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Christopher J Kirk

Publications and source records attributed to Christopher J Kirk.

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Complex changes in cellular inositol phosphate complement accompany transit through the cell cycle.

Inositol polyphosphates other than Ins(1,4,5)P3 are involved in several aspects of cell regulation. For example, recent evidence has implicated InsP6, Ins(1,3,4,5,6)P5 and their close metabolic relatives, which are amongst the more abundant intracellular inositol polyphosphates, in chromatin organization, DNA maintenance, gene transcription, nuclear mRNA transport, membrane trafficking and control of cell proliferation. However, little is known of how the intracellular concentrations of inositol polyphosphates change through the cell cycle. Here we show that the concentrations of several inositol polyphosphates fluctuate in synchrony with the cell cycle in proliferating WRK-1 cells. InsP6, Ins(1,3,4,5,6)P5 and their metabolic relatives behave similarly: concentrations are high during G1-phase, fall to much lower levels during S-phase and rise again late in the cycle. The Ins(1,2,3)P3 concentration shows especially large fluctuations, and PP-InsP5 fluctuations are also very marked. Remarkably, Ins(1,2,3)P3 turns over fastest during S-phase, when its concentration is lowest. These results establish that several fairly abundant intracellular inositol polyphosphates, for which important biological roles are emerging, display dynamic behaviour that is synchronized with cell-cycle progression.

Animals↗

Alkylphenol endocrine disrupters inhibit IP3-sensitive Ca2+ channels.

We have investigated the influence of alkylphenol endocrine disrupters and the synthetic estrogen diethylstilbestrol (DES) on inositol-1,4,5-trisphosphate (IP(3))-sensitive Ca(2+) channels from porcine cerebellum and rat testicular membranes. All alkylphenols and DES inhibited the extent of IP(3)-induced Ca(2+) release (IICR) from both cerebellar and testicular microsomes. 4-n-nonylphenol was the most potent compound tested (IC(50), 8 microM). Inhibition of IICR was directly related to the length and hydrophobicity of the alkylphenol side chain. None of the alkylphenols or DES appeared to influence the concentration dependence of IICR nor did they have a significant effect on [3H]IP(3) binding to the membranes. An investigation of the effects of nonylphenol on the transient kinetics of IICR showed that it inhibited the rate constants for both the fast and the slow phases of IICR and also the extent of Ca(2+) release. These results illustrate another mechanism by which these environmental pollutants can disrupt endocrine function without the involvement of estrogen receptors.

Animals↗

Environmental endocrine disrupters dysregulate estrogen metabolism and Ca2+ homeostasis in fish and mammals via receptor-independent mechanisms.

Xenoestrogen endocrine disrupters (EDs) in the environment are thought to be responsible for a number of examples of sexual dysfunction that have recently been reported in several species. There is growing concern that these compounds may also cause abnormalities of the male reproductive tract and reduced spermatogenesis in man. Whilst some effects of EDs may be receptor-mediated, there is growing evidence that these compounds can exert potent effects in vivo by directly interacting with cellular enzyme targets. Here we report on, and review, the effects of alkylphenols and other EDs on two such enzymes: (1) sulfotransferases, which convert active estrogenic steroids to inactive steroid sulfates; and (2) Ca(2+)-ATPases, which are responsible for maintaining low, physiological, intracellular Ca(2+) concentrations. These enzymes are potently inhibited by EDs in both fish and mammalian species. The increased concentrations of active estrogens and the likely cytotoxic effects of elevated concentrations of intracellular Ca(2+) arising from these effects may underlie some of the endocrine disrupting potential of these widespread industrial pollutants.

Animals↗