The Norwegian Scientific Committee for Food Safety (VKM) has appointed an ad hoc-group of experts to answer a request from the Norwegian Food Safety Authority regarding benefit and risk assessment of Lactobacillus paracasei ssp. paracasei F19 (F19) in processed cerealbased baby foods intended for small children 1-3 years. This assessment is based on the literature provided by the notifier as well as that found by a MEDLINE search. A notification regarding two products of processed cereal-based baby foods (hereafter called cereals), intended for small children and supplemented with the bacterium F19 initiated this work. A daily supply of a monoculture of a particular bacterial strain in large quantities to an age group without a fully established intestinal flora, may have unknown adverse effects. There are however, to our knowledge, no studies investigating possible short or long term adverse health effects of F19 in processed cereal-based baby food given to children 13 months onwards. The documentation and information provided by the notifier regarding the genetic stability of F19 in the two products during processing and storage, is considered insufficient and does not allow any conclusions to be drawn. Moreover, the documentation obtained is not conclusive regarding the antibiotic resistance pattern of the bacterial strain used in the products in question, as the information on different antibiotics is partly inconsistent. The information about specific localization (chromosomal, plasmid) of the resistance genes is not sufficient. Studies demonstrate that F19, as well as other bacterial strains considered probiotic, is able to “crosstalk” with enterocytes in mice and that the result of the “crosstalk” depends upon the microbiota present. Whether F19 has a similar “crosstalk-profile” in humans is unknown. However, as the strain is originally of human origin, it seems reasonable to assume that such “crosstalk” may occur. Thus, before giving F19 daily for months and years, it seems reasonable to ask for additional molecular and physiological studies to unravel the functional impact of possible changes in genetic expression in children. Lactobacillus infections do occasionally occur, mainly as bacteremia, endocarditis and localized infections (e.g. abscesses, peritonitis, and meningitis) in patients with severe underlying diseases. Most of them are elderly, but children are not excluded. The species most often isolated are L. casei and L. rhamnosus, followed by L. paracasei. The increasing use of immunosuppressive therapy and broad spectrum antibiotics which are ineffective against Lactobacillus, might increase the importance of these bacteria as possible pathogens. In order to be able to draw any conclusions regarding beneficial effects of F19, there is a need for randomized placebo-controlled studies in larger populations and in the relevant age group. According to EFSA, Lactobacillus paracasei ssp. paracasei F19 is sufficiently characterized. The documentation provided is, however, not sufficient to claim positive health effects and thus F19 is not proven to be probiotic. There are no published dose-response studies of F19 in children, neither regarding survival of F19 in the gastrointestinal tract, nor possible negative health effects. Thus the potential for negative health effects as e.g. spreading of antimicrobial resistance or unfavourable impact on the genetic expression in children related to the frequency and/or dose of a monoculture of F19 cannot be assessed.

The Norwegian department of agriculture decided to re-evaluate the Regulation No. 951 of 4 July 2003 on fertilizers and soil improvers of organic origin. The Norwegian Food Safety Authority (NFSA) requested VKM for a statement on the use of manure from farms where grey water and human waste (sewage) is disposed of directly to the farm manure cellar. Consideration was given to differences in risk according to the types of domestic wastewater, the species of animal from which the manure derived, the extent and type of sanitary facilities, the crops to which the amended manure is applied, and the effects of storage on infection risk. According to current legislation, sewage sludge cannot be spread on land where vegetables, potatoes, berries or fruit are grown. Furthermore, sewage cannot be spread on meadows or used for horticultural purposes. In private gardens, parks, playgrounds and similar residential areas, sewage may be used only as a component in a fertiliser, and not applied at the surface. Use of sewage as a fertilizer for the cultivation of grains is permitted. Sewage can also be used when establishing vegetation along roads and embankments. VKM concludes that manure cellars, to which wastewater, from private household use, and sewage from toilets in the outbuildings are drained, may contain pathogens from humans, in addition to those pathogens originating from animals. The quantity and species of pathogens in this sewage-amended manure would reflect the species and prevalence of pathogens in the population using the facilities. Although the prevalence of intestinal pathogens in the Norwegian human population is relatively low, it should be noted that farms in Norway often provide tourist accommodation, camping facilities, and may house migrant short-term employees during the summer season during which labour requirements are increased. Thus non-Norwegian populations may also use toilet facilities on these farms, and thus when considering the risk of human pathogens, consideration should also be given to people from countries where the prevalence of such pathogens may be higher. As many viruses and parasites are host-specific, the risk of contamination of produce with human pathogens from such manure is likely to be greater than from manure which has not been amended with untreated sewage. Pathogen survival is affected by storage, but it should be noted that some pathogens have robust and environmentally resistant transmission stages (e.g. parasite oocysts, cysts and eggs), a proportion of which may survive for prolonged periods in stored manure.

