TFA from HFO-1234yf: accumulation and aquatic risk in terminal water bodies

A next-generation mobile automobile air-conditioning (MAC) refrigerant, HFO-1234yf (CF(3) CF = CH(2)), is being developed with improved environmental characteristics. In the atmosphere, it ultimately forms trifluoroacetic acid (TFA(A); CF(3)COOH), which is subsequently scavenged by precipitation and deposited on land and water as trifluoroacetate (TFA; CF(3)COO(-)). Trifluoroacetate is environmentally stable and has the potential to accumulate in terminal water bodies, that is, aquatic systems receiving inflow but with little or no outflow and with high rates of evaporation. Previous studies have estimated the emission rates of HFO-1234yf and have modeled the deposition concentrations and rates of TFA across North America. The present study uses multimedia modeling and geographic information system (GIS)-based modeling to assess the potential concentrations of TFA in terminal water bodies over extended periods. After 10 years of emissions, predicted concentrations of TFA in terminal water bodies across North America are estimated to range between current background levels (i.e., 0.01-0.22 µg/L) and 1 to 6 µg/L. After 50 years of continuous emissions, aquatic concentrations of 1 to 15 µg/L are predicted, with extreme concentrations of up to 50 to 200 µg/L in settings such as the Sonoran Desert along the California/Arizona (USA) border. Based on the relative insensitivity of aquatic organisms to TFA, predicted concentrations of TFA in terminal water bodies are not expected to impair aquatic systems, even considering potential emissions over extended periods.

Quantitative characterization of short- and long-chain perfluorinated acids in solid matrices in Shanghai, China

Perfluorinated acids (PFAs) have been recognized as emerging environmental pollutants because of their widespread occurrences, persistence, and bioaccumulative and toxicological effects. PFAs have been detected in aquatic environment and biota in China, but the occurrences of these chemicals have not been reported in solid matrices in China. In the present study, short- and long-chain PFAs (C2-C14) have been quantitatively determined in solid matrices including sediments, soils and sludge collected in Shanghai, China. The results indicate that sludge contains more PFAs than sediments and soils, and the total PFAs concentrations in sediments, soil and sludge are 62.5-276 ng g(-1), 141-237 ng g(-1) and 413-755 ng g(-1), respectively. In most cases, trifluoroacetic acid was the major PFA and accounted for 22-90% of the total PFAs. Although the levels of perfluorooctanoate (PFOA) and perfluorooctanesulfonate (PFOS) were not only lower than trifluoroacetic acid, but also lower than some short-chain PFCAs (<C8) in some individual cases, PFOA and PFOS were still the major pollution compounds in most cases and they constituted 2-34% and 1-9% of the total PFAs, respectively. Meanwhile, unlike previous studies, PFOS levels were not always higher than PFOA in solids collected in Shanghai, China. Given that some short-chain PFAs such as trifluoroacetic acid are mildly phytotoxic and their higher levels in solid matrices were collected in Shanghai, China, these chemicals should be included in future environmental monitoring efforts.

Effect of trifluoroacetate, a persistent degradation product of fluorinated hydrocarbons, on Phaseolus vulgaris and Zea mays

The aim of this study was to quantify the effect of the pollutant, trifluoroacetate (TFA), on growth and photosynthesis of Phaseolus vulgaris (C(3)) and Zea mays (C(4)) in order to elucidate the physiological and biochemical basis of its inhibitory action. In whole plant studies, photosynthetic gas exchange, fast phase fluorescence kinetics and Rubisco activity were measured in parallel over a 14-day period in plants cultivated in a water culture system with NaTFA added at concentrations ranging from 0.625 to 160mgl(-1). Although initial stimulation of some photosynthetic parameters was observed at low TFA concentrations early on in the experiment, marked inhibition occurred at higher concentrations. In general Z. mays was affected more severely than P. vulgaris showing a large TFA-induced decrease in both apparent carboxylation efficiency (ACE) and in vitro Rubisco (ribulose-1,5-bisphosphate carboxylase/oxygenase; EC 4.1.1.39) activity. Analysis of photosynthetic gas exchange revealed that besides constraints on mesophyll processes such as Rubisco activity, stomatal limitation also increased with increasing TFA concentration, especially in P. vulgaris. In depth analysis of the fast phase fluorescence transients pointed at TFA-induced uncoupling of the oxygen evolving complex (OEC) and inhibition of electron transport beyond Q(a) including possible constraints on the reduction of end electron acceptors of photosystem I.

