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Browsing by Subject "peat"

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  • Kuisma, Eero (2013)
    The use of peat as a growing-medium has raised concerns globally, because it is not ecologically sustainable. Coir is an ecologically friendly alternative, but it is transported very long way to Finland. Therefore, a substitute for peat and coir as a growing-medium in soilless culture is needed. The aim of this research was to find out, whether Finnish plant fibre medium can replace peat or coir in greenhouse production of strawberry. In the experiments four substrates were compared: coir, peat, plant fibre and peat/plant fibre mix. Water holding capacity, pH-buffer capacity and mineralisation of nitrogen were determined, and vegetative and generative growth of strawberries on different substrates were measured. In strawberry cultivation experiment the pH of plant fibre (6,5-7,7) was very close to that of peat (6,4-7,6). Coir and plant fibre had considerably lower pH-buffer capacity than the media that contained peat. The water holding capacity (613 % per dw) of plant fibre was considerably lower than in other media. Plant fibre medium´s water content (32-42 % v/v) was however closest to strawberry´s optimum (25-34 % v/v) during almost the whole experiment. Plant fibre (23:1) and peat/plant fibre mix (29:1) had optimal C/N- ratios in this experiment. The amount of soluble nitrogen was highest in plant fibre medium in the beginning of the experiment. The EC of plant fibre medium was very low in the beginning (0,5 mS/cm), but it increased quickly being 1,2-2,1 mS/cm, so it was second closest to the optimum during the rest of the experiment. The vegetative growth of strawberry plants was more vigorous in peat compared to other substrates. The growth of the root system was weakest in peat. Medium had no significant influence on the amount of yield, and had only minor influence on the quality of the yield. In conclusion, the plant fibre medium could replace peat or coir in the soilless cultivation of strawberry.
  • Rainio, Pauli (2013)
    In Norway spruce (Picea abies) dominated mineral soil sites, the polypore Heterobasidion parviporum often causes severe decay problems (butt rot, root rot). Not much is however known on the ability of H. parviporum to cause decay losses in peatland. The purpose of this study was to answer some fundamental question: 1) Is H. parviporum able to cause decay losses in drained mires? 2) Is there an effect of other soil microbes during saprotrophic growth of Heterobasidion on peat soil? 3) What are the potential inhibitory effects of microbes inhabiting peat soil on growth of Heterobasidion? For the decay study, wood discs (P. abies) in mesh bags were buried at the different forest sites; mineral soil and peatlands (including drained mire and undrained mire). The amount of weight loss was documented after four months. The study was repeated in vitro by autoclaving soil samples from these sites together with wood discs followed by inoculation with H. parviporum. On mineral soil, H. parviporum decayed spruce (P. abies) wood disc much more than on non-drained pristine mire. On drained (ditched) mire, no significant difference in the weight loss was observed. H. parviporum grew significantly more on the sterilized soil and decayed more wood, compared to non-sterilized soil. The results suggested that secreted metabolites in the unsterilized soil may be able to significantly suppress saprotrophic growth of H. parviporum. In the fungal growth inhibition experiment, water- and acetone-soluble substances were extracted from the soil with acetone and water. No fungal growth inhibiting substances were detected from the various peat soils or mineral soils.
  • Granqvist, Anna-Liisa (2022)
    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.
  • Binte Mostafiz, Suraiya (2014)
    Plant production in soilless systems is attracting increased interest day by day. The major reason for these interest is the fact that soilless medium can help to eliminate soil-borne diseases and give an understanding of plant nutritional requirements. The aim of this thesis is to evaluate the suitability of chemically and physically modified wood shavings as growing media for horticultural crop production. Five different wood shavings derived from Scots pine trees, namely untreated wood, heat treated wood, organic acid treated wood, Q-Treat, Q-Treat and organic acid treated wood, along with mixtures of peat and Q-Treat as 50/50 v/v (P50Q50), 25/75 (v/v) (P25Q75) and peat (control ) were used. In order to assess the characteristics of the growing media phytotoxicity, pH, water holding capacity, N immobilization, EC, water content of the substrates were analysed. Plant performances on the substrates was evaluated by observing the vegetative and generative growth of Hosta ‘Golden Tiara’ and strawberry ‘Elsanta’ plants. Q-Treat, organic acid treated wood and P50Q50 showed a high water holding capacity. No nitrogen immobilization was observed in Q-Treat. At the same time, EC and water content of the substrates were favourable for both Hosta ‘Golden Tiara’ and strawberry production. Hosta ‘Golden Tiara’ plants grew satisfactorily on all the substrates but the visual quality of the plants was unacceptable on untreated wood. For strawberry, vegetative growth was strong on peat and P50Q50. Least runners were formed on P25Q75 and all of the wood substrates. However, the yield from strawberries was highest on peat and P25Q75. The quality of strawberry fruits on wood substrates was equal to that on peat. In conclusion, based on the results obtained in this experiment, 50% of peat may be replaced by 50% Q-Treat in soilless cultivation for Hosta ‘Golden Tiara’ and 75% of peat may be replaced by Q-Treat in soilless strawberry production.