Browsing by Subject "peatland"

Peat lands are net sinks of carbon (C) and a net source of carbon dioxide (CO2) emissions owing to drainage during the growing season. The surface peat layer can be lost because of aerobic decomposition (oxidation) after drainage resulting in emissions of CO2. One way to reduce these emissions is to keep the water table at a high level as much as possible. The resulting anoxic conditions reduce the decomposition of organic matter and hence CO2 emissions. In the current Finnish agri-environmental scheme, the farmers may receive subsidies for controlled drainage on peatlands, and a raised ground water level through controlled drainage could be used as a greenhouse gas mitigation measure. This study reports the carbon balance of drained peatland under controlled drainage during the growing season in Mouhijärvi, Southwestern Finland. The CO2 fluxes measured with a transparent chamber method were divided into gross primary productivity (GPP) and ecosystem respiration (ER) for modelling based on environmental factors (light and temperature) and canopy reflectance (leaf area index, LAI). The GPP model estimates the effect of light and vegetation status, whereas the ER model captures the share of foliar biomass-dependent respiration and the ground water table. The sum of the study period (June–August 2016) GPP varied from -1301 to -670 g C m-2, ER from 632 to 1029 g C m-2 and net ecosystem exchange (NEE) from -322 to 68.5 g C m-2. NEE indicated a net sink of C in all plots except one with poor crop growth. The net ecosystem carbon balance (as the sum of NEE and carbon export as grains), indicated a net source of carbon in both plots with controlled drainage and a net sink in conventionally drained plots during the cultivation period. The greatest sink reported either as NEE or with the harvest included was the wettest plot, indicating that cereal production is possible in wetter than normal conditions.

Peatlands are a significant carbon and nitrogen reservoirs, making them potential sources of carbon dioxide (CO2), methane (CH4), and nitrous oxide (N2O) emissions. Variations in water table level change the oxygen content of peat, affecting the oxidation-reduction or redox state of the peat, which is known to influence the biochemical processes and thus greenhouse gas (GHG) emissions. The aim of this study was to assess the effect of controlled anoxic redox conditions and inorganic electron acceptors (TEAs) on redox potential (Eh), and N2O, CH4, and CO2 emissions. In this study during an anaerobic incubation experiment, the rates of formation of these GHGs and Eh values as a function of time were measured from drained (D) and undrained (UD) peat of three nutrient levels: mesotrophic (ME), oligotrophic (OL), and ombrotrophic (OM). Redox conditions were controlled to three levels by nitrate (NO3-), ferric iron (Fe3+), and sulphate (SO42-). In addition, measurements were performed on untreated (Ctrl) peat. The peat was in an anoxic state throughout the incubation (Eh < 300 mV) and the values were in the order of TEA reduction, even though they were mainly in the iron and manganese reduction zones, probably due to the naturally high iron content of the peat. As expected, N2O formation was highest in flasks with added NO3-, and N2O formation was weak and ceased without addition. CH4 formation was reduced in flasks with added NO3- or SO42-, and SO42- addition also inhibited CO2 formation on which NO3- addition had no effect. In contrast, the addition of Fe3+ increased both CO2 and CH4 formation compared to Ctrl treatment, and it is possible that methanogens were involved in the reduction of Fe3+. In Ctrl flask, the redox state did not decrease to the lowest level compared to the other treatments as expected, but the Ctrl treated UD ME peat had the highest CH4 formation at the end of incubation. For all treatments, GHG emissions were higher from nutrient-rich peat in the descending order ME > OL > OM. In general, UD peat also had higher gas formation than D peat. All GHGs were formed the most while Eh values were around 0 mV and the value was especially high for CH4 formation, probably due to the linkage between methanogens and iron. The poor ability of the Pt electrode to detect NO3- or oxygen was the most likely reason for the variable and low Eh values of the flasks with NO3- addition. For the same reason, oxygen leakage of the anaerobic chamber was most likely responsible for the varying Eh values measured from Ctrl treated OM peat. This study suggests that Eh measurement is a useful predictor of the redox state and reactions, but it must be considered together with other measurements and analyses such as microbial analysis, nutrient analysis, and GHG measurements to predict redox processes and GHG emissions in anaerobic peatland. In particular, the role of iron on CH4 emissions requires further research.

Experimental warming provides a method to determine how an ecosystem will respond to increased temperatures. Northern peatland ecosystems, sensitive to changing climates, provide an excellent setting for experimental warming. Storing great quantities of carbon, northern peatlands play a critical role in regulating global temperatures. Two of the most common methods of experimental warming include open top chambers (OTCs) and infrared (IR) lamps. These warming systems have been used in many ecosystems throughout the world, yet their efficacy to create a warmer environment is variable and has not been widely studied. To date, there has not been a direct, experimentally controlled comparison of OTCs and IR lamps. As a result, a factorial study was implemented to compare the warming efficacy of OTCs and IR lamps and to examine the resulting carbon dioxide (CO2) and methane (CH4) flux rates in a Lake Superior peatland. IR lamps warmed the ecosystem on average by 1-2 oC, with the majority of warming occurring during nighttime hours. OTC's did not provide any long-term warming above control plots, which is contrary to similar OTC studies at high latitudes. By investigating diurnal heating patterns and micrometeorological variables, we were able to conclude that OTCs were not achieving strong daytime heating peaks and were often cooler than control plots during nighttime hours. Temperate day-length, cloudy and humid conditions, and latent heat loss were factors that inhibited OTC warming. There were no changes in CO2 flux between warming treatments in lawn plots. Gross ecosystem production was significantly greater in IR lamp-hummock plots, while ecosystem respiration was not affected. CH4 flux was not significantly affected by warming treatment. Minimal daytime heating differences, high ambient temperatures, decay resistant substrate, as well as other factors suppressed significant gas flux responses from warming treatments.

