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NIBIOs ansatte publiserer flere hundre vitenskapelige artikler og forskningsrapporter hvert år. Her finner du referanser og lenker til publikasjoner og andre forsknings- og formidlingsaktiviteter. Samlingen oppdateres løpende med både nytt og historisk materiale. For mer informasjon om NIBIOs publikasjoner, besøk NIBIOs bibliotek.

2022

Sammendrag

Invasive plant propagative material can be introduced to new regions as contaminants in soil. Therefore, moving soil should be done only when the soil has been verified to be free of invasive species. Stationary soil steaming as a non-chemical control method has the potential to disinfect soil masses contaminated with invasive species. We investigated the possibility of thermal control of propagative material of Bohemian knotweed (Reynoutria × bohemica) in two experiments using a prototype of a soil steaming device. Five soil temperatures of 60, 70, 80, 90 and 99 °C with an exposure duration of 3 min were tested. In each replicate and target temperature, rhizome cuttings containing at least two buds and shoot clumps were placed at the bottom of a plastic perforated basket and covered by a 7-cm soil layer. Each basket was placed in the steaming container and steam was released from the top and vacuumed from the bottom. Soil temperature was monitored by 10 thermocouples and steaming was stopped when 5 of the thermocouples had reached the target temperature. The basket was then removed from the steaming container after 3 min. Plant materials were taken out and planted in pots. Buds sprouting was followed for 8 weeks. Non-steamed plant materials were used as controls. Results showed 100% rhizome death at soil temperatures of ≥70 and 99 °C in the first and second experiments, respectively. Shoot clumps death was obtained at ≥90 °C in both experiments. These results showed that steaming at 99 °C for 3 min can guarantee control of Bohemian knotweed in infested soils supporting the steam treatment as a potential method of disinfecting soil against invasive species. However, depending on the intended re-use of the soil, further studies are needed on the effect of potential negative impacts of high temperatures on the soil quality.

Sammendrag

Store mengder god jord med frø eller rotstengler av fremmede invaderende karplanter deponeres hvert år. For en mer bærekraftig forvaltning av jordressurser ønsket Statens vegvesen å undersøke om slik jord fra veianlegg isteden kan kanaliseres til jordbruket der vanlig ugraskontroll og drift forhåpentligvis kan kontrollere de uønskede artene. I prosjektet FoU-forsøk «Håndtering av jordmasser infisert av fremme karplanter gjennom landbruket» gjennomførte vi tre forsøk der vi 1. undersøkte etablering av kanadagullris fra lagret A-sjikt tilbakeført til eng, 2. etablering av kanadagullris fra infisert jord lagt ut på arealer til korndyrking, og 3. bruk av geiter til å kontrollere slireknearter i infisert jord lagt ut til beite. Resultatene fra disse forsøkene presenteres i denne rapporten. Resultatene viser at disse tilnærmingene kan fungere, men effektene må dokumenteres bedre.

Sammendrag

Reusing soil can reduce environmental impacts associated with obtaining natural fresh soil during road construction and analogous activities. However, the movement and reuse of soils can spread numerous plant diseases and pests, including propagules of weeds and invasive alien plant species. To avoid the spread of barnyardgrass in reused soil, its seeds must be killed before that soil is spread to new areas. We investigated the possibility of thermal control of barnyardgrass seeds using a prototype of a stationary soil steaming device. One Polish and four Norwegian seed populations were examined for thermal sensitivity. To mimic a natural range in seed moisture content, dried seeds were moistened for 0, 12, 24, or 48 h before steaming. To find effective soil temperatures and whether exposure duration is important, we tested target soil temperatures in the range 60 to 99 C at an exposure duration of 90 s (Experiment 1) and exposure durations of 30, 90, or 180 s with a target temperature of 99 C (Experiment 2). In a third experiment, we tested exposure durations of 90, 180, and 540 s at 99 C (Experiment 3). Obtaining target temperatures was challenging. For target temperatures of 60, 70, 80, and 99 C, the actual temperatures obtained were 59 to 69, 74 to 76, 77 to 83, and 94 to 99 C, respectively. After steaming treatments, seed germination was followed for 28 d in a greenhouse. Maximum soil temperature affected seed germination, but exposure duration did not. Seed premoistening was of influence but varied among temperatures and populations. The relationships between maximum soil temperature and seed germination were described by a common dose–response function. Seed germination was reduced by 50% when the maximum soil temperature reached 62 to 68 C and 90% at 76 to 86 C. For total weed control, 94 C was required in four populations, whereas 79 C was sufficient in one Norwegian population.

Sammendrag

Established invasive alien plant species make it difficult and costly to move and make use of infested soil in public and private construction work. Stationary soil steaming as a non-chemical control method has the potential to disinfect soil masses contaminated with seeds and other propagative plant materials. The outcome can vary depending on steaming temperature and duration. Higher temperatures and longer durations are relatively more efficient but may also have side-effects including change in soil physical and chemical characteristics. Barnyard grass (Echinochloa crus-galli) is among troublesome invasive species in Norway. We have tested different steam duration at 99°C to find the possible lowest effective exposure duration for killing seeds of this annual grass species. Four replications of 40 barnyard grass dry seeds of one population were placed in polypropylene-fleece bags (9*7 cm), moistened for 12 hours, and covered by the soil at a depth of 7 cm in 60*40*20 cm boxes. The boxes with soil and bags were steamed at 99°C for 1.5, 3 and 9 min. The bags including steamed seeds were taken out, opened, placed on soil surface in pots and covered by a thin layer of soil. The pots were placed in greenhouse and watered from below and seed germination was followed for a month. Moistened non-steamed seeds were used as control. It was shown that steaming at 99°C gave 0% germination indicating that 100% of the seeds were killed regardless of exposure duration while in the control seed germination was 100%. Consequently, to achieve an efficacy of 100%, exposure duration of 1.5 min would be enough. Finding the lowest possible steam temperature and exposure duration to get the highest possible seed killing in a seed mixture of different plant species as well as other factors to increase the heat transferability are under investigation. Keywords: Echinochloa crus-galli; Resource recovery; Steaming temperature and duration; Thermal soil disinfection