In the light of the recent findings of the tapeworm Echinococcus multilocularis (EM) in four red foxes from three different locations in Sweden, the Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen; VKM), Panel of Biological Hazards (Faggruppe hygiene og smittestoffer) took the initiative to undertake a risk assessment regarding the probability of this parasite being introduced to mainland Norway and thus becoming a threat to public health in the country. EM is a small tapeworm that resides in the intestine of carnivores (e.g. foxes, dogs) that function as final hosts for the adult tapeworm. The infection here gives few or no symptoms. Adult tapeworms produce eggs that are released in the faeces of the carnivores and may be ingested by mammals, usually rodents or lagomorphs1, which act as intermediate hosts. In the intermediate hosts, the larval form of the tapeworm produces cysts, predominantly in the liver, where they proliferate and may invade the surrounding tissues. If the infected intermediate host is eaten by a susceptible final host, the adult tapeworm develops in the intestine and the lifecycle is completed. EM is of public health significance as humans may act as accidental intermediate hosts if they ingest eggs, either through contaminated foods or water, or from contact with infected final hosts (dogs, foxes) or their faeces. In untreated patients the disease is often fatal (10 year survival rate of 29 %), and in treated patients the 10 year survival rate is 80 %. The anthelmintic treatment is long-term (for several years, possibly life-long) and expensive. Liver transplantation may be required. Conclusions: Based on the fact that EM is endemic in many European countries, that the incidence in endemic countries is increasing, and that the areas of endemicity are expanding it seems likely that EM will be imported into Norway at some point, perhaps within the next 10 years. Given the high numbers of pets crossing the border between Sweden and Norway and the paucity of checks regarding compliance with treatment legislation, this seems to be a likely route of entry of EM to Norway, should this occur. Introduction of checks may reduce this likelihood. Under the current monitoring conditions, VKM find it less likely that EM will be detected upon the first introduction to Norway. EM will probably only be detected once the prevalence in foxes is greater than 1%. The red fox population size is estimated to be between 70 000 to 120 000 animals. This means between 700 to 1200 red foxes would need to be infected before EM infection is likely to be detected under the current monitoring program. If EM is identified early enough after introduction, then it might be possible to avoid the establishment of EM in Norway and/or to limit the region of endemicity. This is dependent on optimal detection techniques and sufficient monitoring. VKM considers that it is unlikely that EM will be imported to Norway via contaminated produce (berries, fruits and mushrooms). Norway’s strong ‘outdoor’ culture, in which hunting, camping, berry-picking and other outdoor activities play a significant role, may place the Norwegian population at greater likelihood of contracting EM than populations in other European countries. However, it should be noted that even in countries with endemic EM, human echinococcosis is, apparently, relatively rare.