Root and butt rot is the most harmful fungal disease affecting Norway spruce in southern Finland. In approximately 90 % of cases the causal agent is Heterobasidion parviporum. Root and butt rot infections have not been reported in Finnish peatlands. However, the increase in logging operations in peatlands means there is a risk that the fungus will eventually spread to these areas. The aim of this study was to find out the impact of growing site on the resistance of Norway spruce to Heterobasidion parviporum infections. This was investigated by artificially inoculating H. parviporum to spruce trees in pristine mire, drained peatland and mineral soil and comparing the defence reactions. Additionally, the effect of genotype on resistance was studied by comparing the responses of spruce clones representing different geographic origins. The roots and stems of the trees to be sampled were wounded and inoculated with wood dowels pre-colonised by H. parviporum hyphae. The resulting necrosis around the point of inoculation was observed. It was presumed that increased length of necrosis indicates high susceptibility of the tree to the disease. The relationship between growth rate and host resistance was also studied. The results indicated that growing site does not have a statistically significant effect on host resistance. The average length of necrosis around the point of inoculation was 35 mm in pristine mire, 37 mm in drained peatland and 40 mm in mineral soil. It was observed that growth rate does not affect resistance, but that the genotype of the tree does have an effect. The most resistant spruce clone was the one with Russian origin. The results suggest that the spruce stands in peatlands are not more resistant to root and butt rot infections than those in mineral soil. These findings should be taken into consideration when logging peatland forests.

Pristine mires are an important carbon storage, but after drainage, the carbon is released from the peat through aerobic decomposition. In Finland, half of the original mire area has been drained, mainly for forestry purposes. Majority (83 %) of the drained area is suitable for forestry. Out of the forestry-suited drained peatlands, the nutrient-rich forestry drained peatlands emit high amounts of CO2 due to high aerobic decomposition as nutrient-rich conditions are favourable for decomposing bacteria. Rewetting of these nutrient-rich peatlands could offer a solution for halting the CO2 emission, but the CH4 emission increases after rewetting. The studies show differing results of CH4 emission from nutrient-rich rewetted peatlands. There are studies reporting both high and low emission of CH4 from nutrient-rich peatlands, and differing studies on how the emission evolves in time. This thesis focused on three variables that could affect the CH4 emission: time from rewetting, water level and site type. There were 27 different study sites at 8 locations. These sites were rewetted 3 to 28 years prior to measurements and represented nutrient-rich tree-covered peatlands (Rhtkg, Mtkg, Ptkg). Ptkg was the least nutrient-rich site type in the study. The CH4 flux was measured with a chamber method from July to November of 2021. Water level was monitored with loggers and manual measurements. The data was analysed with linear regression and analysis of variance, depending on the independent variable. Mean CH4 fluxes were used to compare sites with each other. The results show that water level affects the CH4 emission at statistically significant level. When water level is deeper than 10cm below ground level, the CH4 emission is low. One site differed from this trend and despite the high water level, the CH4 emission was close to zero. Time from rewetting did not affect CH4 emission at statistically significant level, but there was a visible trend of older rewetted peatlands emitting less than more recently rewetted ones. This finding was contradicting to the literature as it was supposed that the more recently rewetted peatlands emit less CH4. Out of site types, the Mtkg2 and Rhtkg site types emitted most, but there was no statistical significance. When analysed with using both the water level and site type, there were statistical differences between site types. When comparing mean CH4 emissions from nutrient-rich (Rhtkg+Mtkg) and least nutrient-rich (Ptkg) peatlands at the same water level, the Ptkg sites emitted less, but not at a statistically significant level. The findings indicate that, when rewetting a nutrient-rich tree-covered peatland, it should be done so that the water-level does not rise above 10cm, but this is very difficult or impossible to regulate. Restoration process and how it develops is difficult to foresee and the end-result might differ. Research on CH4 emissions from rewetted nutrient-rich peatlands and what affects it is increasingly important as CH4 affects the climate change in the near future.

The study is part of Future Biorefinery, the second research program of Forestcluster Ltd. The goal of the program is to find innovative ways to better utilize the raw materials of the forest industry. The aim of the study is to investigate the structure and characters of stump- and rootwood of Scots pine (Pinus sylvestris L.) and Norway spruce (Picea abies [L.] Karst.). The aim is to find out if there is any reaction wood in the roots of Scots pine and Norway spruce and what is the proportion of the acetone soluble extractives in the stump- and root wood. The study material consisted of five stems of Scots pine and Norway spruce of various age. Root and stump samples of Scots pine and Norway spruce were collected after cutting the timber from a peatland site in Parkano (62.017°N, 23.017°E), Western Finland. Cutting was done by the Finnish Forest Research Institute (Metla). The samples were taken from the underground parts of roots a three different distances from the root collar. The study was executed as descriptive research. Neither of the species showed traces of actual reaction wood, but some samples showed traces of mild reaction wood. The mild form of reaction wood was more common in the pine roots than in the spruce roots and it did not appear in the samples that were taken from the thinnest parts of roots, i.e. the roots with ca. 2 cm diameter. The acetone soluble extractive content was higher in the pine stumps than in the spruce stumps. In the pine roots the extractives per cent increased towards the root tips. On the spruce roots the extractives per cent decreased at first and then increased near the root tips. The extractives per cent of the bark was higher than of the wood and that applied for both species. Becouse the sample set was rather limited there was no attempt to make any statistic analysis of the data. There is a need for further studies concerning properties of roots and stumps from peatlands. The supply of wood from peatlands is increasing in the future in Finland while the studies on wood properties and extractives of roots have been focused in the mineral soils.