Biological effects and physical properties in the marine environment of aliphatic chlorinated by-products from vinyl chloride production

1972 ◽  
Vol 6 (10) ◽  
pp. 1181-1191 ◽  
Author(s):  
Arne Jernelöv ◽  
Rutger Rosenberg ◽  
Sören Jensen
Author(s):  
Julián Blasco ◽  
Miriam Hampel ◽  
Olivia Campana ◽  
Ignacio Moreno-Garrido

2021 ◽  
Vol 174 ◽  
pp. 107247
Author(s):  
Ε. Pagona ◽  
K. Kalaitzidou ◽  
A. Zouboulis ◽  
M. Mitrakas

1976 ◽  
Vol 17 ◽  
pp. 211-216 ◽  
Author(s):  
M Winell ◽  
B Holmberg ◽  
T Kronevi

2018 ◽  
Vol 72 (7) ◽  
pp. 564-571 ◽  
Author(s):  
Pooja Jain ◽  
Paolo Vineis ◽  
Benoît Liquet ◽  
Jelle Vlaanderen ◽  
Barbara Bodinier ◽  
...  

Epidemiological studies provide evidence that environmental exposures may affect health through complex mixtures. Formal investigation of the effect of exposure mixtures is usually achieved by modelling interactions, which relies on strong assumptions relating to the identity and the number of the exposures involved in such interactions, and on the order and parametric form of these interactions. These hypotheses become difficult to formulate and justify in an exposome context, where influential exposures are numerous and heterogeneous. To capture both the complexity of the exposome and its possibly pleiotropic effects, models handling multivariate predictors and responses, such as partial least squares (PLS) algorithms, can prove useful. As an illustrative example, we applied PLS models to data from a study investigating the inflammatory response (blood concentration of 13 immune markers) to the exposure to four disinfection by-products (one brominated and three chlorinated compounds), while swimming in a pool. To accommodate the multiple observations per participant (n=60; before and after the swim), we adopted a multilevel extension of PLS algorithms, including sparse PLS models shrinking loadings coefficients of unimportant predictors (exposures) and/or responses (protein levels). Despite the strong correlation among co-occurring exposures, our approach identified a subset of exposures (n=3/4) affecting the exhaled levels of 8 (out of 13) immune markers. PLS algorithms can easily scale to high-dimensional exposures and responses, and prove useful for exposome research to identify sparse sets of exposures jointly affecting a set of (selected) biological markers. Our descriptive work may guide these extensions for higher dimensional data.


2007 ◽  
Vol 9 (3) ◽  
pp. 118-121 ◽  
Author(s):  
Jerzy Myszkowski ◽  
Eugeniusz Milchert ◽  
Waldemar Paździoch ◽  
Robert Pełech

Formation of environmentally friendly chloroorganic compounds technology by sewage and by-products utilization The processes presented in the study enables the separation and disposal of the chloroorganic compounds as by-products from the vinyl chloride plant by using the dichlorethane method and also from the production of propylene oxide by the chlorohydrine method. The integrated purification method of steam stripping and adsorption onto activated carbon allows a complete removal and recovery of the chloroorganic compounds from waste water. Waste distillation fraction is formed during the production of vinyl chloride. 1,1,2-trichloroethane separated from the above fraction, can be processed to vinylidene chloride and further to 1,1,1-trichloroethane. 2,3-Dichloropropene, 2-chloroallyl alcohol, 2-chloroallylamine, 2-chlorothioallyl alcohol or bis(2-chloroallylamine) can be obtained from 1,2,3-trichloropropane. In the propylene oxide plant the waste 1,2-dichloropropane is formed, which can be ammonolysed to 1,2-diaminopropane or used for the production of β-methyltaurine. Other chloroorganic compounds are subjected to chlorinolysis which results in the following compounds: perchloroethylene, tetrachloromethane, hexachloroethane, haxachlorobutadiene and hexachlorobenzene. The substitution of the milk of lime by the soda lye solution during the saponification of chlorohydrine eliminates the formation of the CaCl2 waste.


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