TY - THES A1 - Usmani, Shirin T1 - Wood treated with nano metal fluorides - relations between composition, size, and durability N2 - In this study, nanoscopic particles of magnesium Fluoride (MgF2) and calcium fluoride (CaF2) also known as nano metal fluorides (NMFs), were evaluated for their potential to improve wood durability. Even though these fluorides are sparingly soluble, their synthesis in the form of nano-sized particles turns them into promising candidates for wood preservation. Their distinct property of low-water solubility is proposed to maintain long-lasting protection of treated wood by reducing the leaching of fluoride. Analytical methods were used to characterize the synthesized NMFs and their distribution in treated wood specimens. Transmission electron microscopy images showed that these fluoride particles are smaller than 10 nm. In nano metal fluoride (NMF) treated specimens, aggregates of these particles are uniformly distributed in the wood matrix as confirmed with scanning electron microscopy images and their corresponding energy-dispersive X-ray spectroscopy maps. The fluoride aggregates form a protective layer around the tracheid walls and block the bordered pits, thus reducing the possible flow path for water absorption into wood. This is reflected in the reduced swelling and increased hydrophobicity of wood treated with NMFs. The biocidal efficacy of NMFs was tested against brown-rot fungi (Coniophora puteanaand Rhodonia placenta), white-rot fungus (Trametes versicolor), and termites (Coptotermes formosanus). The fungal and termite tests were performed in accordance with the EN 113 (1996) and EN 117 (2012) standards, respectively. Prior to fungal tests, the NMF treated wood specimens were leached according to the EN 84 (1997)standard. Compared to untreated specimens, the NMF treated wood specimens have a higher resistance to decay caused by brown-rot fungi, white-rot fungus, and termites. Although all NMF treatments in wood reduce the mass loss caused by fungal decay, only the combined treatment of MgF2 and CaF2 has efficacy against both brown-rot fungi and white-rot fungus. Similarly, wood treated with the combined NMF formulation is the least susceptible to attack by C. formosanus.It is proposed that combining MgF2 and CaF2changes their overall solubility to promote the release of fluoride ions at the optimal concentration needed for biocidal efficacy against fungi and termites. In this thesis, it was proven that even after leaching, sufficient fluoride was present to protect NMF treated wood from fungal decay. This shows that NMFs are robust enough for above ground contact outdoor applications of wood, where permanent wetness cannot be avoided according to Use Class 3.2, as per the EN 335 (2013) standard. Also, they pose a low risk to human health and the environment because they are sparingly soluble. Since NMFs significantly reduce the decay of wood, the CO2 fixed in it will be retained for longer than in unpreserved wood. Overall, the novel results of this study show the potential of NMFs to increase the service life of building materials made from non-durable wood. KW - Termites KW - Nano metal fluorides KW - Solubility KW - Wood protection KW - Fungi PY - 2021 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-525108 DO - https://doi.org/10.18452/22553 SP - i EP - 118 PB - Humboldt-Universität zu Berlin CY - Berlin AN - OPUS4-52510 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - European Food Safety Authority (EFSA), A1 - European Centre for Disease Prevention and Control (ECDC), A1 - European Chemicals Agency (ECHA), A1 - European Environment Agency (EEA), A1 - European Medicines Agency (EMA), A1 - European Commission's Joint Research Centre (JRC), T1 - Scientific report - Impact of the use of azole fungicides, other than as human medicines, on the development of azole‐resistant Aspergillus spp. N2 - The use of azoles in the European Union and European Economic Area (EU/EEA) other than as human medicines has raised concerns about emergence and spread of azole‐resistant Aspergillus species. EU agencies, with the support of JRC, reviewed the evidence and provided conclusions and recommendations on this topic. Although incomplete, data from 2010 to 2021 showed that around 120,000 tonnes of azoles were sold in EU/EEA for uses other than as human medicines. The majority are used as plant protection products (119,000 tonnes), with a stable temporal trend. Evidence supported a link between environmental azole exposure and cross‐resistance selection to medical azoles in Aspergillus species (primarily shown for A. fumigatus). Prevalence of azole‐resistant A. fumigatus in human A. fumigatus infections ranges from 0.7% to 63.6% among different disease presentations and geographic regions; mortality rates range from 36% to 100% for invasive aspergillosis (IA). It was concluded that azole usage outside the human domain is likely or very likely to contribute to selection of azole‐resistant A. fumigatus isolates that could cause severe disease like IA. Environmental hotspots for resistance selection were identified, including stockpiling of agricultural waste and their possible use as soil amendment/fertiliser for certain agricultural crops (for plant protection products) and freshly cut wood (for biocides). Recommendations were formulated on measures to prevent and control selection of azole resistance in A. fumigatus, including implementation of good agricultural/horticultural practices, proper agricultural and wood waste storage and management, and on approval of new azole fungicides or renewal of existing fungicides. Recommendations on topics to be covered by studies provided when submitting applications for the approval of azole fungicides were listed. For the evaluation of such studies within the approval procedure, a preliminary framework for risk