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- Beding-Barnekow, B., et al.
(författare)
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Systemic and intraocular uptake of spantide, a tachykinin antagonist, following topical application to the rabbit eye.
- 1990
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Ingår i: Experimental Eye Research. - 0014-4835. ; 50:1, s. 21-26
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Tidskriftsartikel (refereegranskat)abstract
- Previous observations have indicated that topical application to the rabbit eye of tachykinin antagonists, including spantide, effectively prevents the miosis and the disruption of the blood-aqueous barrier consequent to ocular injury. The present study shows that spantide is taken up into the rabbit eye following topical application. This was established by determination of spantide in the aqueous humor by radioimmunoassay. The concentrations reached in the aqueous humor were those that could be expected to block tachykinin receptors. The elimination of spantide from the aqueous humor was found to be slow. From HPLC analysis it seemed that spantide in the aqueous humor is degraded to smaller products, predominantly spantide 5–11. Some of the topically applied peptide appeared in the general circulation. Here the rate of elimination was rapid by comparison. Very small amounts of spantide appeared in the cerebrospinal fluid after intravenous injection.
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| 2. |
- Björk, Mats, 1960-, et al.
(författare)
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Procedures for Protoplast Isolation from Red Seaweeds.Demonstration on Gracilaria sordida and Gracilaria tenuistipitata.
- 1991
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Ingår i: Recent Advances in Seaweed Cellular Biotechnology, Physiology and Intensive Cultivation. ; , s. 283-286
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Konferensbidrag (övrigt vetenskapligt/konstnärligt)abstract
- This procedure consists of four main steps. The precultivation of the plant material, the pretreatment of thetissue, the incubation of the tissue in an enzyme solution, and finally the purification of the protoplasts. Allsteps have influence on the final yield and viability of the protoplasts. To prevent contamination all work shouldbe done in a laminar flow hood. Sterilize all tools, andfilter all solutions through a 0,22 jJ.m sterile filter beforeuse. Use standard axenic procedures.By this method a protoplast yield of 1x1a6 to 1x107 per gram fresh weight has been obtained. These protoplastswere viable and divided up to three times while in culture. (Bjork et al. 1990)
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| 3. |
- Ion, John, et al.
(författare)
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Laser surface modification of a 13.5% Cr, 0.6% C steel
- 1991
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Ingår i: Journal of Materials Science. - 0022-2461 .- 1573-4803. ; 26:1, s. 43-48
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Tidskriftsartikel (refereegranskat)abstract
- A 13.5% Cr, 0.6% C steel, with an initial microstructure of chromium carbides in a ferrite matrix, was heat-treated by scanning a high-power laser beam over the surface. The aim was to compare the physical and chemical properties produced by this type of selective surface treatment with those resulting from a conventional furnace desensitization and quench-hardening heat treatment. Surface heating homogenized the carbon originally bound in the carbides sufficiently to produce martensite, giving hardening to levels comparable with a conventional heat treatment. Chromium-rich zones, carbides and retained austenite were also detected in the heated microstructure. Surface melting produced complete homogenization of both carbon and chromium, which resulted in the retention of large amounts of austenite in the microstructure on cooling to room temperature. Subsequent refrigeration at - 196 °C transformed some of the austenite to martensite. Pitting corrosion and local reductions in hardness were observed adjacent to treated areas under certain conditions, due to precipitation of secondary carbides and elevated tempering, respectively.
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| 5. |
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| 6. |
- Vought, Lena B. M., et al.
(författare)
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Nutrient retention in riparian ecotones
- 1994
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Ingår i: Ambio. - 0044-7447 .- 1654-7209. ; 23:6, s. 342-348
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Tidskriftsartikel (refereegranskat)abstract
- Nutrient retention mechanisms in riparian buffer strips are reviewed with emphasis on surface runoff and subsurface flows, the main pathways of exchanges between the stream and its surroundings. Unique physical and biogeochemical properties prevailing in these riparian ecotones dictate the flux of water, nutrients and other exogenous substances between the upland areas and the stream. Removal of nutrients from surface inflows is induced by deposition of sediment bound nutrients and exchange of dissolved nutrients with the soil/litter surface. Removal of nitrogen in subsurface flows can partly be explained by vegetation uptake, but the main mechanism for removal is usually denitrification. In channelized streams, the subsurface inflows have, in most cases, been altered to discharges via drainage tiles, with the exchange flows (water leaving and re-entering the open-channel via the stream bed and banks) being greatly decreased. Consequently, to improve nitrogen removal in these systems, these flows have to be intercepted or reestablished either through restoration of the old stream valley or through managed structures in the buffer strips.
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| 7. |
- Vought, Lena B. M., et al.
(författare)
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Nutrient retention in riparian ecotones
- 1994
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Ingår i: Ambio. - : Allen Press Inc.. - 0044-7447 .- 1654-7209. ; 23:6, s. 342-348
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Tidskriftsartikel (refereegranskat)abstract
- Nutrient retention mechanisms in riparian buffer strips are reviewed with emphasis on surface runoff and subsurface flows, the main pathways of exchanges between the stream and its surroundings. Unique physical and biogeochemical properties prevailing in these riparian ecotones dictate the flux of water, nutrients and other exogenous substances between the upland areas and the stream. Removal of nutrients from surface inflows is induced by deposition of sediment bound nutrients and exchange of dissolved nutrients with the soil/litter surface. Removal of nitrogen in subsurface flows can partly be explained by vegetation uptake, but the main mechanism for removal is usually denitrification. In channelized streams, the subsurface inflows have, in most cases, been altered to discharges via drainage tiles, with the exchange flows (water leaving and re-entering the open-channel via the stream bed and banks) being greatly decreased. Consequently, to improve nitrogen removal in these systems, these flows have to be intercepted or reestablished either through restoration of the old stream valley or through managed structures in the buffer strips.
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