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.
2010
Sammendrag
VKMs Panel on Plant Health gives the following main conclusions of the pest risk assessment: 1) The pest of concern is the oomycete Phytohthora fragariae Hickman. The PRA area is Norway. P. fragariae is present in at least five limited regions of the PRA area. These regions are located in the counties of i) Hedmark, ii) Aust-Agder and Vest-Agder, iii) Hordaland and Rogaland, iv) Vestfold, and v) Møre og Romsdal. It is probable that the pathogen is present at some places of production without having been detected yet. The pathogen is regulated as a quarantine pest in the PRA area. 2) With the current import regulations there is a medium probability of introduction of P. fragariae through import of infected Rubus plants for planting and a low probability of introduction through import of other consignments. However, there is little updated information available on the presence of the pathogen in different production systems, and there is only very limited evidence that the pathogen can spread by other means than strawberry plants. The level of uncertainty is therefore high. 3) Without the current import regulations there would be a very high probability of introduction through the import of non-certified strawberry plants. The level of uncertainty of this assessment is low. The probability of introduction through import of certified strawberry plants is considered low, but without detailed information on the presence/absence of the pathogen in such material the level of uncertainty is high. 4) With the current pest management procedures the probability of spread within the PRA area is medium for raspberry plants and machinery, other farm implements, footwear and animals. The probability of spread through other pathways ranges from low (legally traded, non-certified strawberry plants, seed potatoes, surface water, waterways and irrigation systems) to very low (remaining pathways). The level of uncertainty is low for certified strawberry plants and medium for legally traded, non-certified strawberry plants. Due to limited knowledge on the spread and survival of the pathogen, the level of uncertainty is high for all other pathways. 5) Without the current pest management procedures the probability of spread with strawberry plants within the PRA area would be very high. The probability of spread with raspberry plants would be high and the probability of spread with seed potatoes, machinery, other farm implements, footwear, animals, surface water, waterways and irrigation systems would be medium. The probability of spread through other pathways would range from low to very low. The level of uncertainty is low for strawberry plants, but due to limited knowledge on the spread and survival of the pathogen, the level of uncertainty is generally high for all other pathways. 6) All strawberry-growing areas in the whole PRA area are considered endangered areas.
Sammendrag
VKM"s Panel 9 gives the following main conclusions of part 2 of the risk assessment: 1) Under the present climatic conditions, and if no control measures are taken, an introduction of PWN to the PRA area will not cause increased pine tree mortality. The level of uncertainty of this assessment is low. 2) Assuming the IS92a climate change scenario for the period 2000-2049 (RegClim), which involves a ~2 ºC temperature increase by the end of the period, an introduction of PWN to the PRA area will, if no control measures are taken, cause a minor increase in pine tree mortality (300 trees per year on average). The mortality can become larger if the temperature increases more than 2 ºC, and will gradually increase with time after 2049 due to spread of PWN. The level of uncertainty of these assessments is medium to high. 3) Any effects of PWN presence in the PRA area on export of wood and wood products will be of little importance. The level uncertainty of this assessment is low. 4) It will be almost impossible to eradicate PWN once it has been introduced to the PRA area. The level of uncertainty of this assessment is low. 5) The cost of a single eradication event as described in the preliminary contingency plan for the PRA area is approximately 700 mill. NOK. Due to expected spread, the total cost of eradication attempts following one introduction event will be approximately 2000 mill. NOK for the first 50 years. The level of uncertainty of these assessments is medium. 6) The negative effects of the control measures on the environment will be major. The level of uncertainty of this assessment is low.