Trifluoroacetylated adducts in spermatozoa, testes, liver and plasma and CYP2E1 induction in rats after subchronic inhalatory exposure to halothane

The induction of cytochrome P450 (CYP) 2E1 in testes and liver and the presence of trifluoroacetylated (TFA) adducts in spermatozoa, testes, liver and plasma were investigated in rats subchronically exposed by inhalation to halothane (15 ppm/4 h/day/5 days/week/9 weeks). After halothane exposure, p-nitrophenol hydroxylase (p-NPH) activity increased 3.2-fold and CYP2E1 apo-protein content 7-fold in testes, whereas in liver, p-NPH increased 2.3-fold and CYP2E1 apoprotein content 1.4-fold. These results suggest a differential inductive effect of halothane on CYP2E1 in these tissues. Moreover, TFA adducts were present in microsomes of testis and liver and in plasma of halothane-treated rats. The immunoblot analysis of testicular microsomes showed two intense TFA protein bands of 63 and 59 kDa, whereas in liver three intense bands of 100, 76 and 63 kDa were observed. Bands of similar molecular weights to those observed in liver were detected in the plasma of halothane-treated animals. In addition, TFA adducts were detected by immunofluorescence in spermatozoa, probably in the acrosome and/or perinuclear theca region, and in the distal tail of spermatozoa. The increase in CYP2E1 apoprotein and p-NPH activity observed in testis and liver microsomes suggests that halothane induces its own biotransformation both hepatically and extrahepatically and in addition, that the nature of the TFA adducts will depend on the proteins present in each tissue. Also, the presence of TFA adducts in spermatozoa may result from the activation of halothane in the reproductive tract. The detailed mechanism of TFA adduct formation and its consequences on the spermatozoa function remain to be fully clarified.

Trichloroacetic acid (TCA) and trifluoroacetic acid (TFA) mixture toxicity to the macrophytes Myriophyllum spicatum and Myriophyllum sibiricum in aquatic microcosms

Trichloroacetic acid (TCA) and trifluoroacetic acid (TFA) have been detected together in environmental water samples throughout the world. TCA may enter into aquatic systems via rainout as the degradation product of chlorinated solvents, herbicide use, as a by-product of water disinfection and from emissions of spent bleach liquor of kraft pulp mills. Sources of TFA include degradation of hydrofluorocarbons (HFCs) refrigerants and pesticides. These substances are phytotoxic and widely distributed in aquatic environments. A study to assess the risk of a binary mixture of TCA and TFA to macrophytes in aquatic microcosms was conducted as part of a larger study on haloacetic acids. M. spicatum and M. sibiricum were exposed to 0.1, 1, 3 and 10 mg/l of both TCA and TFA (neutralized with sodium hydroxide) in replicate (n = 3) 12000 l aquatic microcosms for 49 days in an one-way analysis of variance design. Each microcosm was stocked with 14 individual apical shoots per species. The plants were sampled at regular intervals and assessed for the somatic endpoints of plant length, root growth, number of nodes and wet and dry mass and the biochemical endpoints of chlorophyll-a, chlorophyll-b, carotenoid content and citric acid levels. Results indicate that there were statistically significant effects of the TCA/TFA mixture on certain pigment concentrations immediately after the start of exposure (2-7 days), but the plants showed no signs of stress thereafter. These data suggest that TCA/TFA mixtures at environmentally relevant concentrations do not pose a significant risk to these aquatic macrophytes.

