A systematic review of measures of the personal recovery orientation of mental health services and staff.

PURPOSE: This review aimed to update and extend the Williams and colleagues 2012 systematic review of measures of recovery-orientation of mental health services by examining whether any of the specific knowledge gaps identified in this original review had subsequently been addressed. METHODS: A systematic review using CINAHL, ASSIA, Embase, PsycINFO, Medline and other sources, searched from 2012 until 2021. The conceptualisation of recovery and recovery-orientation of services was explored. Psychometric properties of measures were evaluated using quality criteria and according to ease of use. RESULTS: Fourteen measures assessing aspects of the recovery orientation of services and staff were identified, of which ten met the eligibility. Psychometric properties were evaluated, and conceptualisations of recovery and recovery-orientation of services investigated. CONCLUSION: After over a decade of research in the field of recovery outcome measurement, there remains a lack of a single gold-standard measure of recovery-orientation of mental health services. There is a need for researchers to develop a new gold standard measure of recovery-orientation of services that is psychometrically valid and reliable, demonstrates sensitivity to change and is easy to use. It needs to show a good fit to an underpinning conceptual model/ framework of both personal recovery and recovery-oriented services and/or systems, with different versions for stakeholders at each level of an organisation or system.

Role of the fungal mycelium in the retention of radiocaesium in forest soils.

The aim of this work was to study possible binding of 137Cs to various organic components in the soil and fungi, by using various sequential extraction procedures. The retention and binding of 137Cs has been studied in two horizons Of/Oh and Ah/B of a Ukrainian forest soil. The exchangeable fractions 137Cs from soil (sum of H2O and 1 M NH4OAc fraction) were found to be 12% in the organic-rich layer (range 11-14%) and 23% in the organic-poor (range 20-29%). The hydrolysis with 10% H2SO4 resulted in an additional release of 30% of 137Cs from the organic-rich soil (range 30-35%) and 38% from the organic-poor soil horizon (range 27-53%). Extraction with 30% H2O2 released 11 and 15% of the 137Cs activity from organic-rich and organic-poor soil horizons. The corresponding values for treatment with 98.8% NaOCl were about 27% in both types of soil. About 11% of the total 137Cs activity was found in the humic acid fraction, about 5% in the fulvic fraction and 46% in the residue fraction. Relatively high level of 137Cs activity in soil (ca. 50%) was thus still left unsolved in the residue fraction. About 29% of 137Cs activity concentration in fungal mycelia was found as water soluble with a range of 11 to 41%. Additionally 24% of the 137Cs activity from mycelia was released by 1 M ammonium acetate extraction. Together, water and 1 M ammonium acetate extraction released about 53% of the total 137Cs activity in the mycelia. In fruit bodies of mycorrhizal fungi, 68% of the total 137Cs inventory was found to be water soluble at room temperature and 93% at 80 degrees C.

137Cs in the fungal compartment of Swedish forest soils.

The (137)Cs activities in soil profiles and in the mycelia of four ectomycorrhizal fungi were studied in a Swedish forest in an attempt to understand the mechanisms governing the transfer and retention of (137)Cs in forest soil. The biomass of four species of fungi was determined and estimated to be 16 g m(-2) in a peat soil and 47-189 g m(-2) in non-peat soil to the depth of 10 cm. The vertical distribution was rather homogeneous for two species (Tylospora spp. and Piloderma fallax) and very superficial for Hydnellum peckii. Most of the (137)Cs activity in mycelium of non-peat soils was found in the upper 5 cm. Transfer factors were quite high even for those species producing resupinate sporocarps. In the peat soil only approximately 0.3% of the total (137)Cs inventory in soil was found in the fungal mycelium. The corresponding values for non-peat soil were 1.3, 1.8 and 1.9%.

Accumulation of 137Cs by fungal mycelium in forest ecosystems of Ukraine.

During 1996-1998, 16 fruit bodies of different species and 204 soil samples down to 10 cm in the close vicinity of the fruit body sites were collected in a coniferous forest in the Ovruch region of Ukraine. The soil samples were sliced into 1 or 2 cm layers and the fungal mycelium was prepared from each of the layers. The 137Cs activity concentration was determined in both soil and mycelium. The mean weight of fungal mycelium was 13.8 mg g(-1) of soil in the upper 4 cm and 7.3 mg g(-1) when measured for the upper 10 cm. At the sites of Paxillus involutus and Sarcodon imbricatus, the mycelium was rather homogeneously distributed in the upper 10 cm and at sites of Xerocomus subtomentosus and Cantharellus cibarius, the mycelium was distributed mostly in the upper layers. The highest 137Cs activity concentrations were found in the upper layers of the soil profile. The 137Cs activity concentrations were usually higher in the fruit bodies compared with the mycelium, with ratios ranging from 0.1 to 66 and a mean of 9.9. The percentage of the total inventory of 137Cs in the soil found in the fungal mycelium ranged from 0.1 to 50%, with a mean value of 15%.

High-throughput screening of small molecules for bioactivity and target identification in Caenorhabditis elegans.

This protocol describes a procedure for screening small molecules for bioactivity and a genetic approach to target identification using the nematode Caenorhabditis elegans as a model system. Libraries of small molecules are screened in 24-well plates that contain a solid agar substrate. On top of the agar mixture, one small-molecule species is deposited into each well, along with worm food (E. coli), and two third-stage or fourth-stage larval worms using a COPAS (Complex Object Parametric Analyzer and Sorter) Biosort. Three to five days later the plates are screened for phenotype. Images of the wells are acquired and archived using a HiDI 2100 automated imaging system (Elegenics). Up to 2,400 chemicals can be screened per week. To identify the predicted protein target of a bioactive molecule, wild-type worms are mutagenized using ethylmethanesulfonate (EMS). Progeny are screened for individuals resistant to the molecules effects. The candidate mutant target that confers resistance is then identified. Target identification might take months.