Koti-aapinen: lasten ensimmäistä opetusta warten

Kansikuvan ja kuvituksen signeeraus: A. F-ey = Alex Federley..

Jauhatusparametrien vaikutus jauhatustuotteen partikkelikokoon ja suodattuvuuteen

Tämän diplomityön tarkoituksena on tutkia ensin jauhatusparametrien vaikutus rikastushiekan hienousasteeseen eli miten partikkelikokojakaumaa kuvaavat partikkelikoot muuttuvat. Tämän jälkeen tutkitaan miten rikastushiekan hienousasteen muuttuminen vaikuttaa jauhettujen rikastushiekkalietenäytteiden suodattuvuuteen. Partikkelikokojakauman variaatioista yritetään löytää yhteys suodinkakun ominaisvastuksen ja huokoisuuden välillä. Jauhatus suoritettiin laboratoriomittakaavan helmimyllyllä märkäjauhatuksena. Jauhatusta varten tehtiin kolmitasoinen faktorikoesuunnitelma, jossa muuttujina ovat lasihelmien halkaisija, jauhatusaika ja sekoitinelimen pyörimisnopeus. Suodatus toteutettiin vakiopainesuodatuksena kolmella eri suodatuspaineella Nutsche-suodattimella. Työn tuloksista saatiin selville, että partikkelikokojakauman leveys korreloi suodinkakun ominaisvastuksen kanssa. Kun partikkelikokojakauma leveys muuttui kapeammaksi, saatiin kakun ominaisvastus pienemmäksi ja suodatukseen kulunut aika lyheni. Kapein partikkelikokojakauman leveys saatiin suurimmalla helmen halkaisijalla, pisimmällä jauhatusajalla sekä suurimmalla sekoitusnopeudella.

Kammottu ja kaivattu kosketus

Kirjallisuusarvostelu

[Kirja-arvostelu]

Kirjallisuusarvostelu

Sukupuolipopulismi ja maskulinistinen standpoint-empirismi

Pohjautuu Rovaniemen yliopistossa sukupuolentutkimuksen ja kulttuurintutkimuksen päivillä 2013 pidettyyn esitelmään Totuuksien politiikat.

Tehohoitopotilaan siirtotiedote hoitotyön päätöksenteon tukena - retrospektiivinen asiakirja-analyysi vuosilta 2001-2013

Tuija Lehtikunnas: Intensive care patient handover document in support of decision-making in nursing work - Retrospective document analysis for the period 2001–2013 University of Turku, Faculty of Medicine, Nursing Science Annales Universitatis Turkuensis Turku 2016 ABSTRACT The continuity of care and flow of information must be ensured when transferring the responsibility of care, whether this is done within an organisation or from one organisation to another. The purpose of this study was to describe and compare the nursing handover documents of long-term intensive care patients and changes to these documents during the years 2001–2013. Research data comprehended long-term intensive care patient handover documents (N = 250). Data was gathered from one university hospital intensive care unit and subjected to a content analysis of technical implementation, structure and content at five different time points. In addition to this, the nursing handover documents were analysed from a nursing decision-making standpoint. Sub-data (n = 5 x 50) from the years 2001, 2002, 2004, 2006 and 2013 was gathered. The first sub-data was manual, written on paper with a pen. The rest of the sub-data obtained was entered in a dedicated intensive care information system. The study developed an intensive care patient nursing handover document analysis framework, which was used to deductively analyse the research data. The results indicated that the transitioning to electronic records reinforced structure and identification improving the reusability of data was increased. Although intensive care nursing was recorded on nursing handover documents more comprehensively in more recent sub-data, it was done selectively with regard to overall patient care, e.g. there are no entries concerning the psychological support and counselling of patients or family members. Nursing handover documents do not contain a systematic description of the patient's communication and functional capacity at the moment of transfer. The patient's condition at the moment of transfer is not clearly indicated on the handover documents. Plans for follow-up treatment are not recorded at all. Nursing decision-making is difficult to find on the nursing handover documents used as research data. The study developed a handover document model for intensive care nursing that supports nursing decision-making and the continuity of care. Developmental recommendations focus on the management of co-operation within organisations for ensuring the continuity of care and enhancing each area of nursing in recording nursing handover documents by planning nursing for the patient, taking follow-up treatment resources into consideration. Keywords: Intensive care nursing, nursing decision-making, nursing records, information flow, nursing handover document, continuity of care

