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Publikasjoner

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.

2011

Sammendrag

Vegetasjonskart gjev eit bilete av den mosaikken av vegetasjonstypar som det naturlege plantedekket består av. Ein vegetasjonstype er ei karakteristisk samling planteartar som vil gå att på lokalitetar med like veksetilhøve. Ei oversikt over utbreiinga av vegetasjonstypar gjev oss på denne måten informasjon også om variasjonen i økologiske faktorar (klima, næring og vatn i jorda, snødekke og kulturpåverknad) i eit område. I tillegg kan kvar vegetasjonstype tilleggast eigenskapar med omsyn til ulik ressursutnytting og bruk (beite, slitestyrke for ferdsel, artsmangfald m.m.). Skog og landskap har laga vegetasjonskart over beiteområdet til Hanestadkjølen sausankelag i Rendalen kommune. Området er 67 km² i landareal og 3 km² vatn. Viktigaste målsettinga med kartlegginga er å lage eit grunnlag for planlegging av beitebruk i området. Kartlegginga er gjort etter Skog og landskap sin instruks for vegetasjonskartlegging i M 1:20 000 - 50 000...

Sammendrag

Housing of horses in Norway - an overview Grete H.M. Jørgensen1 and Knut E. Bøe2  1Bioforsk, National Institute for Agricultural and Environmental Research, Tjøtta Norway2Department of Animal and Aquacultural Sciences, Norwegian University of Life Sciences, UMB, ås Norway Corresponding author: +47 40 76 67 69 e-mail grete.jorgensen@bioforsk.no Similar to the National regulations for cattle, poultry and pigs the Norwegian regulation for the welfare of horses also states that horse owners should facilitate social contact for their horses. Nevertheless, it is quite common that horses are kept individually or even isolated from others throughout the year. Chronic obstructive pulmonary diseases are an increasing problem in the horse population and bad air quality in stables may contribute largely to this disease. Stables with fewer than ten horses do not have to register with the National Food Safety Authorities, and a public register of stables is not available. The aim of this study was therefore to provide an overview of the current management and living conditions for trotting horses in Norway. We wanted to focus both on the outdoor and indoor environment and investigate which ventilation systems that are commonly used in stable buildings. With help from the National Trotting Association (DNT) we sent out a questionnaire to members of their local branches in order to ensure answers from all areas of Norway. In each local branch we selected four to five stables after the following criteria: one small stable with 1-2 horses, to or three medium sized stables with 3-10 horses and the largest stable in that area. The questionnaire consisted of 32 questions divided into four subcategories: management, stable environment, ventilation and outdoor areas and paddocks. 275 (61%) of the 442 initial questionnaires were returned. Seven of these were however disregarded due to incomplete answers. The results were therefore finally based on 268 stables, 38 small stables (1-2 horses), 164 medium sized stables (3-10 horses) and 60 large stables (>10 horses). The data included over 2400 horses. More than half of the stable buildings had earlier been used for other purposes (56.4%). The majority of the stable buildings were insulated (83.6%), while a few had non-insulated stables (10.1%) or shelters with three walls and a roof (1.1%). Most stables had mechanical ventilation with a fan (49.6%), while 38.4% indicated that their stable had natural ventilation. Among the stable owners that indicated having natural ventilation in the stable, only 23.1% (8.9% of all stables) had non-insulated buildings and ventilation through adjustable openings, while 76.9% (29.8%) had insulated buildings and ensured airflow through opening doors and windows. A total lack of ventilation was indicated by 4.9% of the stable owners while 0.4% did not know what type of ventilation the stable had. In addition to this, 2.6% of the stable owners had most of their horses in 24 hour loose housing outdoors with open shelters and a ventilation system was therefore not necessary. Individual housing in boxes indoors dominated (84% of all stables), while very few horses were kept in outdoor boxes (1.1%). Other housing methods were tie-stalls 1.5%), 24 hour loose housing outdoors (3.4%), both tie-stalls and individual boxes (6.0%) and tie-stalls or boxes combined with group housing or several horses in the same box (1.1%). Six of the 38 small stables had only one horse which consequently was kept alone, while 34% of the small stables kept their horses in separate paddocks. Only 15% of the medium sized stables kept the horses in individual paddocks and 80.4% kept two or more horses together during turn-out. Ninety percent of the large stables indicated that they allowed two or more horses to share paddocks during turn-out. In conclusion, Norwegian trotting horses are mainly housed in individual boxes indoors and many stables have a ventilation system that does not work properly. Most trotting horses have access to a paddock or pasture on a daily basis. Housing and management of horses in other disciplines should also be investigated.