Potentially toxic metals (PTM), along with PTM-resistant bacteria and PTM-resistance genes may be introduced to soil and water through sewage systems, direct excretion, land application of biosolids (organic matter recycled from sewage, especially for use in agriculture) or animal manures as fertilisers, and irrigation with wastewater or treated effluents. The Norwegian Food Safety Authority (NFSA) asked the Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen for mattrygghet, VKM) for an assessment of the link between antimicrobial resistance (AMR) and potentially toxic metals (PTM) in soil and fertilising products. The NFSA would like VKM to give an opinion on the following question related to the influence of potentially toxic metals on antimicrobial resistance: Can the content of arsenic (As), cadmium (Cd), chromium (CrIII + CrVI), copper (Cu), lead (Pb), mercury (Hg), nickel (Ni), and zinc (Zn) in soil and fertilising products that are relevant for Norway play a role in the development, spreading, and persistence of bacterial resistance to these elements, as well as cross or co-resistance to antimicrobial agents? VKM appointed a working group, consisting of two members of the Panel on Biological Hazards, to prepare a draft Opinion document and answer the questions. The Panel on Biological Hazards has reviewed and revised the draft prepared by the working group and approved the Opinion document “The link between antimicrobial resistance and the content of potentially toxic metals in soil and fertilising products”. In this report we assess the following PTM: arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), nickel (Ni), mercury (Hg), lead (Pb), and zinc (Zn), because of their possible presence in fertilisers and their potential to induce AMR in bacteria. This assessment is based on internationally published data. There is no systematic monitoring for toxic metals in soils in Norway, and the levels are expected to be highly variable depending on the input sources, previous and current agricultural practices, and the characteristics of the soil. Data on PTM in fertilising products added to soil are also fragmented and limited. Fertilising materials, in the form of sewage sludge or livestock manure, will add toxic metals to the existing levels in soil, and in areas of intensive agriculture, the levels will be expected to be highest. The additive effect of toxic metals in fertilising materials must be assessed from a long-term perspective, as these metals accumulate in the environment. Development of AMR can be partly regarded as a dose- and time-dependant response to exposure to different drivers for resistance. There is an indication that the presence of potentially toxic metals is a driver for development of AMR in exposed bacteria, but the dose and time exposure most likely to cause this effect is not known. Investigation of PTM-driven co-selection of AMR in environments impacted by agriculture and aquaculture should focus especially on Cu and Zn, which are added to animal feed, and on Cd because of its high concentration, in comparison with other PTM, in inorganic fertilising products. The naturally occurring background resistance in environmental bacteria complicates the estimation of the effect of PTM exposure on development of resistance. In addition, it is difficult to distinguish between the natural resistome and an elevated abundance of AMR in environmental samples. Spreading of resistance towards the PTM evaluated in this assessment involves cross- and co-resistance to antimicrobial agents used in prophylaxis and therapy in animals and people. Most important are those cases where toxic metal resistance is coupled to resistance towards highly important and critically important antibiotics. This has been described in some of the published articles included in this assessment. We do not fully understand the mechanisms behind persistence of AMR, and removing drivers for development and spread of resistance may result in a decrease in the levels of resistance, but not necessarily full disappearance. There is lack of knowledge regarding links between the level and concentration of PTM in fertilising products and soil and development of resistance in bacteria. Data regarding the routes and frequencies of transmission of AMR from bacteria of environmental origin to bacteria of animal and human origin were lacking in the published articles reviewed here. Due to the lack of such data, it is difficult to estimate the probability of development, transmission, and persistence of PTM resistance in the Norwegian environment. More research is needed to explain the relationship between development of resistance against potential toxic metals and resistance toward antimicrobial agents in bacteria.

