Table 1. Details of the study sites, Asa and Turbo, and experimental installations. | ||
Asa | Turbo | |
Latitude / longitude | 57°08´N / 14°47´E | 60°14´N / 15°51´E |
Altitude (m amsl) | 235 | 195 |
Aspect / topography | east /gentle slope | west / gentle slope |
Soil type | podzolized sandy-silty till | podzolized silty till |
C/N in mor layera | 29.9 (26.7) | 27.5 (25.5) |
Mean precipitation (mm year–1)b | 664 | 581 |
Annual mean air temperature (°C)b | 5.3 | 5.0 |
Open-field deposition (mean for 1994–2000)c (kg ha–1 year–1) | ||
NO3--N | 3.8 | 2.0 |
NH4+-N | 3.4 | 1.9 |
SO42--S | 5.2 | 3.0 |
Cl- | 12 | 2.7 |
Na++K++Mg2++Ca2+ | 12 | 4.4 |
Site quality class (m3 ha–1 year–1) | 11.3 | 8.4 |
Tree species composition of the harvested stand, by basal area | P. abies (100%) | P. abies (71%) & Pinus sylvestris L. (29%) |
Date of harvest | 23–24 April, 2001 | Shift May-June, 2001 |
Date of residue treatment | 3 May, 2001 | 31 May, 2001 |
Date of installation of suction cups and funnelsd | Late April, 2001 | Early May, 2001 |
aMeasured in 2006 and, shown within parentheses, in 2008. bData from nearby meteorological stations (Alexandersson and Eggertsson Karlström 2001). cData from nearby monitoring stations (http://www.krondroppsnatet.ivl.se/). dFunnels were installed at Asa only. |
Table 2. Studied treatments at the Asa and Turbo sites. Logging residues (LR) include tops and branches with needles. The stand-specific amount of LR (1LR) is defined as the estimated LR amount per hectare of the harvested tree stand spread on one hectare of the ground. The treatments 2LR and 4LR refer to, respectively, two and four times that amount. For the needle treatments, the amounts of needles, calculated according to Marklund (1988), are presented within parentheses. | |||
Treatment | Abbreviation | Added amount of logging residues in 2001 (kg m-2 dry matter) | |
Asa | Turbo | ||
LR harvested | 0LR | 0 | 0 |
1×stand-specific amount of LR | 1LR | 4.4 | 5.0 |
Needles from 1×stand-specific amount of LR (tops and branches were removed after about 20 weeks)a | 1Needle_20 | 4.4 (1.5) | 5.0 (1.6) |
2×stand-specific amount of LR | 2LR | 8.8 | 9.9 |
4×stand-specific amount of LR | 4LR | 17.6 | 19.8 |
Needles from 8×stand-specific amount of LR (tops and branches were removed after about 7 weeks)a | 8Needle_7 | 35.2 (11.6) | 39.6 (12.6) |
Needles from 8×stand-specific amount of LR (tops and branches were removed after about 20 weeks)a | 8Needle_20 | 35.2 (11.6) | 39.6 (12.6) |
aThe added amounts of needles were less than the presented total amounts, i.e. significant amounts of needles were removed with the tops and branches after storage on the study plots. In the 8Needle_7 and 8Needle_20 treatments, less than 30% of the total amount remained on the ground after removing the LR. |
Table 3. Results from the linear mixed models (Model 1) used to determine effects of treatment, time and the interaction between treatment and time for the studied soil-solution variables; number of observations and p-values according to Model 1. | ||||||||
Variable | Number of observations, n | p-values for effect of treatment, αi | p-values for effect of time, τk | p-values for interaction between treatment and time, (ατ)ik | ||||
Asa | Turbo | Asa | Turbo | Asa | Turbo | Asa | Turbo | |
Electrical conductivity | 629 | 266 | 0.36 | <0.0001 | <0.0001 | <0.0001 | 0.25 | <0.0001 |
H+ | 735 | 490 | 0.56 | 0.0015 | <0.0001 | <0.0001 | 0.56 | <0.0001 |
K+ | 736 | 490 | 0.77 | 0.0048 | <0.0001 | <0.0001 | 0.90 | <0.0001 |
Mg2+ | 736 | 490 | 0.21 | 0.0005 | <0.0001 | <0.0001 | 0.025 | <0.0001 |
Ca2+ | 736 | 490 | 0.68 | 0.57 | <0.0001 | <0.0001 | 0.042 | <0.0001 |
Al | 735 | 489 | 0.98 | 0.026 | <0.0001 | <0.0001 | 0.28 | 0.0022 |
Cd | 386 | 214 | 0.46 | 0.0049 | <0.0001 | 0.0006 | 0.19 | 0.049 |
Zn | 579 | 218 | 0.21 | 0.0043 | <0.0001 | <0.0001 | 0.46 | 0.40 |
NH4+-N | 734 | 487 | 0.30 | 0.028 | <0.0001 | <0.0001 | 0.39 | 0.0048 |
NO3--N | 710 | 487 | 0.0039 | 0.0013 | <0.0001 | <0.0001 | 0.0002 | 0.0009 |
SO42--S | 735 | 485 | 0.65 | 0.014 | <0.0001 | <0.0001 | 0.29 | <0.0001 |
Cl- | 735 | 485 | 0.028 | 0.0008 | <0.0001 | <0.0001 | 0.84 | 0.020 |