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Sammendrag

We used two datasets of 14C analyses of archived soil samples to study carbon turnover in O horizons from spruce dominated old-growth stands on well-drained podzols in Scandinavia. The main data set was obtained from archived samples from the National Forest Soil Inventory in Sweden and represents a climatic gradient in temperature. Composite samples from 1966, 1972, 1983 and 2000 from four different regions in a latitude gradient ranging from 57 to 67º N were analysed for 14C content. Along this gradient the C stock in the O horizon ranges from 2.1 kg m-2 in the north to 3.7 kg m-2 in the southwest. The other data set contains 14C analyses from 1986, 1987, 1991, 1996 and 2004 from the O horizons in Birkenes, Norway. Mean residence times (MRT) were calculated using a two compartment model, with a litter decomposition compartment using mass loss data from the literature for the threefirst years of decomposition and a humus decomposition compartment with a fitted constant turnover rate. We hypothesized that the climatic gradient would result in different C turnover in different parts of the country between northern and southern Sweden. The use of archived soil samples was very valuable for constraining the MRT calculations, which showed that there were differences between the regions. Longest MRT was found in the northernmost region (41 years), with decreasing residence times through the middle (36 years) and central Sweden (28 years), then again increasing in the southwestern region (40 years). The size of the soil organic carbon (SOC) pool in the O horizon was mainly related to differences in litter input and to a lesser degree to MRT. Because N deposition leads both to larger litter input and to longer MRT, we suggest that N deposition contributes significantly to the latitudinal SOC gradient in Scandinavia, with approximately twice as much SOC in the O horizon in the south compared to the north. The data from Birkenes was in good agreement with the Swedish dataset with MRT estimated to 34 years.

Sammendrag

The process of minimising medicine use through dialogue based animal health and welfare planning. Livestock are important in many organic farming systems, and it is an explicit goal to ensure high levels of animal health and welfare (AHW) through good management. In two previous EU network projects, NAHWOA & SAFO, it was concluded that this is not guaranteed merely by following organic standards. Both networks recommended implementation of individual animal health plans to stimulate organic farmers to improve AHW. These plans should include a systematic evaluation of AHW and be implemented through dialogue with each farmer in order to identify goals and plan improvements. 11 research institutions in 7 European countries have been involved in the ANIPLAN project with the main objective to minimise medicine use in organic dairy herds through active and well planned AHW promotion and disease prevention. The project consisted of 5 work packages, 4 of which comprised research activities building on current research projects, new applications across borders, exchange of knowledge, results and conclusions between participating countries, and adopting them to widely different contexts. International and national workshops have facilitated this exchange.  In the project, animal health and welfare planning principles for organic dairy farms under diverse conditions were developed. Animal health and welfare assessments, based on the WelfareQuality parameters, were conducted in different types of organic dairy herds across Europe. Finally, guidelines for communication about animal health and welfare promotion in different settings were also developed relevant to both  existing animal health advisory services or farmer groups such as the Danish Stable School system and the Dutch network program. These proceedings contain the presentations at the final workshop, which also included invited external guests. The proceedings also contain three reports which are deliverables of the project. They are focused on the process of planning for better animal health and welfare, and how farmers and facilitators manage this situation. The focus areas are animal health planning, AHW assessment using animal based parameters and development of advisory systems and farmer groups.

Sammendrag

Cyst nematodes, Heterodera spp. are known world-wide as parasites of cereals and grasses.  Norwegian surveys have revealed that nematodes belonging to the H. avenae complex occur throughout the country; our studies have combined morphology, protein variability (IEF), bio-tests and internal transcribed spacers (ITS3 and ITS5) for the identification of Heterodera populations. Our results showed some divergences between techniques in species identity of some of the studied populations H. avenae is the most common species followed by H. filipjevi (Holgado et al., 2009).. Several populations of H. filipjevi west did not reproduce in oat differentials. In this case both the morphology and protein patterns rather indicated these populations to belong to H. pratensis. In this study a population from Brekstad differed from all other populations in its morphology, and the protein pattern was close to H. mani. This population was collected from barley, and in the pathotype test it was virulent on several barley cultivars. Mathews, 1971reported that H. mani did not reproduce on cereals while (Cook, 1982) indicates that some barley cultivars can serve as hosts. Surprisingly the ITS studies indicated the Brekstad population to be close to H. avenae. This population is in many ways strikingly different from H. avenae, and this result may indicate a need to revise the present gene library of H. avenae. It also demonstrates the need for using several techniques in species identification. In our study the least degree of divergent results on nematode identity is between morphology and IEF.

Sammendrag

Cyst nematodes, Heterodera spp. are known world-wide as parasites of cereals and grasses.  Norwegian surveys have revealed that nematodes belonging to the H. avenae complex occur throughout the country; our studies have combined morphology, protein variability (IEF), bio-tests and internal transcribed spacers (ITS3 and ITS5) for the identification of Heterodera populations. Our results showed some divergences between techniques in species identity of some of the studied populations H. avenae is the most common species followed by H. filipjevi (Holgado et al., 2009).. Several populations of H. filipjevi west did not reproduce in oat differentials. In this case both the morphology and protein patterns rather indicated these populations to belong to H. pratensis. In this study a population from Brekstad differed from all other populations in its morphology, and the protein pattern was close to H. mani. This population was collected from barley, and in the pathotype test it was virulent on several barley cultivars. Mathews, 1971reported that H. mani did not reproduce on cereals while (Cook, 1982) indicates that some barley cultivars can serve as hosts. Surprisingly the ITS studies indicated the Brekstad population to be close to H. avenae. This population is in many ways strikingly different from H. avenae, and this result may indicate a need to revise the present gene library of H. avenae. It also demonstrates the need for using several techniques in species identification. In our study the least degree of divergent results on nematode identity is between morphology and IEF.

Sammendrag

The aim of this study is to see if the raw material influences fixation and leachability of wood preservatives. Moving towards more eco-friendly and –concious society, the wood industries must adjust itself to new rules and regulations. Greener solutions in wood protection are being tested and introduced, older systems are being improved, but questions still arise concerning some elements currently used in wood preservation. Preservatives leaching into the nature is a problem, especially agents that consist copper. Studies have been conducted on the raw material`s influence on impregnability and variations in sapwood penetration have been found. This gives reason to believe that the leaching of wood preservatives is also influenced by the raw material. This study tries to set the variation of leachability of Wolmanit CX-8 and Tanalith into a system, evaluating the origin of a tree and the origin of a sample. The study uses Scots pine (Pinus sylvestris) as a raw material. Material was harvested from different stands in Norway and Denmark. Pine`s sapwood was cut into samples in size of 20x20x50mm. The samples were treated with the wood protection agents Wolmanit CX-8 and Tanalith. The variation in leachability within trees, between trees and between different stands was studied. Within this material, it is possible to trace the individual sample to its original position in the stem. Samples were climatized, impregnated with preservatives and leached according to standard EN84. Copper and boron content in water samples was determined by an ICP (Inductively Coupled Plasma) technique. Comparing leaching results with different variables, correlation was found with latitude and vertical position of the sample, indicating that southern stands leach out more preservative. The lowest part of the tree does not fixate preservatives.

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The trans-border brown bear population of Pasvik-Inari-Pechenga (Norway-Finland-Russia) has been monitored using genetic analyses of feces collection since 2005. In addition in 2007, hair traps were systematically placed out in the area to collect hairs for genetic analysis, to more precisely determine the minimum numbers of bears. In 2011, we repeated this hair trap study, using the exact same methodology as in 2007, to make a direct comparison of the results from the two years. Brown bear DNA was detected in 68 of 88 hair samples (77%) obtained from hair traps in 2011 and for 56 of these samples, a complete DNA profile could be determined. We identified 20 different bears in 2011, 12 females and 8 males. Only one bear was found in more than one country (Norway and Russia). We detected 11 bears in Norway, 7 bears in Finland and 3 bears in Russia in 2011. Four of these 20 bears were previously unknown, all four from Finland. A comparison of the results from 2007 and 2011 showed that we detected fewer bears in hair traps in 2011 (20 bears) than in 2007 (24 bears), but this modest difference may be coincidental. However, we observed a large drop in the yield of hair samples in the traps in 2011 compared to 2007 (88 versus 196 samples). This observation may be suggestive of some reduced activity of bears within the study area in 2011. In addition, only five (21%) of the bears caught in hair traps in 2007 were recaptured in 2011, which indicates a substantial turnover of individuals and may indicate that more frequent hair trapping monitoring would be beneficial to reliably track changes in the population. Additional samples (mainly scats) collected opportunistically in the field within the Russian and Finnish parts of the study area in 2011 detected four male bears in the Finnish part that had not been detected by hair traps. No additional samples from Norway were included to this study and any comparisons between the hair-trapping and opportunistic sampling at this point remains difficult. However, the results indicate that both methods combined are currently the most feasible methods to monitor brown bear numbers in an area.