Forfattere
Marcel Van Oijen Ad Schapendonk Mats HøglindSammendrag
Background and Aims The carbon balance of vegetation is dominated by the two large fluxes of photosynthesis (P) and respiration (R). Mechanistic models have attempted to simulate the two fluxes separately, each with their own set of internal and external controls. This has led to model predictions where environmental change causes R to exceed P, with consequent dieback of vegetation. However, empirical evidence suggests that the R : P ratio is constrained to a narrow range of about 0·4-0·5. Physiological explanations for the narrow range are not conclusive. The aim of this work is to introduce a novel perspective by theoretical study of the quantitative relationship between the four carbon fluxes of P, R, growth and storage (or its inverse, remobilization). Methods Starting from the law of conservation of mass - in this case carbon - equations are derived for the relative magnitudes of all carbon fluxes, which depend on only two parameters: the R : P ratio and the relative rate of storage of carbon in remobilizable reserves. The equations are used to explain observed flux ratios and to analyse incomplete data sets of carbon fluxes. Key Results The storage rate is shown to be a freely varying parameter, whereas R : P is narrowly constrained. This explains the constancy of the ratio reported in the literature. With the information thus gained, a data set of R and P in grassland was analysed, and flux estimates could be derived for the periods after cuts in which plant growth is dominated by remobilization before photosynthesis takes over. Conclusions It is concluded that the relative magnitudes of photosynthesis, respiration, growth and substrate storage are indeed tightly constrained, but because of mass conservation rather than for physiological reasons. This facilitates analysis of incomplete data sets. Mechanistic models, as the embodiment of physiological mechanisms, need to show consistency with the constraints.
Forfattere
Aslaf Belachew Arne Stensvand Nina Trandem Vitalis Wafula Wekesa Gilberto de Moraes Ingeborg KlingenSammendrag
The co-occurrence of powdery mildew, Podosphaera aphanis, and the two-spotted spider mite, Tetranychus urticae, on strawberry plants requires a strategic use of fungicides to control powdery mildew without harming predatory mites and other beneficial organisms. Sulfur has been used for two centuries to manage powdery mildew and is the only fungicide approved for use in organic strawberry production in Norway. However, there are contrasting reports in the literature about the effect of sulfur on predatory mites and two-spotted spider mite from field studies. Controlled laboratory experiments were therefore conducted on strawberry leaf disks to study the main as well as the interacting effects of sulfur on P. aphanis, T. urticae and the predatory mite, Phytoseiulus persimilis. The following seven treatment combinations: 1) Sulfur + P. aphanis 2) Sulfur + T. urticae 3) Sulfur + P. persimilis 4) Sulfur + P.aphanis + P.persimilis 5) Sulfur + P.aphanis + T.urticae 6) Sulfur + P. Persimilis + T.urticae 7) Sulfur + P.aphanis + P.persimilis + T.urticae and seven parallel treatment combinations with water instead of sulfur (control) were used. Leaf disks were dipped in a sulfur (Thiovit Jet) solution or water and inoculated with P. aphanis after the sulfur/ water had dried on the leaf surface. In treatments with mites, five female T. urticae and one female P. persimilis were added per leaf disk. Preliminary analysis of the results showed that only the predatory mite and sulfur significantly (P ≤ 0.05) affected egg production and mortality of T. urticae. In the treatment that combined sulfur + P. aphanis + P. persimilis + T. urticae a significantly reduction in T. urticae egg production was seen. However, there was no significant effect on egg production and mortality of T. urticae in the three-way or two-way interactions of sulfur, powdery mildew and predatory mite. There was no significant effect of sulfur on mortality of P. persimilis, and sulfur did not seem to affect the efficiency of this predatory mite. Powdery mildew did not affect T. urticae probably because the mildew was not well developed due to inoculation at the same time as the mites were added. In another experiment, however, mites were released on leaf disks that had well developed powdery mildew, and here a negative effect of the mildew on T. urticae egg production was clearly seen.