The Norwegian Scientific Commitee for Food Safety (VKM) appointed a working group of experts to answer a request from the Norwegian Food Safety Authority regarding health risk assessment of Lactobacillus reuteri Protectis® in a food supplement intended for use by infants and young children. The mandate of this health risk assessment was not to evaluate the health claims related to the products as such health claims are assessed by EFSA. The specific strain DSM 17938 is a “daughter strain” of the strain ATCC 55730 which was originally isolated from normal human milk. ATCC 55730 harbours two plasmids carrying transferable resistance genes against tetracycline and lincosamides respectively. The “daughter strain” DSM 17938 was established in 2008 by curing the ATCC 55730 for these plasmids, but is in all other respects claimed to be identical to ATCC 55730 and bioequivalence of the two strains has been suggested. The strain DSM 17938 was still resistant to tetracycline (although at a considerably lower level than ATCC 55730) and a number of other antibiotics, but these resistances were all considered being intrinsic by FBO. The absence of possible transferable/mobile genes has, to our knowledge, not been confirmed in later studies. We are not aware of any data indicating that L. reuteri has been the cause of serious human diseases – and none of the studies examined has reported any adverse or undesirable short time effects. It has also been used in preterm infants with dosage corresponding to the actual recommended doses - without reporting any adverse, short term reaction. There is therefore no evidence leading to consider the strain DSM 17938 at the dosage recommended as unsafe. However, more long-term data are still lacking and the long-term safety for the age groups considered in this assessment cannot be established. As evidence is accruing that the early microbial composition of the infant gut is important for the development of the gut flora and the immune system of the growing child, it is not possible to exclude that a daily supply of a particular bacterial strain over a prolonged period of time to an immature gastro-intestinal tract may have long-term, albeit still unknown, adverse effects on it’s development. As the long-term data are lacking it is not possible to answer whether the amount of the food supplement or the age of the infant or young child is of importance. However, if later long-term data should reveal any adverse reaction, it is reasonable to assume that the actual age group will be the most vulnerable. As the safety was not entirely established, the question of whether there are any vulnerable groups (i.e. premature, infants or children with diseases) where there are health risks associated with the intake of Lactobacillus reuteri Protectis®, as a food supplement was not considered.

The Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen for mattrygghet, VKM) has, at the request of the Norwegian Food Safety Authority (Mattilsynet; NFSA), assessed the risk of "other substances" in food supplements sold in Norway. These risk assessments will provide NFSA with the scientific basis for regulation of the addition of “other substances” to food supplements and other foods. "Other substances" are described in the food supplement directive 2002/46/EC as substances other than vitamins or minerals that have a nutritional and/or physiological effect. It is added mainly to food supplements, but also to other foods. VKM has not in this series of risk assessments of "other substances" evaluated any claimed beneficial effects from these substances, only possible adverse effects. The present report is a risk assessment of Lactobacillus rhamnosus Rosell-11 ND, Lactobacillus rhamnosus W71, Lactobacillus rhamnosus GG and Lactobacillus rhamnosus Lr-329 based on previous risk assessments and also publications retrieved from literature search. The risk of the Lactobacillus strains listed above was assessed for the general population. However, in previous assessments of probiotics published by VKM, concerns have been identified for specific groups. Therefore, the risk was assessed for the age group with immature gastro-intestinal microbiota (age group 0-36 months), population with mature gastro-intestinal microbiota (>3 years) and vulnerable groups with mature gastro-intestinal tract. VKM has also assessed the risk of L. rhamnosus Rosell-11 ND, L. rhamnosus W71, L. rhamnosus GG and L. rhamnosus Lr-329 in food supplements and other foods independent of the dose and have assessed exposure in general terms. VKM concludes that it is unlikely that L. rhamnosus Rosell-11 ND, L. rhamnosus W71, L. rhamnosus GG and L. rhamnosus Lr-329 would cause adverse health effects in the general healthy population with mature gastro-intestinal tract. However, no data on long-term adverse effects on infants and young children were identified. As evidence is accruing that the early microbial composition of the neonatal gut is important for the development of the gut microbiota and the immune system of the growing child, it is not possible to exclude that a daily supply of a single particular bacterial strain over a prolonged period of time to an immature gastro-intestinal tract may have long-term, although still unknown, adverse effects on that development.