Uptake, toxicity, and effects on detoxication enzymes of atrazine and trifluoroacetate in embryos of zebrafish

The uptake, toxicity, and elimination of atrazine and trifluoroacetate (TFA) were studied in early life stages of the zebrafish (Danio rerio). Furthermore, the effects of these xenobiotics on soluble (s) and microsomal (m) glutathione S-transferases (GST) of zebrafish embryos were investigated using 1-chloro-2,4-dinitrobenzene (CDNB), 1,2-dichloro-4-nitrobenzene (DCNB), and [(14)C]atrazine. [(14)C]Atrazine was taken up by the embryos within seconds, unhindered by the chorions. It accumulated in the embryos by a factor of 19 after 24 h of exposure time. LC(50) (48 h) was determined at 36.8 mg/L. At a level of 5 mg/L atrazine, activities of s and m GSTs were elevated in most stages, especially in prim 6 and long pec stage (24, 48 h after fertilization, respectively). GST activity toward atrazine was detectable only in untreated D. rerio eggs, increasing with developmental time. [(14)C]Atrazine was eliminated from the embryos between 24 and 48 h, indicating a possible metabolism to a more hydrophilic GSH conjugate. [(14)C]TFA was taken up by embryos, reaching at maximum fivefold the concentration of the incubation medium after 10 h. The chorions served no physiological protection. TFA (1 g/L) caused low elevation of the GST activity. No acute toxic effects (48 h) were observed up to 4 g/L TFA.

Postnatal hepatic and renal consequences of in utero exposure to halothane or its oxidative metabolite trifluoroacetic acid in the rat

In utero exposure of rats to low levels of the anaesthetic halothane has been reported to produce ultrastructural changes in the liver and kidney at birth. The current study examined the postnatal functional capacities of the liver and the kidney following prenatal exposure to halothane. Halothane or its oxidative metabolite trifluoroacetic acid (TFAA) were given to Sprague-Dawley rats on gestational days 10-20. Halothane was administered by inhalation at concentration of 50 or 500 ppm 6 h-1 day-1, and TFAA was administered by gavage at doses of 75 or 150 mg kg-1 day-1. The exposed offsprings were examined on postnatal days 3, 12 or 49 for hepatic and renal biochemistry and/or function through measurements of several serum and urinary parameters. Neither halothane nor TFAA treatments had statistically significant effect on litter size, neonatal survival or postnatal growth. Both prenatal halothane and TFAA exposure produced changes in liver biochemistry of newborns, as indicated by significant increases in the serum activities of glutamate dehydrogenase and aspartate aminotransferase. In addition, TFAA caused a functional deficit of the proximal tubule in newborns, as evidenced by the significant increase in the urinary excretion of beta 2-microglobulin. However, these hepatic and renal alterations were restricted to the early postnatal period and were no longer observed by postnatal day 49. It is concluded that prenatal exposure to relatively low levels of halothane can cause slight and transient changes in the neonatal rat liver.

Rat liver metabolism and toxicity of 2,2,2-trifluoroethanol

2,2,2-Trifluoroethanol (TFE) is a metabolite of anesthetic agents and chlorofluorocarbon alternatives. Its toxicity in rats is a consequence of its metabolism to 2,2,2-trifluoroacetaldehyde (TFAld) and then to trifluoroacetic acid (TFAA). The enzymes involved in the toxic metabolic pathway have been investigated in this study. For the reaction of TFE to TFAld, the major hepatic metabolism associated with toxicity (as assessed by pyrazole-inhibitability) was NADPH dependent and occurred in the microsomes, whereas for TFAld conversion to TFAA, NADPH-dependent microsomal metabolism was significant, but mitochondrial and cytosolic metabolism in the presence of NADPH were also major contributors. NADPH-dependent hepatic microsomal metabolism of TFE to TFAld and TFAld to TFAA was inhibited by carbon monoxide, 2-allyl-2-isopropylacetamide, SKF-525A, metyrapone, imidazole, and pyrazole, and both reactions were oxygen dependent. The metabolism of TFE to TFAld was inhibited by diethyldithiocarbamate, a specific inhibitor of cytochrome P450E1, and by a monoclonal antibody to P4502E1, whereas the metabolism of TFAld was inhibited by neither. Ethanol pretreatment of rats enhanced the Vmax for hepatic microsomal metabolism of TFE to TFAld from 5.3 to 9.7 nmol/mg protein/min, while for TFAld to TFAA the Vmax was increased from 4.3 to 6.5 and the Km was unaffected for both reactions. Phenobarbital pretreatment of the rats did not affect any of these kinetic parameters. Coadministration of ethanol and a lethal dose of TFE very markedly decreased the lethality. Both the lethality (LD50 0.21 to 0.44 g/kg) and the metabolic kinetic parameters [(Vmax/Km)H(Vmax/Km)D = 4.2] were affected markedly when deuterated TFE replaced TFE. In contrast, deuteration of TFAld did not affect its lethality or rates of metabolism, but did affect its Km. Taken together these results indicate that P4502E1 catalyzed toxicity-associated hepatic metabolism of TFE to TFAld, while TFAld metabolism was catalyzed by a P450 which was not P4502E1. The hepatic metabolism of TFAld was not associated with its toxicity, which has been determined previously to be associated with its intestinal metabolism.