Forfattere
Espen Govasmark Børge Holen Jessica Stäb Mirja Salkinoja-Salonen Douwe Hoornstra Hilde Marit Østlie Tommy NesbakkSammendrag
Det er ikke registrert sammendrag
Sammendrag
The report discusses strategies for the utilization of anaerobically treated poultry manure and slaughterhouse waste (ADR) from Lusakert Poultry Plant Production (LPPP) at Lusakert Biogas Plant (LBP), Kotayk Region, Armenia. ADR is currently an untapped resource of nutrients stored in lagoons, while at the same time representing a source of pollution for the Hsradan river. The project"s two goals were to 1) contribute to the reduction in waste disposed in lagoons from LBP and 2) increase recycling of organic wastes in Armenia. Both goals will contribute to sustainable resource management in Armenia. Anaerobically digested residue from LBP represents an untapped source of essential nutrients for crop production in Armenia. Plant nutrients in ADR are readily available. When ADR is used as fertilizer, crop yields similar to those achieved with the use of mineral fertilizers may be obtained. However, distribution of ADR from the biogas plant to the surrounding farms requires transport by tanker trucks, and the transport distances are longer than what is common for transport of liquid organic fertilizers in the Nordic countries. It is also necessary to develop an infrastructure for storing the ADR at the individual recipient or in greater common stock near the farms. An alternative is to store ADR in the lagoons of LBP and pump it on tanker trucks that run directly to the farmer"s fields, where it is spread immediately. However, this option can only be conducted during the growing season. Alternatively, the ADR can be used to produce solid organic fertilizer and soil conditioner, which would facilitate transportation and storage. This can be done by 1) aerobic composting, 2) vermi-composting and 3) concentrating nutrients in ADR to a solid that can be separated from the liquid. All these strategies can produce a valuable fertilizer, but the market for such products needs to be developed in Armenia. ADR or composted ADR can contain contaminants with health and environmental risks, depending on the origin of the raw material used. If mushroom waste is used as a substrate for the composting of ADR, the heavy metal content of the final compost is not expected to be much lower than in ADR because mushroom waste of interest is based on chicken manure. By using straw or other suitable plant material as a substrate, it is likely that the heavy metal content is reduced. The concentrations of organic pollutants in composted ADR from LBP are expected to be low, due to expected low concentrations of organic contaminants in poultry manure and slaughterhouse waste. It is also assumed that veterinary pharmaceuticals do not pose a risk through the use of ADR or composted ADR. There is a risk that pathogenic bacteria are found in the ADR and composted ADR, but these bacteria are not in their natural environment, and it is unknown whether pathogen contamination is a real risk to the public by the use of ADR in agriculture. Armenia has an Agriculture Support Republican Center, which heads the Agriculture Support Regional Centers. The regional centers provide counseling to farmers in Armenia. The Agriculture Support Centers should be strengthened and further developed as a strategy for optimal use of ADR in Armenian agriculture. Collaboration between the biogas plants, farmers, farmer organizations, non-governmental organizations (NGOs), government organizations and scientific institutions should be developed with the common goal of helping to develop good management practices for optimum utilization of ADR as organic fertilizer in Armenia.
