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Results of Monitoring at Olkiluoto in 2006 - Environment (pdf) - Posiva

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29<strong>of</strong> both PO 4 -P and Mn <strong>in</strong> stand throughfall is normally higher than th<strong>at</strong> <strong>in</strong> bulk deposition.However, the other elements are not normally measured <strong>in</strong> bulk deposition <strong>in</strong> studieson ecosystem function<strong>in</strong>g, and therefore it is difficult to f<strong>in</strong>d comparable resultsfrom the liter<strong>at</strong>ure. An <strong>in</strong>crease <strong>in</strong> Fe, Mn and Si is understandable because these elementsare associ<strong>at</strong>ed with m<strong>in</strong>eral dust (e.g. from forest roads), but Al would also havebeen expected to <strong>in</strong>crease correspond<strong>in</strong>gly. The deposition <strong>of</strong> PO 4 -P, Al, Fe, Mn, Cu,Zn and Si <strong>in</strong> bulk deposition and stand throughfall was rel<strong>at</strong>ively similar <strong>in</strong> <strong>2006</strong> to thelevels <strong>in</strong> 2004 and 2005.Forest Intensive <strong>Monitor<strong>in</strong>g</strong> Plot: FIPSoil SolutionThe results <strong>of</strong> the soil solution monitor<strong>in</strong>g <strong>in</strong> 2004-<strong>2006</strong> were orig<strong>in</strong>ally reported byJohn Derome (F<strong>in</strong>nish Forest Research Institute) <strong>in</strong> a memo and are summarized below.The result tables can be found <strong>in</strong> Appendix F.The pl<strong>at</strong>e lysimeters <strong>at</strong> a depth <strong>of</strong> 5 cm functioned well on FIP4 dur<strong>in</strong>g the monitor<strong>in</strong>gperiod, the samples hav<strong>in</strong>g been obta<strong>in</strong>ed on almost all sampl<strong>in</strong>g occasions (<strong>at</strong> ca. fourweek <strong>in</strong>tervals). Despite the rel<strong>at</strong>ively dry summer <strong>in</strong> 2005, and especially <strong>in</strong> <strong>2006</strong>, thesuction-cup lysimeters also provided samples on seven sampl<strong>in</strong>g occasions (ca. fourweek <strong>in</strong>tervals) from 24.5.2005 to 7.11.2005 and on five occasions from 23.5. to2.11.<strong>2006</strong>. In July <strong>2006</strong>, no samples were obta<strong>in</strong>ed because precipit<strong>at</strong>ion was only 1.6mm. The pl<strong>at</strong>e lysimeters <strong>in</strong>stalled <strong>at</strong> a depth <strong>of</strong> 5 cm on the spruce plot yielded samplesonly on two occasions <strong>in</strong> 2005 (5.8. and 6.9.), but on five occasions <strong>in</strong> <strong>2006</strong> (19.6.,14.8., 11.9., 10.10. and 2.11.).In FIP4 the amount <strong>of</strong> percol<strong>at</strong>ion w<strong>at</strong>er pass<strong>in</strong>g down to a depth <strong>of</strong> 5 cm dur<strong>in</strong>g thesnow-free period (Fig. 20, Table F-1) was ca. 17% <strong>of</strong> the <strong>in</strong>put to the forest floor (standthroughfall) <strong>in</strong> 2004, ca. 21% <strong>in</strong> 2005, and ca. 16% <strong>in</strong> <strong>2006</strong>. There was considerablevari<strong>at</strong>ion between the sampl<strong>in</strong>g d<strong>at</strong>es due primarily to the vary<strong>in</strong>g amounts <strong>of</strong> standthroughfall. The amounts were especially low after snowmelt <strong>in</strong> the l<strong>at</strong>ter half <strong>of</strong> Mayand the first half <strong>of</strong> June <strong>in</strong> 2004, and <strong>in</strong> July and August <strong>in</strong> <strong>2006</strong>. Overall, the proportion<strong>of</strong> w<strong>at</strong>er pass<strong>in</strong>g down to a depth <strong>of</strong> 5 cm was rel<strong>at</strong>ively similar <strong>in</strong> all years, withslightly lower values <strong>in</strong> the dry parts <strong>of</strong> summer <strong>in</strong> 2004 and <strong>2006</strong>.

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