Toxicokinetics and biotransformation of pentachlorophenol in the topsmelt (Atherinops affinis)

Pentachlorophenol and other chlorinated phenols are substrates for human hydroxysteroid sulfotransferase hSULT2A1

Pentachlorophenol (PCP) is a persistent chemical contaminant that has been extensively investigated in terms of its toxicology and metabolism. Similar to PCP, other chlorinated phenol derivatives are also widely present in the environment from various sources. Even though some of the chlorine-substituted phenols, and particularly PCP, are well-known inhibitors of phenol sulfotransferases (SULTs), these compounds have been shown to undergo sulfation in humans. To investigate the enzymatic basis for sulfation of PCP in humans, we have studied the potential for PCP as well as the mono-, di-, tri-, and tetra-chlorinated phenols to serve as substrates for human hydroxysteroid sulfotransferase, hSULT2A1. Our results show that all of these compounds are substrates for this isoform of sulfotransferase, and the highest rates of sulfation are obtained with PCP, trichlorophenols, and tetrachlorophenols. Much lower rates of sulfation were obtained with isomers of monochlorophenol and dichlorophenol as substrates for hSULT2A1. Thus, the sulfation of polychlorinated phenols catalyzed by hSULT2A1 may be a significant component of their metabolism in humans.

Toxicokinetics and biotransformation of p-nitrophenol in white sturgeon (Acipenser transmontanus)

White sturgeon (Acipencer transmontanus) were exposed to 7.2 microM (1.0 ppm) 14C-labeled p-nitrophenol (PNP) in brackish water for 24 h and then allowed to depurate in clean brackish water for another 24h. Absorption, conditional uptake clearance, and conditional elimination rate constants were 0.08+/-0.04 h(-1), 8.1+/-3.6 mL g(-1) h(-1), and 0.46+/-0.21 h(-1), respectively. A whole-organism total concentration factor of 18.7+/-2.6 was determined from equilibrium tissue and water concentrations. Sturgeon depurated 89.4% of absorbed PNP within 24h, of which 53.0+/-8.3% was unmetabolized parent compound, 9.6+/-3.6% was p-nitrophenyl-beta-d-glucuronide, and 39.1+/-8.3% was p-nitrophenylsulfate.

Toxicokinetics and biotransformation of p-nitrophenol in red abalone (Haliotis rufescens)

Red abalone (Haliotis rufescens) were exposed to 3.6 microM (0.5 ppm) 14C-labelled p-nitrophenol (PNP) for 24 h, then were allowed to depurate in clean seawater for another 24 h. Absorption, conditional uptake clearance and elimination rate constants were 0.12+/-0.04 h(-1), 3.2+/-1.1 ml g(-1) h(-1) and 0.05+/-0.02 h(-1), respectively. The sigmoidal shape of the PNP uptake curve suggests a biphasic process. A whole-organism total concentration factor (TCF) of 2.37+/-0.07 was determined from equilibrium tissue and water concentrations, with the highest concentration of PNP plus metabolites found in gill tissue (11.8+/-0.2 nmol g(-1), wet weight). Digestive gland, foot muscle and remaining body tissues accumulated 8.8+/-0.9, 7.7+/-0.6 and 7.5+/-0.6 nmol g(-1) radiolabelled residues, respectively. Abalone depurated 91.6% of absorbed PNP within 24 h, of which 87.5+/-3.1% was unmetabolized parent compound, 13.1+/-3.1% was p-nitrophenylsulfate, 0.32+/-0.09% was p-nitroanisole, and 0.14+/-0.07% was p-acetamidophenol.

Systemic uptake and cutaneous disposition of pentachlorophenol in a sequential exposure scenario: effects of skin preexposure to benzo[a]pyrene