The Norwegian Food Safety Authority (NFSA) and Norwegian Environmental Authority (NEA) asked the Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen for mattrygghet, VKM) for an opinion on factors associated with the introduction of Chronic Wasting Disease (CWD) to Norway. VKM appointed a working group consisting of two members of the Panel on Biological Hazards, one member of Panel on Animal Health and Welfare, and two external experts to prepare the answer to the questions. The Panel on Biological Hazards has reviewed and revised the draft prepared by the working group and approved the opinion. CWD was diagnosed in March 2016 in a wild reindeer (Rangifer tarandus) from the Nordfjella mountain area in Norway and in May and June in two mooses (Alces alces) in Selbu in South Trøndelag County, approximately 300 km north from the first case. There is currently no information to determine the origin(s) of CWD agents in Norway. However, the sporadic or genetic (somatic mutation) occurrence of prion disease in cervids cannot be excluded, nor can introduction from North America or other countries. Furthermore, there is no evidence that it has not been circulating at low levels in the Norwegian cervid populations for years, but has not previously been identified. In this scientific opinion, information on prion diseases in general, and CWD in particular, is presented in the light of experiences with this disease in North America. Prions are among the most resilient pathogens known and dissemination of prions into ecosystems is likely to result in long-term problems. Prions bind strongly to soil and remain infectious. In CWD, prions are present in most peripheral organs and also shed into the environment via saliva, faeces, and urine, as well as with the placenta. CWD transmits easily among cervids, either through direct contact, or indirectly via the environment. Migration of animals is relevant for the spread between areas. Strain diversification might occur in CWD and may influence transmission properties of the agents. Clinical signs of CWD are non-specific and do not alone enable confirmation of the diagnosis. Analysis of tissue from the brainstem at the level of the obex by approved methods is necessary for diagnosis of CWD. Prion infectivity is assessed by bioassays, often involving transgenic mice. In vitro conversion assays, like protein misfolding cyclic amplification (PMCA), provide sensitive quantification of converting activity, which is a good approximation of infectivity. Genetic variation (polymorphisms) in the gene that encodes PrP (PRNP) can modulate sensitivity towards CWD. The level of such genetic variation in Norwegian wild and semi-domesticated cervids is currently unknown. Cattle and sheep are at very low risk of developing CWD and it is highly unlikely that prion diseases in sheep or cattle are the origin of CWD. Although transmission of CWD to humans has never been known to occur, and animals other than cervids have not been found to be infected, indicating a species barrier, this possibility cannot be excluded. Thus, measures for reduction of human exposure are recommended. Taking into account uncertainties regarding the plasticity of the CWD agents and the lack of transmission data from the Norwegian isolates, this scientific opinion considers the zoonotic risk of CWD to be very low.

The Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen for mattrygghet, VKM) has, at the request of the Norwegian Food Safety Authority (Mattilsynet; NFSA), assessed the risk of "other substances" in food supplements sold in Norway. These risk assessments will provide NFSA with the scientific basis for regulation of the addition of “other substances” to food supplements and other foods. "Other substances" are described in the food supplement directive 2002/46/EC as substances other than vitamins or minerals that have a nutritional and/or physiological effect. It is added mainly to food supplements, but also to other foods. VKM has not in this series of risk assessments of "other substances" evaluated any claimed beneficial effects from these substances, only possible adverse effects. The present report is a risk assessment of Lactobacillus acidophilus W37, Lactobacillus acidophilus DDS-1, Lactobacillus acidophilus La-5 and Lactobacillus acidophilus La-14 based on previous risk assessments and also publications retrieved from literature search. The risk of the Lactobacillus strains listed above was assessed for the general population. However, in previous assessments of probiotics published by VKM, concerns have been identified for specific groups. Therefore, the risk was assessed for the age group with immature gastro-intestinal microbiota (age group 0-36 months), population with mature gastro-intestinal microbiota (>3 years) and vulnerable groups with mature gastro-intestinal tract. VKM has also assessed the risk of L. acidophilus W37, L. acidophilus DDS-1, L. acidophilus La-5 and L. acidophilus La-14 in food supplements and other foods independent of the dose and have assessed exposure in general terms. VKM concludes that it is unlikely that L. acidophilus W37, L. acidophilus DDS-1, L. acidophilus La-5 and L. acidophilus La-14 would cause adverse health effects in the general healthy population with mature gastro-intestinal tract. However, no data on long-term adverse effects on infants and young children were identified. As evidence is accruing that the early microbial composition of the neonatal gut is important for the development of the gut microbiota and the immune system of the growing child, it is not possible to exclude that a daily supply of a single particular bacterial strain over a prolonged period of time to an immature gastro-intestinal tract may have long-term, although still unknown, adverse effects on that development.

