquifers. However, groundwater reserves <strong>in</strong> F<strong>in</strong>land do not<br />

normally suffer from contam<strong>in</strong>ation on a wider scale, because <strong>in</strong>dividual bodies of<br />

groundwater tend to be small. The risk of contam<strong>in</strong>ation is highest <strong>in</strong> areas where<br />

soils consist of high permeable layers of sands and gravel, which can be easily<br />

<strong>in</strong><strong>fi</strong>ltrated by pollutants.<br />

Groundwater resources along the coastal area are at risk, not only due to the<br />

change of hydrologic patterns. They also are vulnerable to sea level rise, especially<br />

<strong>in</strong> coastal areas along the southern coast, where future sea level rise is expected to<br />

NORDREGIO REPORT 2007:5 193

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