Equol: a comparison of the effects of the racemic compound with that of the purified S-enantiomer on the growth, invasion, and DNA integrity of breast and prostate cells in vitro

It has been postulated that the R- and S-equol enantiomers have different biological properties given their different binding affinities for the estrogen receptor. S-(-)equol is produced via the bacterial conversion of the soy isoflavone daidzein in the gut. We have compared the biological effects of purified S-equol to that of racemic (R and S) equol on breast and prostate cancer cells of varying receptor status in vitro. Both racemic and S-equol inhibited the growth of the breast cancer cell line MDA-MB-231 (> or = 10 microM) and the prostate cancer cell lines LNCaP (> or = 5 microM) and LAPC-4 (> or = 2.5 microM). The compounds also showed equipotent effects in inhibiting the invasion of MDA-MB-231 and PC-3 cancer cells through matrigel. S-equol (1, 10, 30 microM) was unable to prevent DNA damage in MCF-7 or MCF-10A breast cells following exposure to 2-hydroxy-4-nonenal, menadione, or benzo(a)pyrene-7,8-dihydrodiol-9,10-epoxide. In contrast, racemic equol (10, 30 microM) prevented DNA damage in MCF-10A cells following exposure to 2-hydroxy-4-nonenal or menadione. These findings suggest that racemic equol has strong antigenotoxic activity in contrast to the purified S-equol enantiomer implicating the R-, rather than the S-enantiomer as being responsible for the antioxidant effects of equol, a finding that may have implications for the in vivo chemoprotective properties of equol.

Genusperspektiv i historieläromedel - finns det? : En jämförande analys av fem läroböcker i historia för gymnasiet utgivna under åren 1995-2004

Syftet med denna uppsats har varit att studera om det finns något genusperspektiv i valda nedslag i gymnasieläroböcker i ämnet historia. De teoretiska utgångspunkterna och definitionerna har hämtats i Micael Nilssons rapport Historia ur ett genusperspektiv – En granskning av genusaspekterna i ämnet historia vid Linköpings universitet. Materialet har kategoriserats i tre olika perspektiv; kvinnohi-storiskt perspektiv, jämställdhetsperspektiv och genusperspektiv. Litteraturen har därefter place-rats i den så kallade genustrappan som i Nilsson version består av fem olika steg; genusmedveten, jämställdhetsmedveten, könsmedveten, könsomedveten eller könsmakts-förstärkande. Det un-dersökta materialet har bestått av fem läroböcker som behandlar A-kursen i historia. Läroböcker-na är utgivna på fem olika förlag, ingen av dem har en ensam författare och tre av böckerna har en kvinnlig medförfattare. Undersökningen är baserad på både den kvalitativa och den kvantitati-va metoden. Den kvantitativa delen av undersökning har gått ut på att räkna antal kvinnonamn i böckernas register och antal illustrationer som innehåller kvinnor. I den kvalitativa delen av un-dersökningen har material om kvinnor samt kvinnors situation i kapitlen om antikens Grekland, nordisk medeltid och industrialismen analyserats. Undersökningen visar att läroböckerna repre-senterar en historieskrivning som i stora drag lämnar kvinnorna utanför. Ingen av böckerna når upp till kategorien genusmedveten, de två böcker som placerar sig högst når kategorien jäm-ställdhetsmedveten. Resultatet visar att läroböckerna inte lever upp till styrdokumentens krav på en jämställd undervisning.

Bioremediation of PAHs - Limitations and soultions

Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.