N-trifluoroacetyl derivatives as pharmacological agents. V. Evaluation of antiinflammatory and antimicrobial activities of some N-heterocyclic trifluoroacetamides

Following the investigation on pharmacological aspects of N-trifluoroacetyl compounds some heterocyclic trifluoroacetamides were prepared and explored as potential antiinflammatory-analgesic and antimicrobial agents. The trifluoroacetamides 3, 4, 5, and 6 reached significant activity in the hot plate analgesic test; the same 4 and 5, along with 7 and 8 showed inhibitory properties in the adjuvant arthritis test; only 7 however, displayed a significant dose-dependent activity in the carrageenin edema test. In addition the parent heterocyclic amines were similarly explored for comparison. Test for antimicrobial activity were carried out in parallel. Among the examined compounds, only 4-aminomorpholine and 2-aminobenzimidazole were found active when assayed against gram+ and gram- bacteria and mycetes.

2,2,2-Trifluoroethanol intestinal and bone marrow toxicity: the role of its metabolism to 2,2,2-trifluoroacetaldehyde and trifluoroacetic acid

2,2,2-Trifluoroethanol (TFE) produces bone marrow and small intestine toxicity resulting in leukopenia, loss of intestinal dry weight, and consequent lethal septicemia in male Wistar rats. Its metabolic pathway, based on serum and small intestine time courses of substrate and metabolites, was determined to be TFE in equilibrium 2,2,2-trifluoroacetaldehyde (TFAld)----trifluoroacetic acid (TFAA). Administered TFE and TFAld were not toxic per se, since their toxicity and metabolism were inhibited by pyrazole. TFE and TFAld were equipotent at equimolar doses thus precluding the oxidative reaction, TFE to TFAld, from being the toxic step. Since equimolar TFAA exhibited no toxic effects, an oxidative intermediate on the pathway from TFAld to TFAA, most likely F3C-C+(OH)2, must thus be the toxic moiety. The intermediate TFAld is stable in serum, as determined by a novel assay developed for its analysis in biological systems, and can be transported to the target tissues, bone marrow, and small intestine, after formation probably in the liver. On the basis of the more rapid metabolism of TFE to higher levels of TFAld in the small intestine and bone marrow than in the serum, the closer correspondence of bone marrow and small intestine metabolite ratios than serum ratios at high and low doses of TFE to the corresponding ratios of toxicity, and the decreased toxicity of TFAld when administered ig versus ip, the formation of the toxic metabolic intermediate of TFE probably occurs in the target tissues.

Trifluoroethanol and its oxidative metabolites: comparison of in vivo and in vitro effects in rat testis

Trifluoroethanol (TFE) and trifluoroacetaldehyde (TFALD) produced a reduction in testis weight 3 days after a single oral dose of 10 mg/kg. In contrast, administration of trifluoroacetic acid (TFAA) caused no observable testicular effects. Reduction in testis weight was accompanied by morphological changes, involving specific damage to pachytene and dividing spermatocytes, and round spermatids. In an in vitro Sertoli/germ cell co-culture system, only TFALD was found to produce dose-related effects at concentrations of 10(-3) and 10(-4) M. There was increased germ cell loss from the cultures, particularly loss of pachytene and dividing spermatocytes, accompanied by leakage of the pachytene spermatocyte marker enzyme, lactate dehydrogenase-X. TFE and TFAA did not produce these effects in the culture system at concentrations equimolar with TFALD. These results suggest that TFALD may play a critical role in the development of the testis lesion seen with TFE in vivo. The effects seen both in vivo and in vitro were remarkably similar to those previously reported for another substituted alcohol and its metabolites, ethylene glycol monomethyl ether. It is postulated that the two series of compounds may have a similar mode of action on rat testis.