In March 2016, the EU Commission presented a proposal for new regulations on fertilising material. The regulation includes product rules for a wide range of organic and inorganic products. Microbial biostimulants is one of the categories of products that are included. Biostimulants, in the draft EU regulation, are defined as fertilising materials that affect nutrient processes independently of the product's own nutrient content and with the purpose of improving nutrient utilisation, tolerance for abiotic stress or quality of the crop. Positive list in which species of these bacterial genera are listed: Azotobacter spp, Rhizobium spp., Azospirillum spp and Mycorrhizal fungi are a part of the regulation. Since the import and use of these organisms are the responsibility of both the Norwegian Food Safety Authority and the Norwegian Environment Agency, they asked VKM to submit a joint report on effects on health (humans, plants and animals), biodiversity and dispersal, quality of agricultural land and on soil environment. Conclusions: Health risks: Based upon our literature review, we have found no indication of any specific diseases in plants, animals or humans induced by the discussed microorganisms. A few reported cases of human disease are caused through wound infections or injections in immunocompromised patients. These represent a situation where any microorganism may induce infections and is not specific for the agents discussed in this report. In summary, the risk of any disease caused by the discussed microorganisms is considered negligible. Environmental risks: In soil the biodiversity, competition, adaptation and functional redundancy of microorganisms are extremely high. This means that introduced microorganisms have a very small chance for establishing, and even less so for affecting biodiversity and soil functioning. Introduction of nitrogen fixing species or fungi that can transport P to plants (mycorrhiza) will lead to an increase in the primary production. However, even a large increased activity for these processes will not outcompete naturally occurring symbiotic N-fixation or growth of inherently non-mycorrhizal plant species. Thus, the risks associated with introduced non-pathogenic microorganisms are very low.

The Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen for mattrygghet, VKM) has, at the request of the Norwegian Food Safety Authority (Mattilsynet; NFSA), assessed the risk of "other substances" in food supplements sold in Norway. These risk assessments will provide NFSA with the scientific basis for regulation of the addition of “other substances” to food supplements and other foods. "Other substances" are described in the food supplement directive 2002/46/EC as substances other than vitamins or minerals that have a nutritional and/or physiological effect. It is added mainly to food supplements, but also to other foods. VKM has not in this series of risk assessments of "other substances" evaluated any claimed beneficial effects from these substances, only possible adverse effects. The present report is a risk assessment of Bifidobacterium lactis Bi-07, Bifidobacterium bifidum W23, Bifidobacterium longum Rosell-175, Bifidobacterium breve Rosell-70, and Bifidobacterium animalis sub. lactis Bb12 based on previous risk assessments and also publications retrieved from literature search. The risk of the Bifidobacterium strains listed above was assessed for the general population. However, in previous assessments of probiotics published by VKM, concerns have been identified for specific groups. Therefore, the risk was assessed for the age group with immature gastro-intestinal microbiota (age group 0-36 months), population with mature gastro-intestinal microbiota (>3 years) and vulnerable groups with mature gastro-intestinal tract. VKM has also assessed the risk of Bifidobacterium spp. in food supplements and other foods independent of the dose and have assessed exposure in general terms. VKM concludes that it is unlikely that B. lactis Bi-07, B. bifidum W23, B. longum Rosell-175, B. breve Rosell-70, and B. animalis sub. lactis Bb12 would cause adverse health effects in the general healthy population with mature gastro-intestinal tract. However, no data on long-term adverse effects on infants and young children were identified. As evidence is accruing that the early microbial composition of the neonatal gut is important for the development of the gut microbiota and the immune system of the growing child, it is not possible to exclude that a daily supply of a single particular bacterial strain over a prolonged period of time to an immature gastro-intestinal tract may have long-term, although still unknown, adverse effects on that development.