assessment was developed and should be further refined. Data gaps and uncertainties were identified, alongside with respective recommendations to address them. KW - Antimicrobial surfaces KW - Biocides KW - Antimicrobial resistance KW - Azoles KW - Fungi KW - Wood preservatives PY - 2025 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-652175 DO - https://doi.org/10.2903/j.efsa.2025.9200 SN - 1831-4732 VL - 23 IS - 1 SP - 1 EP - 35 PB - Wiley CY - Hoboken, NJ AN - OPUS4-65217 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - RPRT A1 - European Food Safety Authority (EFSA), A1 - European Centre for Disease Prevention and Control (ECDC), A1 - European Chemicals Agency (ECHA), A1 - European Environment Agency (EEA), A1 - European Medicines Agency (EMA), A1 - European Commission's Joint Research Centre (JRC), T1 - Annex to: Scientific report 'Impact of the use of azole fungicides, other than as human medicines, on the development of azole-resistant Aspergillus spp.' doi:10.2903/j.efsa.2025.9200 - Annex E - Detailed answer to Term of Reference 5 'Environmental hotspots' and Term of Reference 6 'Prevention and control options' N2 - The widespread use of azole compounds in various sectors has led to the emergence of azole-resistant Aspergillus fumigatus (ARAf), which poses a significant challenge for treating fungal infections, especially in immunocompromised patients. Certain environmental conditions and practices, particularly in agricultural settings and the use of azoles as biocides, have been identified as hotspots for the selection and dispersal of azole-resistant strains of Aspergillus spp. Factors contributing to the selection of resistance include the use of azoles in crop protection, wood preservation and, to a much lesser extent, veterinary medicine. For plant protection products (PPPs), a number of scenarios (green waste of indoor-grown vegetables, uses with the production of wet pomace used as fertiliser, maize or sugar beet silage, and field heaps including flower bulbs) are deemed high risk for hotspot development. Based on EU authorised use patterns, these scenarios are characterised by the hazard characteristics of the azole fungicides in terms of activity against the wild-type Aspergillus spp. compared to resistant strains, substrate characteristics and residue levels, and environmental conditions that promote the growth of the fungus. For biocidal azole applications, products (biocidal product [BP]) for temporary preservation of freshly cut wood have been identified to have the potential for hotspot formation because freshly cut wood allows the growth of Aspergillus spp., and azole concentrations in treated wood are above the predicted no effect concentration (PNEC) for resistance selection (PNECres) and below the minimum inhibitory concentration (MIC) of ARAf for most analysed products on the EU market. Following identification of environmental hotspots, the report recommends measures to prevent the selection of azole-resistant strains in the environment, including controlled storage of organic waste, proper waste management, and responsible use and disposal of azole-treated products. Azole use in veterinary medicinal products (VMPs) represents a very small percentage of total azole use and is unlikely to be a significant source of selection of resistance in the environment. As such, the focus for mitigating resistance should be on other uses of azoles. The report stresses the importance of ongoing surveillance to monitor the presence of ARAf in the environment and to inform risk assessments and management strategies. As industrial chemicals, the azole substances are mostly used as intermediates (precursors) to manufacture yet a different substance, are formulated into a mixture or are reported to be manufactured as active substances in PPP, BP or VMP (therefore already covered above). There are only a few industrial azole substances with widespread use, and as for the moment, there is no evidence from the literature that industrial azoles would be a source of a possible hotspot; thus, the industrial chemicals were not further investigated. There are several areas where further research is needed, including understanding the environmental conditions that support the growth of Aspergillus spp. in different agricultural matrices or on wood, assessing human exposure to resistant strains, regional waste practices and the impact of active substance combinations for azole resistance selection. There is also a need for more comprehensive data on the use and quantities of azole-containing products. Furthermore, industrial substances with widespread use and having antifungal effects, e.g. an antidandruff substance in cosmetics, could be further investigated. Measures were identified that could be implemented with respect to the use of azole fungicides in PPPs as well as in BPs and with respect to the storage, processing and disposal of crop (waste) materials containing azole residues to prevent or minimise the selection of environmental resistance or to minimise the spread of resistant Aspergillus spp. to patients. Any measures that slow down or prevent growth in the presence of azoles, sporulation and dispersal of Aspergillus spp. should be encouraged. A coordinated effort among various stakeholders, including farmers, manufacturers, industrial users, waste managers, regulatory bodies and scientists, is essential to effectively address the challenge of azole resistance in A. fumigatus. KW - Antimicrobial surfaces KW - Biocides KW - Antimicrobial resistance KW - Azoles KW - Fungi KW - Wood preservatives PY - 2025 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-652187 UR - https://doi.org/10.5281/zenodo.14223436 DO - https://doi.org/10.5281/zenodo.14223435 SP - 1 EP - 76 PB - Zenodo CY - Geneva AN - OPUS4-65218 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER -