Oxidation of Fe(II) in rainwater.

Photochemically produced Fe(II) is oxidized within hours under environmentally realistic conditions in rainwater. The diurnal variation between photochemical production and reoxidation of Fe(II) observed in our laboratory accurately mimics the behavior of ferrous iron observed in field studies where the highest concentrations of dissolved Fe(ll) occur in afternoon rain during the period of maximum sunlight intensity followed by gradually decreasing concentrations eventually returning to early morning pre-light values. The experimental work presented here, along with the results of kinetics studies done by others, suggests thatthe primary process responsible for the decline in photochemically produced Fe(II) concentrations is oxidation by hydrogen peroxide. This reaction is first order with respect to both the concentrations of Fe(II) and H2O2. The second-order rate constant determined for six different authentic rain samples varied over an order of magnitude and was always less than or equal to the rate constant determined for this reaction in simple acidic solutions. Oxidation of photochemically produced ferrous iron by other oxidants including molecular oxygen, ozone, hydroxyl radical, hydroperoxyl/superoxide radical, and hexavalent chromium were found to be insignificant under the conditions present in rainwater. This study shows that Fe(II) occurs as at least two different chemical species in rain; photochemically produced Fe(II) that is oxidized over time periods of hours, and a background Fe(II) that is protected against oxidation, perhaps by organic complexation, and is stable against oxidation for days. Because the rate of oxidation of photochemically produced Fe(II) does not increase with increasing rainwater pH, the speciation of this more labile form of Fe(II) is also not controlled by simple hydrolysis reactions.

Photochemical production of Fe(II) in rainwater.

Significant concentrations of Fe(II) were produced upon irradiation of authentic rainwater with simulated sunlight. The magnitude of photoproduction was dependent on initial Fe(II), Fe(III), and hydrogen ion concentrations, with more Fe(II) photoproduction when initial Fe(III) and H+ concentrations were high and initial Fe(II) concentrations were low. An equation was developed that accurately predicts photoproduction of Fe(II) in rainwater based on initial Fe speciation values and pH. The quantum yield of Fe(II) photochemical production in rain decreased dramatically with increasing wavelength and decreasing energy of incoming radiation with the average quantum yield at 265 nm approximately an order of magnitude greater than at 546 nm. Probable photochemical precursors of Fe(II) in authentic rain include iron(III) oxalate, iron(III) hydroxide, and an undefined Fe(III) complex. The wavelength-dependent Fe(II) production was modeled using the average Fe(II) efficiency spectrum, an average rainwater absorption spectrum, and the modeled actinic flux for temperate latitudes in both summer and winter. The response spectrum has the highest photoproduction of Fe(II) in summer and winter at 325 and 330 nm, respectively, with greater production in summer rain due to increased actinic flux and longer hours of irradiation.

Biliary function studies during multiple time periods in freely moving rats. A useful system and set of marker solutes.

Biliary output of endogenous and exogenous compounds is altered by anesthesia, depletion of bile salts, and hydrostatic pressure. The described system for bile function studies minimizes these confounding factors by substantially modifying existing methods. Experiments were conducted in freely moving rats which eliminates effects of anesthesia or restraint-induced stress. Depletion of bile salts was prevented by intraduodenal infusion of taurocholate which maintains bile volume. Bile was collected in containers taped to the rat's back which minimizes hydrostatic forces induced by lengthy or elevated biliary cannulas. Animals were prepared for hepatobiliary function studies 1 week before experiments by placement and exteriorization of a jugular cannula and a bile duct to duodenal fistula. Experiments involved monitoring biliary outputs of marker solutes for various pathways of bile formation during three sequential time periods of 120 min, that is, a basal period in the morning and two experimental periods in the afternoon. We found similar patterns of biliary output in each time period for small i.v. doses of conventional exogenous markers [3H-taurocholate, phenolphthalein glucuronide, indocyanine green, and horseradish peroxidase] and for less commonly studied endogenous markers [glucose, inorganic phosphate (Pi), total protein, and leucine aminopeptidase]. This temporal stability indicates a lack of confounding circadian variability for these markers during the course of the biliary function study. Biliary excretion patterns of these marker solutes (e.g., rapid high recoveries of phenolphthalein glucuronide and low concentrations of Pi and glucose) demonstrated that our system for bile function studies is associated with intactness of the examined pathways of bile formation. These results validate our system and set of marker solutes for in vivo biliary function studies.(ABSTRACT TRUNCATED AT 250 WORDS)