The Norwegian Food Safety Authority (Mattilsynet, NFSA) and the Norwegian Environment Agency (Miljødirektoratet, NEA) requested the Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen for mattrygghet, VKM) for a scientific opinion on Chronic wasting disease (CWD) in cervids. The project was divided into two phases, and VKM published the scientific opinion from phase I “CWD in Norway” in June 2016. The current report is the result of phase II. VKM was asked to provide updated information on food safety, aspects important for transmission of CWD within and between populations and species, and the potential origin of the disease in Norway. Moreover, VKM was asked to highlight important risk factors with regard to disease transmission, and how these risk factors might affect choice of management strategy. Finally, VKM was asked to highlight relevant management strategies from North America or elsewhere. VKM appointed a working group consisting of one member of the Panel on Microbial Ecology, one member of the Panel on Biological Hazards, and five external experts, as well as VKM`s secretariat to answer the questions from NEA and NFSA. One member of the Panel on Alien Organisms and Trade in Endangered Species (CITES), one member of the Panel on Animal Health and Welfare, as well as one member of the Panel on Biological Hazards commented on the draft report. The Panel on Biological Hazards assessed and approved the final report. Background: Chronic wasting disease (CWD) is a prion disease that affects deer, moose, reindeer, and related species (cervids). Prion diseases are chronic neurodegenerative diseases that occur naturally in humans and ruminants, and are invariably fatal. Some prion diseases, such as classical scrapie in sheep and goats and chronic wasting disease (CWD) in cervids, are contagious, spreading directly between animals or via environmental contamination. In contrast, prion diseases known to affect humans are not known to be contagious. Prions are extraordinary agents consisting of misfolded protein aggregates that are remarkably stable and can remain infectious for years in the environment. Prion proteins are present in most animals, but the misfolding makes them very hard to break down. Consequently, misfolded prion proteins accumulate in the brain and eventually in other tissues, causing damage to those tissues. Until recently, CWD was only known from North America and South Korea. During a routine marking event in April 2016, a female reindeer (Rangifer tarandus) of the Nordfjella wild reindeer herd in Norway exhibited unusual behaviour, and died shortly afterwards. This unusual death was routinely investigated, and the animal was diagnosed with CWD. This was the first time CWD had been diagnosed outside North America and South Korea and the first case of natural CWD in reindeer. In addition, two moose (Alces alces) in Selbu, Norway were diagnosed with CWD in May 2016. Selbu is located approximately 300 km northeast of the Nordfjella mountain range. Currently there is considerable uncertainty regarding the nature of the CWD diagnosed in the two moose. Some of the characteristics of these cases indicate consistency with atypical prion disease, as described in domestic animals, but a final conclusion depends on the results from ongoing investigations. Following the diagnosis in reindeer, Norwegian authorities initiated a screening programme in which hunters were requested to collect tissue and the heads of dead cervids during the 2016 hunting season. Animals that had died from causes other than hunting were also tested for CWD. Since March 2016, 4629 samples of moose, 2550 samples of red deer, 627 samples of roe deer, 860 samples of reindeer, 2494 semi-domesticated reindeer, 163 farmed deer and 104 samples of unidentified species were tested for CWD. Two additional cases of CWD were diagnosed in wild reindeer in the Nordfjella population. Together with a clinical, pathological and epidemiological picture consistent with contagious CWD, as described from North America, this indicated that there is an ongoing outbreak of CWD in the wild reindeer population of the northern part of Nordfjella wild reindeer range. Results: An increase in the distribution and prevalence of CWD will increase exposure of other species, including domestic animals and humans, to this infectious agent. There is currently no evidence indicating transmission of CWD to domestic animals or humans, either by direct contact with cervids, cervid meat, or other products from cervids, or through the environment. VKM continues to support the conclusion from phase I concerning food safety of meat from cervids, that the zoonotic risk of CWD (transmission to humans) is very low. Preliminary results from characterisation of the moose cases and the agent involved indicate that important features deviate significantly from those found in the reindeer and in North American cervids, raising uncertainty with regards to the zoonotic potential. Therefore, based on the data currently available, VKM is not able to reach an evidence-based conclusion regarding the food safety of meat from moose and other cervids infected with this potentially new variant