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Since shrimp farming started in Bangladesh in the 1970s, it has spread throughout the coastal region, increasing soil and water salinity levels. The water salinity in 2005 in the coastal districts of Khulna, Bagherat and Satkhira ranged from 0.3 to 20.7, 0.4 to 27.1 and 0.7 to 24.8 dS m(-1), respectively, whereby it was highly saline for several months of the year. Water salinity above 2.5 dS m(-1) is not suitable for irrigation, and may cause animal health problems. Irrigation with saline water may cause ion toxicity and osmotic stress, reducing plant growth and yield. Salinity has reduced the agro-biodiversity in the coastal regions of Bangladesh, and this paper investigates how these changes have impacted human food habits in the three coastal, rural villages Putia (Satkhira district), Srifaltala (Bagerhat district) and Hogolbunia (Khulna district). Fieldwork was conducted from July to December 2006 and Participatory Rural Appraisal methods including transect walks, key informant interviews, group discussions and personal interviews were carried out. In total, 121 respondents were interviewed and historical data from 1975 to 2006 were collected. For historical data, respondents aged above 50 years were sampled, but additional criteria such as socio-economic condition and farm location were applied to assure a sample representative for the population of the coastal areas. The sampled households had characteristics similar to the major part of Bangladeshi households (rural, agrarian based, regarding family size and food habits), and were thus representative of a broader cross-section of households in Bangladesh. As all sampled villages faced increasing salinity and spread of shrimp farming, they were representative of villages in the coastal areas. When salinity increased, the production of vegetables, seasonal fruits, animal species, eggs and milk declined. As the price of the mentioned animal commodities rose, cheaper commodities such as broilers, exotic and marine fish species and exotic oils were introduced. The decision on what to cultivate was also influenced by non-residents converting the farmers' land into shrimp ponds, increasing the salinity in the surroundings and killing the farmers' ducks. These agro-biodiversity changes caused reduced frequency of consumption of beef, goat, native chicken, egg, local freshwater fish, seasonal fruits, vegetables and milk, while broilers, exotic fish, exotic oils and marine fish species were increasingly consumed. Still, the total fish consumption declined. These changed food habits may lead to considerable negative health consequences for the rural, coastal populations.

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Målet med denne undersøkelsen var å beskrive presisjon og systematiske feil ved tradisjonell høydebonitering (Tveite 1977) i eldre naturskog av gran i høyereliggende skog på indre Østlandet. Dessuten ville vi teste vegetasjonsbonitering (Nilsen & Larsson 1992) og noen mulige korreksjoner av alder ved høydebonitering. Langs bestandsgrenser forårsaket av beltehogster eller eiendomsgrenser, plasserte vi 17 par prøveflater i kommunene Sør Fron, Ringebu og Øyer 700–900 m o.h. Hvert par bestod av én prøveflate i naturskog og én i den tilgrensende kulturskogen slik at det innen par var minst mulig forskjell i høyde over havet, vegetasjonstype, terrengform og jordsmonn. Resultatene viste at tradisjonell høydebonitering ga en gjennomsnittlig underbonitering på 4,2 m. Underboniteringen økte med alder mens overhøyden bare økte svakt med alder. Modellene for alderskorreksjon antyder at avviket i naturskogens overhøydeutvikling fra bonitetskurvene avhenger av vindeksposisjon og jorddybde. Vegetasjonsbonitering ga en underbonitering i samme størrelsesorden som tradisjonell høydebonitering. Underboniteringen skyldes en forskjell i høydeutvikling mellom natur- og kulturskog som vanskelig kan relateres til en enkeltårsak, og som vi fra litteratur på fagfeltet henfører til bl.a. forskjeller i tetthet og genetisk opphav. Vi anbefaler å bruke den presenterte modell 3-alder for alderskorreksjon ved bonitering i naturskog av gran 50–300 høydemeter under skoggrensa der overhøydetrærne er eldre enn 100 år på indre Østlandet.