Analysis of some beam-foil molecular-effect data

1988 ◽  
Vol 21 (10) ◽  
pp. L255-L259 ◽  
Author(s):  
E Veje
1988 ◽  
Vol 102 ◽  
pp. 339-342
Author(s):  
J.M. Laming ◽  
J.D. Silver ◽  
R. Barnsley ◽  
J. Dunn ◽  
K.D. Evans ◽  
...  

AbstractNew observations of x-ray spectra from foil-excited heavy ion beams are reported. By observing the target in a direction along the beam axis, an improvement in spectral resolution, δλ/λ, by about a factor of two is achieved, due to the reduced Doppler broadening in this geometry.


1979 ◽  
Vol 40 (C1) ◽  
pp. C1-190-C1-193 ◽  
Author(s):  
G. Sørensen
Keyword(s):  

1979 ◽  
Vol 40 (C1) ◽  
pp. C1-263-C1-265
Author(s):  
B. Andresen ◽  
S. B. Jensen ◽  
E. Veje ◽  
P. S. Ramanujam
Keyword(s):  

1979 ◽  
Vol 40 (C1) ◽  
pp. C1-10-C1-13 ◽  
Author(s):  
J. Bromander ◽  
S. Hultberg ◽  
B. Jelenkovik ◽  
L. Liljeby ◽  
S. Mannervik
Keyword(s):  

Analgesia ◽  
1998 ◽  
Vol 3 (5) ◽  
pp. 297-305 ◽  
Author(s):  
Jeffrey D. McCary ◽  
Ronald J. Tallarida

2021 ◽  
Vol 33 (1) ◽  
Author(s):  
Simon Schwarz ◽  
Daniela Gildemeister ◽  
Arne Hein ◽  
Patrick Schröder ◽  
Jean Bachmann

AbstractHuman pharmaceuticals are extensively studied and assessed before marketing approval. Since 2006, this also includes an assessment of environmental risks. In the European Union, this is based on the guideline on the environmental risk assessment of medicinal products for human use (EMEA/CHMP/SWP/4447/00 corr 2), which is currently under revision. For Germany, the German Environment Agency (UBA) is tasked with the evaluation of environmental risks of human pharmaceuticals. Applicants seeking approval of medicinal products need to submit fate and effect data, in case predicted environmental concentrations (PECs) exceed 10 ng/L in surface waters, or the substance is of specific concern through its mode of action or physico-chemical characteristics.Over the last decade, this regulatory work resulted in an internal agency database containing effect data on approximately 300 active pharmaceutical ingredients (APIs). A considerable part of this data is currently not publicly available due to property rights held by the respective applicants. The database was evaluated to draw conclusions on how the current assessment approach may be improved.The evaluation of aquatic effect data shows considerable variation in ecotoxic effect concentrations, but supports the current use of 10 ng/L as PEC action limit. For endocrine-active substances and antibiotics, a clear sensitivity profile was observed, which allows a more targeted assessment in the future. The conclusions drawn from terrestrial effect data are less clear, as the database itself is biased because information is only available for substances with high sorption. Further adaptations of the terrestrial assessment strategy, including action triggers, appear necessary. Fate data show a high persistence of many APIs: approximately 43% of all APIs are classified as very persistent; 12% of these show DT50 values in a range where abiotic or biotic degradation is not expected.Overall, the evaluation has shown that improvements of the current guideline are possible.


1980 ◽  
Vol 100 (2) ◽  
pp. K139-K143 ◽  
Author(s):  
M. Grünewald ◽  
P. Thomas ◽  
D. Würtz

1973 ◽  
Vol 110 ◽  
pp. 267-272 ◽  
Author(s):  
D.A. Church ◽  
C.H. Liu
Keyword(s):  
G Factor ◽  

1982 ◽  
Vol 202 (1-2) ◽  
pp. 269-272 ◽  
Author(s):  
C. Jupén ◽  
B. Denne ◽  
J.O. Ekberg ◽  
L. Engström ◽  
U. Litzén ◽  
...  

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