of CWD. Whereas direct transmission (animal-to-animal) seems most important in the early phases of a CWD epizootic, the role of indirect transmission (from the environment) increases as the prevalence increases. Once contagious CWD is established, it is very likely that the disease will increase in prevalence within the affected population and spread to contact populations. The rate of increase in prevalence, the resulting impact in a given population, and the efficacy of spread will depend on a range of environmental factors, and the characteristics of the species and population in question. For example, in affected populations of a gregarious species like reindeer, CWD is likely to lead to population decline in the long-term. Experiences from North America indicate that prions aggregate in the environment, making eradication of the disease extremely difficult once it has been allowed to develop and become endemic. It is therefore important that efficient measures are implemented at the VKM Report 2017:9 9 earliest opportunity in order to have a realistic chance of eradicating local occurrence of CWD and preventing further spread. Contagious CWD found in a confinable population, such as many wild reindeer herds, should be managed by eradication of the host population, fallowing of the area (> 5 years), and restocking from a healthy population. The report explains that culling of the Nordfjella reindeer herd is a necessary, immediate response to the current situation. However, as part of an adaptive management strategy, this measure should be under active review and may be revised in the event that new cases of CWD are discovered. In contrast, in continuous populations, such as most red deer, moose, and roe deer populations, spatially targeted culling within a defined containment zone should be used to control a CWD outbreak. Confinement of CWD-infected populations should be increased where possible and contact with other populations of cervids restricted, for example by fencing, herding, enhancing natural or man-made obstacles, or decreasing the densities of the relevant cervid populations. Potential “hotspots” for disease transmission (supplementary salt-licks, supplementary feeding sites etc.) should be eliminated in areas with CWD as well as the surrounding areas, and should further be considered for other parts of the country. Precautionary measures should be implemented to prevent anthropogenic spread of the disease. Finally, increasing the national surveillance of CWD in cervids is essential to ensure that there is a comprehensive basis for future evidence-based management. This is required to ensure that cases and spread of disease are identified as soon as possible, as late discovery will limit the chances for successful eradication of CWD in Norway.

The Norwegian Scientific Committee for Food Safety (Vitenskapskomiteen for mattrygghet, VKM) has, at the request of the Norwegian Food Safety Authority (Mattilsynet; NFSA), assessed the risk of "other substances" in food supplements sold in Norway. These risk assessments will provide NFSA with the scientific basis while regulating the addition of “other substances” to food supplements and other foods. "Other substances" are described in the food supplement directive 2002/46/EC as substances other than vitamins or minerals that have a nutritional and/or physiological effect. It is added mainly to food supplements, but also to other foods. VKM has not in this series of risk assessments of "other substances" evaluated any claimed beneficial effects from these substances, only possible adverse effects. Grey Literature Grahek-Ogden et al.; EJNFS, 8(4): 326-327, 2018; Article no.EJNFS.2018.058 327 The present report is a risk assessment of Lactobacillus salivarius W24, and it is based on previous risk assessments and articles retrieved from a literature search. The risk of L. salivarius W24 was assessed for the general population. However, in previous assessments of “probiotics” published by VKM, concerns have been identified for specific groups. Therefore, the risk was assessed for the age group with immature gastro-intestinal microbiota (age group 0-36 months), population with mature gastro-intestinal microbiota (>3 years) and vulnerable groups independent of age. VKM has also assessed the risk of L. salivarius W24 in food supplements independent of the dose and have assessed exposure in general terms. Other sources of L. salivarius W24, such as foods, have not been included in the present risk assessment. VKM concludes that it is unlikely that L. salivarius W24 causes adverse health effects in the general healthy population with mature gastro-intestinal tract. However, no data on long-term adverse effects on infants and young children were identified. As evidence is accruing that the early microbial composition of the neonatal gut is important for the development of the gut microbiota and the immune system of the growing child, it is not possible to exclude that a daily supply of a single particular bacterial strain over a prolonged period of time to an immature gastro-intestinal tract may have long-term, although still unknown, adverse effects on that development.