Protection by L-2-oxothiazolidine-4-carboxylate, a cysteine prodrug, against 1,1-dichloroethylene hepatotoxicity in rats is associated with decreases in toxin metabolism and cytochrome P-450.

Our objective was to determine if the intracellular cysteine precursor, L-2-oxothiazolidine-4-carboxylate (OTZ), would protect rats against the hepatotoxicity of 1,1-dichloroethylene (DCE) by altering the toxin's biologic fate. Fasted male rats were pretreated with 10 mmol of OTZ per kg s.c. in saline or with saline only 1 hr before administration of 14C-labeled DCE (50 mg/kg) p.o. in mineral oil. Serial blood samples were taken from permanent jugular cannulas between 1 and 24 hr to monitor the time course of injury and circulating levels of 14C-derived label. DCE caused less liver injury in the OTZ-pretreated group. This protection was associated with about 50% less total, acid soluble and acid precipitable 14C-label in serum; 30% less label in urine; and at 24 hr, 30 to 68% less covalently bound label in liver, kidney and lung. Extent of peak liver injury in individual animals correlated well with the amount of 14C-label in serum at early times and with the amount covalently bound to liver at 24 hr, but correlated poorly with label excreted into urine. An explanation for the apparent decrease in DCE metabolism by OTZ-pretreated animals was investigated by examining effects of OTZ on liver constituents known to have a role in DCE metabolism. Fasted rats given 10 mmol of OTZ per kg showed a persistent loss of hepatic cytochrome P-450 at 3 and 6 hr whereas their hepatic and renal reduced glutathione contents were transiently diminished at 3 hr.(ABSTRACT TRUNCATED AT 250 WORDS)

Potentiation of 1,1-dichloroethylene hepatotoxicity: comparative effects of hyperthyroidism and fasting.

The responses of fed, fasted, and hyperthyroid (T4) Sprague-Dawley male rats to 50 mg 1,1-dichloroethylene (1,1-DCE)/kg were compared. Hyperthyroid rats received three sc injections of thyroxine (100 micrograms/100 g) at 48-hr intervals; all other rats were sham-injected. 1,1-DCE was given po in mineral oil 24 hr after the last T4 dose; controls received only mineral oil. Animals were killed at 2, 4, and 8 hr. Liver GSH contents were lowered about 55% by both fasting and T4 while GSH transferase activities were lowered about 20% by fasting and 35% by T4. Only T4 pretreatment lowered alcohol dehydrogenase activities. Liver injury (i.e., serum glutamate pyruvate transaminase, histology) after 1,1-DCE was minimal in fed rats, moderate in fasted rats, and intermediate in T4 rats. Fasted rats showed a more pronounced depletion of liver GSH after 1,1-DCE than T4 rats and only in fasted rats did the toxicant decrease activities of the detoxification enzymes. Hypoglycemia after 1,1-DCE occurred in fed rats, but more rapidly in T4 rats. In contrast, fasted rats unexpectedly became hyperglycemic after the toxicant. Patterns of body temperature change after the toxicant, which might be due to its metabolites, were dissimilar. Hypothermia was not observed in fed rats, was only transiently evident in T4 rats, but occurred rapidly within 1 hr in fasted rats and steadily became more severe. The dissimilar patterns of liver enzyme and body temperature and serum glucose change after the toxicant in the three groups are indicative of different pathways of injury potentiation by fasting and hyperthyroidism.