Forfattere
Espen Govasmark Anicke Brandt-Kjelsen Brit SalbuSammendrag
The diet is the major source of Se to man and intake of this essential element depends on the Se concentration in food and the amount of food consumed. Since the levels of Se in agricultural products in Northern Europe are generally low, Se deficiency to man and animal is a significant problem in many countries. Agronomic Se-fortification of plant products is one strategy to increase the human Se intake. Estimation of diets for Se adequacy requires information not only on the total Se, but also on Se-species, accessibility, bioavailability of Se-species in food. Therefore, the present work focuses on the distribution and speciation of Se in Se enriched wheat grains and its accessibility estimated from extraction with human gastro intestinal juices (HGIJ) and Se bioavailability to chicken determined as the bioconcentration factor (BCF); breast muscle/feed intake Se concentration. In the present work, wheat grains were Se-selenate enriched by soil or foliar fertilisation in a greenhouse experiment at seeding or tillering with or without a spilt nitrogen fertilisation strategy to investigate (1) if the Se-species distribution in grains were affected. Then, field grown Se-enriched wheat grains were used (2) to estimate the total and Se-species distribution in the flour and bran and its accessibility, as chicken feed (3) to estimate the Se BCF and as ingredience in bread (4) to investigate Se-transformation and estimate the Se-accessibility from wheat flour to bakery product. Se-speciation was performed using an anion exchange-HPLC-ICP/MS system with 25-250 mM NH4Ac, pH 5.1 gradient elution. The Se fertilisation with selenate at tillering is more efficient than at seedling and additional N-fertilisation at tillering increases the Se-uptake and re-translocation from leaf to grains. Selenomethionine (SeMet) was the dominant Se-species in the grains, but an unidentified Se-species (Se-cysteine?) is to be investigated. Selenate fertilization closest to grain filing period had a higher proportion of selenate and a lower ratio between SeMet and the unidentified Se species, than Se fertilization at seeding. N fertilisation did not affect the Se-species distribution. The Se concentration in field grown wheat grains was 1.2 mg Se kg-1, while the concentrations in flour and bran were 1.1 and 1.6 mg Se kg-1, respectively. The main Se-species in the bran and flour was SeMet. The flour and bran HGIJ extraction showed that Se in the flour was more accessible than in the bran, but since the bran has a higher Se concentration, the amount of Se accessible was about the same for flour and bran. The BCF in chicken breast muscle increased from 0.6 to 1.9 by changing from selenite to Se-enriched whole wheat as dietary Se source, thus Se-enriched wheat was more efficient in increasing the chicken meat Se concentration. The bread making procedure did not influence the Se-species distribution when compared to unprocessed flour. The Se-accessibility was higher in the bread kernel compared to the crust, most probably due to high temperature during roasting. High content of bran in the bread decreased the Se-accessibility Thus, agronomic Se-fortification of Se to wheat is a good strategy to increase the human dietary intake and potentially also the human population Se status.
Forfattere
Espen Govasmark Anicke Brandt-Kjelsen Brit SalbuSammendrag
The diet is the major source of Se to man and intake of this essential element depends on the Se concentration in food and the amount of food consumed. Since the levels of Se in agricultural products in Northern Europe are generally low, Se deficiency to man and animal is a significant problem in many countries. Agronomic Se-fortification of plant products is one strategy to increase the human Se intake. Estimation of diets for Se adequacy requires information not only on the total Se, but also on Se-species, accessibility, bioavailability of Se-species in food. Therefore, the present work focuses on the distribution and speciation of Se in Se enriched wheat grains and its accessibility estimated from extraction with human gastro intestinal juices (HGIJ) and Se bioavailability to chicken determined as the bioconcentration factor (BCF); breast muscle/feed intake Se concentration. In the present work, wheat grains were Se-selenate enriched by soil or foliar fertilisation in a greenhouse experiment at seeding or tillering with or without a spilt nitrogen fertilisation strategy to investigate (1) if the Se-species distribution in grains were affected. Then, field grown Se-enriched wheat grains were used (2) to estimate the total and Se-species distribution in the flour and bran and its accessibility, as chicken feed (3) to estimate the Se BCF and as ingredience in bread (4) to investigate Se-transformation and estimate the Se-accessibility from wheat flour to bakery product. Se-speciation was performed using an anion exchange-HPLC-ICP/MS system with 25-250 mM NH4Ac, pH 5.1 gradient elution. The Se fertilisation with selenate at tillering is more efficient than at seedling and additional N-fertilisation at tillering increases the Se-uptake and re-translocation from leaf to grains. Selenomethionine (SeMet) was the dominant Se-species in the grains, but an unidentified Se-species (Se-cysteine?) is to be investigated. Selenate fertilization closest to grain filing period had a higher proportion of selenate and a lower ratio between SeMet and the unidentified Se species, than Se fertilization at seeding. N fertilisation did not affect the Se-species distribution. The Se concentration in field grown wheat grains was 1.2 mg Se kg-1, while the concentrations in flour and bran were 1.1 and 1.6 mg Se kg-1, respectively. The main Se-species in the bran and flour was SeMet. The flour and bran HGIJ extraction showed that Se in the flour was more accessible than in the bran, but since the bran has a higher Se concentration, the amount of Se accessible was about the same for flour and bran. The BCF in chicken breast muscle increased from 0.6 to 1.9 by changing from selenite to Se-enriched whole wheat as dietary Se source, thus Se-enriched wheat was more efficient in increasing the chicken meat Se concentration. The bread making procedure did not influence the Se-species distribution when compared to unprocessed flour. The Se-accessibility was higher in the bread kernel compared to the crust, most probably due to high temperature during roasting. High content of bran in the bread decreased the Se-accessibility Thus, agronomic Se-fortification of Se to wheat is a good strategy to increase the human dietary intake and potentially also the human population Se status.
