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[
Trends in Neurosciences,
1996]
Touch sensitivity in humans is dependent on highly specialized cutaneous nerve endings encapsulated in elaborate cellular structures such as the Pacinian, Ruffini and Meissner's corpuscles. Although the details of the encapsulations vary, the common theme involves the nerve endings making intimate mechanical linkages with the collagen-fiber networks contained within each capsule. Presumably, it is these external linkages with the membrane that serve to transmit and focus mechanical energy onto the mechanotransducers located in the nerve endings, and thus contribute to their low threshold and high mechanosensitivity. Extracellular mechanical linkages are also a feature of specific touch sensors in lower invertebrates, and thus appear to have evolved early in the animal kingdom. Indeed, it seems wherever high mechanosensitivity is required external mechanical linkages are present. In contrast, pain sensation, which is characterized by high threshold and low mechanosensitivity, is mediated by naked or free nerve endings, which lack elaborate external structures. Despite the existence of detailed ultrastructural information, the general inaccessibility of vertebrate touch and pain receptors has hampered studies on the molecules and molecular interactions underlying mechanotransduction in these cells. However, recent molecular-genetic analysis of touch-insensitive mutants in the tiny, free-swimming round worm, Caenorhabditis elegans, carried out by Martin Chalfie and colleagues, has begun to reveal detailed information on the molecular machinery of mechanotransduction. This information should provide useful clues and general principles for unravelling the molecular mechanisms underlying our own sensations of touch and pain.
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[
J. Toxicol. Environ. Health Part A,
2008]
The toxicity of 10 organophophorus (OP) insecticides-acephate, dimethoate, dichlorvos, dicrotophos, monocrotophos, methamidophos, phosphamidon, omethoate, phosdrin, and trichlorfon-was evaluated in Caenorhabditis elegans using lethality, movement, and acetylcholinesterase (AChE) activity as the endpoints after a 4-hr- exposure period. The OP insecticides tested showed LC50 values ranging from 0.039 mM (for dichlorovs) to 472.8 mM (for methamidophos). The order of toxicity for lethality and movement was not significantly different when tested using the rank order correlation coefficient. AChE activity was markedly affected by all the OP insecticide exposures that caused significant inhibition in movement, indicating that the mechanism of toxicity of OP insecticides in C. elegans is the same as in higher animals. All OP insecticides induced greater than 50% inhibition of AChE at the lowest tested OP insecticide concentration resulting in inhibition in movement. While a significant correlation was evident between LC50 values in C. elegans and the LD50 values in rats for the 10 OP insecticides studied, a correlation was not evident between EC50 values in C. elegans and LD50 values in rats. Overall, the two endpoints, LC50 and movement, were more reliable and easier to perform than measurement of AChE activity in C. elegans for determining the toxicity of OP insecticides. Further, ranking of these endpoints with respect to the OP insecticides studied indicates that these parameters in C. elegans are predictive of OP insecticides mammalian neurotoxicity.
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[
International C. elegans Meeting,
1991]
The embryonic DD and postembryonic VD motoneurons innervate different sets of muscles. Inspite of differences in lineal origin and target specificity the two classes of D motoneurons exhibit a number of biochemical and morphological similarities. Our goal is to understand the genetic basis for these similarities and differences. A survey of the neural Unc's reveals mutations in a number of genes that cause identical changes in both classes. Currently only one gene, unc- 55, a ventral coiler, has been identified that specifically affects one of the two classes. Reconstructions by Nawrocki et al., have shown that the Unc-55 allele
e402 respecifies the VD motoneurons so that they innervate the same targets as the DD motoneurons. Our working hypothesis is that initially the genetic programs for both dasses of D motoneurons is the same and that
unc-55 is necessary and sufficient to create the different specificities. A maze was designed to aid in the search for suppressors of
unc-55. The maze, whose structure was inspired by the benzene ring, is effective in enriching for noncoiler phenotypes. Typically 95 to 100X of N2 animals navigate the maze and find the food in a 15 to 20 hour period. However, due to a number of blind alleys, <SX of unc-ff animals are successful. unc-ff strains CB 1170 and ER14 have been mutagenized with EMS following Brenner's procedure and F2 animals placed on the maze. The equivalent of 400,000 mutagenized chromosomes from CBl 170 and 100,000 chromosomes from ER14 have been screened with the maze. Presently we are characterizing two extragenic suppressors that are not coilers. Both are derived from ER14, each is X-linked and recessive. When separated from
unc-55 they exhibit difficulties in moving backward but they are not coilers. Further characterization is underway.
