An occurrence study was conducted to measure five iodo-acids (iodoacetic acid, bromoiodoacetic acid, (Z)-3-bromo-3-iodo-propenoic acid, (E)-3-bromo-3-iodo-propenoic acid, and (E)-2-iodo-3-methylbutenedioic acid) and two iodo-trihalomethanes (iodo-THMs), (dichloroiodomethane and bromochloroiodomethane) in chloraminated and chlorinated drinking waters from 23 cities in the United States and Canada. Since iodoacetic acid was previouslyfound to be genotoxic in mammalian cells, the iodo-acids and iodo-THMs were analyzed for toxicity. A gas chromatography (GC)/negative chemical ionization-mass spectrometry (MS) method was developed to measure the iodo-acids; iodo-THMs were measured using GC/high resolution electron ionization-MS with isotope dilution. The iodo-acids and iodo-THMs were found in waters from most plants, at maximum levels of 1.7 microg/L (iodoacetic acid), 1.4 microg/L (bromoiodoacetic acid), 0.50 microg/L ((Z)-3-bromo-3-iodopropenoic acid), 0.28 microg/L ((E)-3-bromo-3-iodopropenoic acid), 0.58 microg/L ((E)-2-iodo-3-methylbutenedioic acid), 10.2 microg/L (bromochloroiodomethane), and 7.9 microg/L (dichloroiodomethane). Iodo-acids and iodo-THMs were highest at plants with short free chlorine contact times (< 1 min), and were lowest at a chlorine-only plant or at plants with long free chlorine contact times (> 45 min). Iodide levels in source waters ranged from 0.4 to 104.2 microg/L (when detected), but there was not a consistent correlation between bromide and iodide. The rank order for mammalian cell chronic cytotoxicity of the compounds measured in this study, plus other iodinated compounds, was iodoacetic acid > (E)-3-bromo-2-iodopropenoic acid > iodoform > (E)-3-bromo-3-iodo-propenoic acid > (Z)-3-bromo-3-iodo-propenoic acid > diiodoacetic acid > bromoiodoacetic acid > (E)-2-iodo-3-methylbutenedioic acid > bromodiiodomethane > dibromoiodomethane > bromochloroiodomethane approximately chlorodiiodomethane > dichloroiodomethane. With the exception of iodoform, the iodo-THMs were much less cytotoxic than the iodo-acids. Of the 13 compounds analyzed, 7 were genotoxic; their rank order was iodoacetic acid >> diiodoacetic acid > chlorodiiodomethane > bromoiodoacetic acid > E-2-iodo-3-methylbutenedioic acid > (E)-3-bromo-3-iodo-propenoic acid > (E)-3-bromo-2-iodopropenoic acid. In general, compounds that contain an iodo-group have enhanced mammalian cell cytotoxicity and genotoxicity as compared to their brominated and chlorinated analogues.

Fluorotelomer polymers are used in a broad array of products in modern societies worldwide and, if they degrade at significant rates, potentially are a significant source of perfluorooctanoic acid (PFOA) and related compounds to the environment To evaluate this possibility, we incubated an acrylate-linked fluorotelomer polymer in soil microcosms and monitored the microcosms for possible fluorotelomer (FT) and perfluorinated-compound (PFC) degradation products using GC/MS and LC/MS/MS. This polymer scavenged FTs and PFCs aggressively necessitating development of a multistep extraction using two solvents. Aged microcosms accumulated more FTs and PFCs than were present in the fresh polymer indicating polymer degradation with a half-life of about 870-1400 years for our coarse-grained test polymer. Modeling indicates that more-finely grained polymers in soils might have half-lives of about 10-17 years assuming degradation is surface-mediated. In our polymer-soil microcosms, PFOA evidently was lost with a half-life as short as 130 days, possibly by polymer-catalyzed degradation. These results suggest that fluoratelomer-polymer degradation is a significant source of PFOA and other fluorinated compounds to the environment.

Hypothalamic RFamide-related peptide-3 (RFRP-3) neurons inhibit LH secretion via a central action. A direct hypophysiotropic action on the gonadotropes has also been suggested. To assess central RFRP-3 effects on the GnRH/LH surge that induces ovulation, ovariectomized rats were subjected to an estradiol plus progesterone surge-induction protocol. Chronic infusion of RFRP-3 (2.5 or 25 ng/h, intracerebroventricularly) caused a dose-dependent 50-60% inhibition of GnRH neuronal activation (assessed by colocalization with the immediate early gene c-Fos) at the surge peak compared with vehicle-treated controls. RFRP-3 also suppressed neuronal activation in the anteroventral periventricular region, which provides stimulatory input to GnRH neurons, by 50-80% compared with control values. To test whether centrally administered RFRP-3 inhibits pulsatile GnRH/LH secretion, chronically ovariectomized, low-level estradiol-treated rats without surge induction were blood sampled every 10 min for 4 h. Bolus injection of RFRP-3 (0, 2.5, or 25 microg, intracerebroventricularly) after 1.5 h did not affect subsequent LH pulse frequency, pulse amplitude, or the mean concentrations of LH or prolactin. RFRP-3 treatment of isolated anterior pituitary cells at moderate doses of up to 10(-7) m did not significantly inhibit LH release, either with or without GnRH cotreatment. These data reveal a central inhibitory effect of RFRP-3 on the hypothalamo-pituitary gonadal axis specifically during the estradiol-induced GnRH/LH surge. This effect may include actions of RFRP-3 on GnRH neurons and/or their anteroventral periventricular afferent inputs but is unlikely to involve direct inhibition of LH secretion at the level of the gonadotrope.