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Recycle and Recovery of Aqueous Catalysts

In recent years, the evaluation of environmentally benign (so-called green processes) has been a focal point of oxo developments, according to the definitions and targets of the [Pg.124]

In this respect, risk minimization and life cycle assessments play a major role. [Pg.125]

The compound [HRh(C0)(TPPTS)3] is a precatalyst and dissociates to the 16e species [HRh(C0)(TPPTS)2]. This oxo-active complex initiates the hydroformylation cycle. Under oxo conditions (presence of CO/H2, H20, and a surplus of TPPTS) the hydroxo complex [(HO)Rh(CO)(TPPTS)2] may be formed and again reversibly converted to [HRh(C0)(TPPTS)3] (equilibrium lies almost completely towards the hydride). However, higher carbon monoxide partial pressures may cause the displacement of TPPTS by CO according to Equation 5.8. [Pg.126]

Catalyst deactivation includes (among other reactions) the formation of inactive Rh species, ligand decomposition, or P-C cleavage by direct oxidative insertion of the rhodium metal for formation of PDSPP (propyldi[w-sulfophenyl phosphine) acting as strong electron donor reducing the amount of active Rh catalyst. It turned out to be beneficial to control the Pni/Rh ratio and the CO partial pressure very carefully. [Pg.128]

After years of use catalyst solutions typically contain 20 mg-L 1 iron and 0.7 mg-L 1 of nickel, thus showing no corrosivity. The Rh content of crude aldehyde is in the ppb range this corresponds to losses of less than 10 9 g kg 1 n-butanal, totalling some kg rhodium over a twenty-year period and a production of approximately 5 million metric tons of n-butanal. [Pg.128]


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