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[
BMC Genomics,
2009]
BACKGROUND: The wide use of organophosphorus (OP) pesticides makes them an important public health concern. Persistent effects of exposure and the mechanism of neuronal degeneration are continuing issues in OP toxicology. To elucidate early steps in the mechanisms of OP toxicity, we studied alterations in global gene and protein expression in Caenorhabditis elegans exposed to OPs using microarrays and mass spectrometry. We tested two structurally distinct OPs (dichlorvos and fenamiphos) and employed a mechanistically different third neurotoxicant, mefloquine, as an out-group for analysis. Treatment levels used concentrations of chemical sufficient to prevent the development of 10%, 50% or 90% of mid-vulval L4 larvae into early gravid adults (EGA) at 24 h after exposure in a defined, bacteria-free medium. RESULTS: After 8 h of exposure, the expression of 87 genes responded specifically to OP treatment. The abundance of 34 proteins also changed in OP-exposed worms. Many of the genes and proteins affected by the OPs are expressed in neuronal and muscle tissues and are involved in lipid metabolism, cell adhesion, apoptosis/cell death, and detoxification. Twenty-two genes were differentially affected by the two OPs; a large proportion of these genes encode cytochrome P450s, UDP-glucuronosyl/UDP-glucosyltransferases, or P-glycoproteins. The abundance of transcripts and the proteins they encode were well correlated. CONCLUSION: Exposure to OPs elicits a pattern of changes in gene expression in exposed worms distinct from that of the unrelated neurotoxicant, mefloquine. The functional roles and the tissue location of the genes and proteins whose expression is modulated in response to exposure is consistent with the known effects of OPs, including damage to muscle due to persistent hypercontraction, neuronal cell death, and phase I and phase II detoxification. Further, the two different OPs evoked distinguishable changes in gene expression; about half the differences are in genes involved in detoxification, likely reflecting differences in the chemical structure of the two OPs. Changes in the expression of a number of sequences of unknown function were also discovered, and these molecules could provide insight into novel mechanisms of OP toxicity or adaptation in future studies.
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[
International Worm Meeting,
2009]
Organophosphorus pesticides (OP) are insecticides that are widely used to control agricultural and household pests. Initially, OP were designed to affect the nervous system by inhibiting acetylcholinsterase (AChE). However, this is not the only mode of action that leads to toxic effects, as many OPs alter immune functions in mammals by oxidative damage, metabolism modifications, and stress-related immune-suppression. In addition, the mode-of-action of single OP has been thoroughly studied, but little is known about the effects of different combined OP in a mixture. To clarify the underlying mechanisms of OP toxicity and their possible interactions in mixtures, we determined genome-wide transcription profiles of C. elegans exposed to two OP: chlorpyriphos, diazinon and a mixture of both. The influence of temperature was determined by replicate experiments at 16 deg C and 24 deg C. For all treatments, we indentified significantly enriched GO terms and protein domains associated with detoxification, general stress response, ion transport, transport and metabolism of fatty acids, and immune response. Nevertheless, less than 10% of the regulated genes were common to all the treatments. Between the regulated genes we found cadmium responsive genes, genes downstream the
daf-2/daf-16 insulin like pathway, and genes associated with innate immune response. Furthermore, the comparison between single treatments of OPs and their mixtures suggest that, on the gene transcript level, the effect of the OPs mixture is not a summed effects of the single components. This emphasizes a specificity in mixture response involving similar mechanism of response (e.g.: detoxification, stress response or lipid mobilization) by dissimilar gene transcripts compared to single compound exposures. Moreover, we are further studying the influence of the temperature in OPs toxicity by comparison of our data at 16 deg C and 24 deg C. Initial results indicated a larger influence of temperature on the number of genes differently expressed than the toxicants. In other words temperature induces a much less specific gene transcription response than the specific response to toxicants.
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[
PLoS One,
2011]
Although organophosphorus pesticides (OP) share a common mode of action, there is increased awareness that they elicit a diverse range of gene expression responses. As yet however, there is no clear understanding of these responses and how they interact with ambient environmental conditions. In the present study, we investigated genome-wide gene expression profiles in the nematode Caenorhabditis elegans exposed to two OP, chlorpyrifos and diazinon, in single and combined treatments at different temperatures. Our results show that chlorpyrifos and diazinon induced expression of different genes and that temperature affected the response of detoxification genes to the pesticides. The analysis of transcriptional responses to a combination of chlorpyrifos and diazinon shows interactions between toxicants that affect gene expression. Furthermore, our combined analysis of the transcriptional responses to OP at different temperatures suggests that the combination of OP and high temperatures affect detoxification genes and modified the toxic levels of the pesticides.