Characterizing interactions caused by sequential skin exposures to various environmental toxicants can be critical for a meaningful risk assessment. To assess sequential chemical exposure effect on chemical cutaneous disposition and systemic uptake of a toxicant, [(14)C]pentachlorophenol (PCP) was topically administered in three porcine skin models (in vivo, ex vivo, and in vitro) at 40 micro g/cm(2) with or without skin preexposure to benzo[a]pyrene (BaP), a known human carcinogen and cutaneous cytochrome P-450 (CYP450) inducer. In the mass balance studies, BaP skin preexposure was found to enhance (14)C absorption in all three models with detectable in vivo effect during the first several days. Total 8-h absorption was tripled by skin preexposure to BaP in the ex vivo (1.1 to 3.2%) and in vitro (0.20 to 0.66%) systems. As seen in the extended in vivo studies, total absorption was 50-57% regardless of exposure conditions, suggesting the prolonged observation period may conceal existing impact of potentially modified disposition processes, such as cutaneous metabolism, on systemic absorption. Skin preexposure to the skin CYP450 inducer BaP largely changed label penetration depth and distribution pattern in cutaneous tissues and decreased (14)C concentration in skin and fat. Additionally, BaP preexposure altered (14)C systemic tissue disposition, suggesting that altered cutaneous PCP disposition may eventually change the toxicity profile (cutaneous vs. systemic risk). The preliminary tissue distribution and systemic absorption data suggested that skin preexposure to BaP may considerably modify cutaneous biotransformation rate and thus deserves further investigation. The dermal model-dependent impacts of expected skin biotransformation manipulation by preexposure to chemicals such as BaP on cutaneous disposition and systemic uptake of environmental toxicants such as PCP need to be considered in risk assessment.

The fate of organic xenobiotics in aquatic ecosystems: quantitative and qualitative differences in biotransformation by invertebrates and fish

Biotransformation of natural and man-made foreign compounds (xenobiotics) proceeds via introduction of a functional group (phase I metabolism) and subsequent attachment of a polar moiety to the group (phase II metabolism). The biotransformation fate of xenobiotics depends on the activities, complement and inducibility of the biotransformation enzymes. Previous analysis of the dependence of in vivo rates of biotransformation on tissue parent compound concentration for marine invertebrates revealed that hydrocarbons are metabolised more slowly than xenobiotics already containing functional groups, and crustaceans metabolise both types of xenobiotics faster than molluscs (Livingstone D.R., Persistent pollutants in marine ecosystems, pp. 3-34, Pergamon, Oxford). Use of the same approach showed that fish metabolise pentachlorophenol (PCP) and benzo[a]pyrene (BaP) faster than certain aquatic invertebrates, viz. rates of biotransformation to total metabolites (pmol min-1 g-1 wet wt.) at a tissue parent compound concentration of 10 nmol g-1 were, respectively, 19.2 +/- 3.7 (Carassius auratus) and 4.8 +/- 6.6 (molluscan species) (PCP), and 19.1 +/- 6.3 (fish species) and 2.1 +/- 0.2 (crustacean species) (BaP). The higher rate of biotransformation of BaP in fish is consistent with higher levels of total cytochrome P450 and inducible cytochrome P4501A (CYP1A) activity. The similar rate of metabolism of a hydrocarbon (BaP) (requires initial metabolism by cytochrome P450) and a functional group compound (PCP) by fish may also be due to the high levels of cytochrome P450, compared with the situation in invertebrates where rate-limiting cytochrome P450 may be responsible for the lower rates of hydrocarbon compared with functional group compound metabolism.

Toxicokinetics and biotransformation of pentachlorophenol in the sea urchin (Strongylocentrotus purpuratus)

1. The toxicokinetics and biotransformation of pentachlorophenol (PCP) were determined in the purple sea urchin (Strongylocentrotus purpuratus). 2. In a static chamber, urchins (n = 9) were individually exposed to 50 micrograms/l of [U-14C]PCP for 24 h to determine bioconcentration and the absorption rate constant (Ka), elimination rate constant (Ke), and elimination half-life (t1/2). Determination was by direct quantitation of radioactivity in the exposure water. 3. After exposure, urchins were placed in a flow-through chamber for 24 h to allow depuration of retained residues, which were identified by hplc and quantified by lsc. The Ka and Ke, calculated using a simplified model, were 0.12 +/- 0.06 h and 0.43 +/- 0.22 h, respectively, whilst the 24-h total concentration factor was 316.3 +/- 209.7, and the t1/2 was 1.6 +/- 0.8 h. 4. Whereas urchins depurated 40.6% of retained residues, only a small amount of PCP was excreted unchanged (17.0%), as the more polar conjugates pentachlorophenyl-beta-D-glucoside (72.4%) and pentachlorophenylsulphate (10.6%) were also formed.