Forfattere
Espen Govasmark Jessica Stäb Børge Holen Mirja Salkinoja-Salonen Douve HoornstraSammendrag
The European Union Council directive 1999/31/EC states that no waste should be deposited on landfills without being treated in some way. Source separating of organic wastes at the household is one way of treating the waste to reduce the amount of waste entering the landfill. Anaerobic digestion on biogas plants (BGP) is a management strategy of organic wastes which combines recycling of plant nutrients in organic waste with production of renewable energy (Hartmann & Ahring 2006). The anaerobic digested residue (ADR) can be used as fertilizer, thereby recycling nutrients back to agriculture and horticulture. However, the ADR is not a harmless product since it may contain pollutants such as heavy metals, organic pollutants and pesticide but also pathogenic bacteria which are introduced to the soil ecosystem by its application (Kupper at al. 2008; Brändli et al 2007; Brändli et al., 2005; Sahlström 2003). Therefore, it is important to assess the safety of using digestate as fertilizer with respect to the chemical and bacteriological content. Anaerobically digested organic waste was analysed for the content of heavy metals, organic pollutants, pesticides and the bacteria E.coli and B.cereus each month in a year. The digestate was separated into a fiber and liquid fraction by centrifugation at the BGP. Heavy metal concentrations (mg/kg DM) in the fiber was (min-max); Zn (162-364), Cu (34-69), Cd (0.2-0.4), Ni (6-19), Cr (15-33), Pb (6-13) and Hg (0.03-0.17), and in the liquid; Zn (132-422), Cu (23-57), Cd (0.2-0.6), Ni (3-11), Pb (4-6) and Hg (0.05-0.15). Organic pollutant and pesticide concentrations (µg/kg DM) in the fiber was: ∑PAH 16 (585-1544), ∑PBDE (2.4-9.5), DEHP (13440-64874), Imazalil (380-4190) and Tiabendazol (140-670) and in the liquid: ∑PAH 16 (n.d-65), ∑PBDE (n.d-0.2), DEHP (233-2113), Imazalil (370-5770) and Tiabendazol (n.d-730). The digestate did not contain viable E.coli but contained 0.5 to 10 × 106 viable B.cereus per ml of which 1 % were heat stable spores. Culturable presumptive B.cereus was isolated in 9 out of 10 samples. The concentration of heavy metals was within class I according to the Norwegian standard. Only DEHP were found in concentrations higher than the threshold values for composts in Austria and Denmark, but lower than for sewage sludge used as fertilizer in EU. The concentration of Imazalil and Thiabendazol was higher than expected, but not threshold are available. Analysis of DNA showed that the digestate contained B. cereus and a portion of the B. cereus genomes possessed the cesB gene. Approximately 1 % of the heat stable spores represented B. cereus. The content of viable B. cereus in the digestate was acceptable for foods. The authors therefor conclude that the digestate is safe to use as fertilizers in agriculture with respect to heavy metals, organic pollutants, pesticides and the bacteria E.coli and B.cereus. REFERENCES Brändli, R.C., Bucheli, T.D., Kupper, T., Mayer, J., Stadelmann, F.X. & Tarradellas, J. 2007. Fate of PCBs, PAHs and their sorce characteristics ratios during composting and digestion of source-separated organic waste in full-scale plants. Environmental Pollution 