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[
Sci Total Environ,
2020]
Carbamate pesticides (CMs) and organophosphorus pesticides (OPs) have been widely used in agriculture and toxicologically affect non-target organisms. Although there are many reports about their toxicities, the combined behavioral toxicities of CM/OP mixtures on Caenorhabditis elegans have rarely been studied. In this study, body bend inhibition (BBI), head thrash inhibition (HTI), and swimming speed inhibition (SSI) by CMs and OPs were chosen as the toxicity endpoints. The locomotion behavioral toxicities of individual pesticides (carbofuran (CAR), methomyl (MET), chlorpyrifos (CPF), and triazophos (TAP)) and their binary mixtures on C. elegans were determined systematically and the toxicological interaction profiles of various CM/OP mixture rays constructed using the combination index. It was shown that four pesticides and their binary mixture rays have significant inhibitory effects on the locomotion behavior of C. elegans; that is, they produce locomotion behavioral toxicities and the toxicity of two OPs is higher than those of two CMs. The toxicological interactions in the binary CM and OP mixtures are different from each other. For example, one mixture ray (CAR-MET-R1) in the CM system on the SSI endpoint exhibits synergism at all concentration levels, another ray (CAR-MET-R3) displays low-dose synergism and high-dose additive action on BBI and HTI endpoints, and weak synergism at high-dose on SSI, and other rays perform additive action. Two rays (CPF-TAP-R1 and CPF-TAP-R2) in the OP mixture system display low-dose additive action and high-dose antagonism on the three endpoints. Another ray (CPF-TAP-R3) shows the additive action at all concentration levels. It can be concluded that it is not sufficient to evaluate the combined toxicity of binary CM/OP mixtures using only one concentration ratio ray and that it is necessary to examine multiple concentration ratios.
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[
J Agric Food Chem,
2016]
Propolis from different areas has been reported to inhibit oncogenic/ageing kinase PAK1, which is responsible for a variety of conditions, including cancer, longevity and melanogenesis. Here, crude extract of Okinawa propolis (OP) was tested against PAK1 activity, Caenorhabditis elegans (C. elegans) longevity, melanogenesis, and growth of cancer cells. We found that OP blocks PAK1 and exhibits anti-cancer activity in A549 cell (human lung cancer cell) line with IC50 values of 6 g/mL and 12 g/mL, respectively. Most interestingly, OP (1 g/mL) significantly reduces reproduction and prolongs the lifespan of C. elegans by activating HSP-16.2 gene, as shown in the PAK1-deficient strain. Furthermore, OP inhibits melanogenesis in a melanoma cell line (B16F10), by downregulating intracellular tyrosinase activity with an IC50 of 30 g/mL. Our results suggest that OP demonstrated life span extending effect C. elegans, anticancer and antimelanogenic effects via PAK1 inactivation, therefore, this can be a potent natural medicinal supplement against PAK1-dependent diseases.
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[
PLoS One,
2010]
Organophosphorus pesticides (OPs) were originally designed to affect the nervous system by inhibiting the enzyme acetylcholinesterase, an important regulator of the neurotransmitter acetylcholine. Over the past years evidence is mounting that these compounds affect many other processes. Little is known, however, about gene expression responses against OPs in the nematode Caenorhabditis elegans. This is surprising because C. elegans is extensively used as a model species in toxicity studies. To address this question we performed a microarray study in C. elegans which was exposed for 72 hrs to two widely used Ops, chlorpyrifos and diazinon, and a low dose mixture of these two compounds. Our analysis revealed transcriptional responses related to detoxification, stress, innate immunity, and transport and metabolism of lipids in all treatments. We found that for both compounds as well as in the mixture, these processes were regulated by different gene transcripts. Our results illustrate intense, and unexpected crosstalk between gene pathways in response to chlorpyrifos and diazinon in C. elegans.
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[
J Biol Chem,
1994]
Bone morphogenetic proteins (BMPs) are multifunctional proteins, structurally related to transforming growth factor-beta (TGF-beta) and activin. TGF-beta and activin exert their effects by forming heteromeric complexes of type I and type II serine/threonine kinase receptors. We have previously identified a series of type I serine/threonine kinase receptors, termed activin receptor-like kinase (ALK)-1 to -6. ALK-5 is a TGF-beta type I receptor, whereas ALK-2 and ALK-4 are activin type I receptors. Here we investigated the binding of proteins in the BMP family to ALKs. In transfected COS cells, the binding of osteogenic protein (OP)-1 and BMP-4 to certain ALKs was observed in the absence of type II receptors, and their binding was increased after co-transfection of a BMP type II receptor from Caenorhabditis elegans, DAF-4. OP-1 bound to ALK-2 and ALK-6 efficiently, and to ALK-3 less efficiently, whereas BMP-4 bound to ALK-3 and ALK-6 efficiently. Similarly, OP-1 bound to ALK-2, ALK-3, and/or ALK-6 in various nontransfected cell lines, although the binding profiles were different between different cell types. BMP-4 bound to ALK-3 in MC3T3-E1 osteoblasts and human foreskin fibroblasts. These results suggest that ALK-3 and ALK-6 are type I receptors for OP-1 and BMP-4; in addition, ALK-2 is a type I receptor shared by activin and OP-1, but not by BMP-4.