G12/13 Signaling Pathways Substitute for Integrin αIIbβ3-Signaling for Thromboxane Generation in Platelets

We have previously shown that ADP-induced TXA(2) generation requires signaling from αIIbβ3 integrin in platelets. Here we observed that, unlike ADP, protease-activated receptor (PAR)-mediated TXA(2) generation occurs independently of αIIbβ3. PAR agonists, but not ADP, activate G(12/13) signaling pathways. Hence, we evaluated the role of these pathways in TXA(2) generation.Inhibition of ADP-induced thromboxane generation by fibrinogen receptor antagonist SC57101 was rescued by co-stimulation of G(12/13) pathways with YFLLRNP. This observation suggested an existence of a common signaling effector downstream of integrins and G(12/13) pathways. Hence, we evaluated role of three potential tyrosine kinases; c-Src, Syk and FAK (Focal Adhesion Kinase) that are known to be activated by integrins. c-Src and Syk kinase did not play a role in ADP-induced functional responses in platelets. Selective activation of G(12/13) pathways resulted in the activation of FAK, in the absence of integrin signaling. Interestingly, αIIbβ3-mediated FAK activation occurred in a Src family kinase (SFK)-independent manner whereas G(12/13) pathway caused FAK activation in a SFK and RhoA-dependent manner. A FAK selective inhibitor TAE-226, blocked TXA(2) generation. However, in comparison to WT mice, Pf4-Cre/Fak-Floxed mice did not show any difference in platelet TXA(2) generation.Therefore, we conclude that differential activation of FAK occurs downstream of Integrins and G(12/13) pathways. However, the common effector molecule, possibly a tyrosine kinase downstream of integrins and G(12/13) pathways contributing to TXA(2) generation in platelets remains elusive

A comprehensive treatment method for defluoridation of drinking water

314-318The fluoride concentration in ground water is increasing at an alarming rate. Poor ground water recharge, excessive consumption of water and other geological factors contribute to this effect. Conventional reverse osmosis (RO) membrane system has failed because fluoride concentration in permeate is not consistently below 1 mg/L. Moreover, the reject stream of the RO process containing higher fluoride concentration is left untreated. A treatment method has been devised with an objective to reduce fluoride concentration to less than 1 mg/L from fluoride contaminated water using calcium carbonate pretreatment and reverse osmosis. Also a passive adsorption system to treat the reject stream of membrane process has been developed wherein the fluoride concentration in the final effluent is below ambient concentration. This combined system can be used to treat fluoride contaminated water without generating secondary wastes