148, pp. 520-528. Brändli, R.C., Bucheli, T.D., Kupper, T., Furrer, R., Stadelmann, F.X., & Tarradellas, J. 2005. Persistent Organic Pollutants in Source-Separated Compost and Its Feedstock Materials - a Review of Field Studies. Journal of Environmental. Quality 34(3), pp. 735-760. EC. 1999. Council directive of 1999/31/EC on 26 April 1999 on the landfill of waste. Official Journal of the European Communities, European commission, Brussels, Belgium, L182, pp 1-19. Hartmann, H. & Ahring B.K. 2006. Strategies for the anaerobic digestion of the organic fraction of municipal solid waste; an overview. Water Science. Technology 53 (8), pp. 7-22. Kupper, T., Bucheli, T.D., Brändli, R.C., Ortelli, D. & Edder,P. 2008. Dissipation of pesticides during composting and anaerobic digestion of source-separated organic waste at full-scale plants. Bioresource Technology 99, pp. 7988-7994. Sahlström, L. 2003. A review of survival of pathogenic bacteria in organic waste used in biogas plants. Bioresource Technology 87, pp. 161-166.
Forfattere
Carola Strassner Melanie Lukas Anne-Kristin LøesSammendrag
I prosjektet "Økologisk mat til ungdommen", iPOPY (innovative Public Organic food Procurement for Youth) var et av arbeidsområdene kartlegging av flaskehalser i forbindelse med selve matforsyningen (supply chains) og i hvilken grad de ulike landene som deltok i prosjektet har utviklet noen form for godkjenning på dette området. Primærproduksjon og foredling av økologiske matvarer er underlagt regler på EU-nivå. Som en del av EØS-avtalen gjelder dette regelverket også i Norge. For catering, restauranter og annen matservering i ikke-privat regi er det imidlertid ingen regler på EU-nivå. Ulike land har derfor utviklet ulike løsninger for å sertifisere for eksempel restauranter som ønsker å markedsføre servering av økologisk mat.Denne rapporten gjennomgår ordningene i Danmark, Finland, Italia, Norge og Tyskland. Tyskland er brukt som referanse siden de har et godt utviklet system som førsteforfatter av rapporten, Dr. Carola Strassner, kjenner godt fra tidligere kartleggingsarbeid. Rapporten er basert på informasjon fra godkjenningsorganisasjoner og eksperter i hvert land innhentet gjennom spørreskjema som ble besvart via e-post, og oppfølgende telefonintervju.Det er stor variasjon mellom de ulike landene. Danmark har et frivillig system med bronse-, sølv- og gullmedaljer avhengig av andel økologiske råvarer. I Finland er det heller ikke noe krav om sertifisering av matservering, men et frivillig trinnvis system med fem nivå for økende andel økologiske råvarer. Systemet inkluderer rådgivning og et sertifikat som kan brukes i markedsføring. Italia har foreløpig ikke noe krav til sertifisering, men det pågår aktiviteter for å etablere en frivillig eller obligatorisk ordning. I Norge og Tyskland er det krav om sertifisering av virksomheter som vil markedsføre seg med servering av økologisk mat.Italienske aktører ytret ønske om mer standardiserte regler på dette området, mens aktørene i øvrige land sa seg fornøyd med situasjonen slik den var.Sertifisering av økologisk matservering i skoler vil innebære noe ekstra arbeid, men vil samtidig gi serveringen et kvalitetsstempel, øke tilliten hos brukerne og bidra til å synliggjøre en økologisk innsats.