2021

Sammendrag

Statskog eier om lag 8% av Norges produktive skogareal. Skogen er dominert av en stor andel hogstmoden skog og en overvekt av skog på lavere boniteter. Tilveksten i skogen er svakt avtagende noe som sannsynligvis skyldes skjev aldersklasse fordeling med mye eldre skog. Hogsten i skogen er kun om lag en tredjedel av tilveksten og fører til en sterk oppbygging av det stående volum på Statskog sine eiendommer. Når tilveksten er høyere enn avvirking vil man vanligvis forvente et opptak av karbon i skogen. Dette er også tilfellet for Statskog hvor det er estimert et karbonopptak på om lag 1,5 mill. ton CO2 per år. Karbon opptaket er litt mindre nå enn det var tidligere ettersom tilveksten er fallende og hogsten har vært svakt økende. Når man driver hogst er det fossile utslipp knyttet til hogst, terrengtransport, og tømmerbil transport. Mellom 2010 og 2019 har utslippene fra hogst og transport variert mellom 1 600 tonn CO2 og 4 900 tonn CO2 avhengig av hogstkvantum. Det er viktig å fremheve at utslippene fra transport og hogst er minimale sammenlignet med opptaket av CO2 i skogen til Statskog. Når man avvirker skog produseres det materialer som kan erstatte fossil intensive materialer til andre sektorer slik som bygg og energi. Det er vanskelig å direkte kvantifisere substitusjonen av fossil intensive materialer da effekten er avhengig av de spesifikke materialene som erstattes og effektiviteten i hele verdikjeden. På den andre siden er substitusjon en viktig del av klimaeffekten ved hogst og bør inkluderes når man vurderer klimaeffekter av skogsdrift. Hvis vi antar at skurlast produsert fra avvirkningen til Statskog benyttes til å erstatte stål er det estimert at substitusjonen mellom 2010 og 2019 har variert mellom 32 000 og 99 000 tonn CO2 per år. Substitusjonseffekten er dermed mye høyere enn utslippene fra hogst og transport, men likevel små i forhold til opptaket av karbon i skogen til Statskog. Gjennom skogbehandlingen kan man kraftig påvirke opptaket av karbon i skogen. På lang sikt, er det muligheter for å øke opptaket av karbon gjennom økt plantetetthet og økt bruk av foredlet plantemateriale. Ved å gjødsle skogen kan man oppnå raskt økende opptak av karbon, men den samlede effekten er ikke nødvendigvis så stor da det er begrenset med arealer som er egnet til økt gjødslingsintensitet. Andre tiltak slik som forlenget omløpstid kan også vurderes, men må ses i sammenheng med skogens helsetilstand og effekter på det tilgjengelige hogstkvantum.

Sammendrag

Background The Norwegian forest resource map (SR16) maps forest attributes by combining national forest inventory (NFI), airborne laser scanning (ALS) and other remotely sensed data. While the ALS data were acquired over a time interval of 10 years using various sensors and settings, the NFI data are continuously collected. Aims of this study were to analyze the effects of stratification on models linking remotely sensed and field data, and assess the accuracy overall and at the ALS project level. Materials and methods The model dataset consisted of 9203 NFI field plots and data from 367 ALS projects, covering 17 Mha and 2/3 of the productive forest in Norway. Mixed-effects regression models were used to account for differences among ALS projects. Two types of stratification were used to fit models: 1) stratification by the three main tree species groups spruce, pine and deciduous resulted in species-specific models that can utilize a satellite-based species map for improving predictions, and 2) stratification by species and maturity class resulted in stratum-specific models that can be used in forest management inventories where each stand regularly is visually stratified accordingly. Stratified models were compared to general models that were fit without stratifying the data. Results The species-specific models had relative root-mean-squared errors (RMSEs) of 35%, 34%, 31%, and 12% for volume, aboveground biomass, basal area, and Lorey’s height, respectively. These RMSEs were 2–7 percentage points (pp) smaller than those of general models. When validating using predicted species, RMSEs were 0–4 pp. smaller than those of general models. Models stratified by main species and maturity class further improved RMSEs compared to species-specific models by up to 1.8 pp. Using mixed-effects models over ordinary least squares models resulted in a decrease of RMSE for timber volume of 1.0–3.9 pp., depending on the main tree species. RMSEs for timber volume ranged between 19%–59% among individual ALS projects. Conclusions The stratification by tree species considerably improved models of forest structural variables. A further stratification by maturity class improved these models only moderately. The accuracy of the models utilized in SR16 were within the range reported from other ALS-based forest inventories, but local variations are apparent.