Pathogenesis of cell toxicity by plant toxins

Ribosome inactivating proteins (RIPs) are a family of plant proteins that depurinate the major rRNA, inhibiting the protein synthesis. RIPs are divided into type 1, single chain proteins with enzymatic activity, and type 2 RIPs (toxic and non-toxic), with the enzymatic chain linked to a binding chain. RIPs have been used alone or as toxic component of immunotoxins for experimental therapy of many diseases. The knowledge of cell death pathway(s) induced by RIPs could be useful for clarifying the mechanisms induced by RIPs and for designing specific immunotherapy. The topic of the current study was (i) the determination of the amino acid sequence of the type 2 RIP stenodactylin. The comparison with other RIPs showed that the A chain is related to other toxic type 2 RIPs. whereas the B chain is more related to the non-toxic type 2 RIPs. This latter result is surprising because stenodactylin is actually the most toxic type 2 RIP known; (ii) the study of the cell death mechanisms induced by stenodactylin in human neuroblastoma cells (NB100). High doses of stenodactylin can activate the effector caspases (perhaps through the DNA damage and/or intrinsic/extrinsic pathways) and also cause ROS generation. Low doses cause a caspase-dependent apoptosis, mainly via extrinsic pathway. Moreover, the activation of caspases precedes the inhibition of protein synthesis; (iii) the investigation of the cell death pathway induced by the non-toxic type 2 RIPs ebulin l and nigrin b. These RIPs demonstrated high enzymatic activity in a cell-free system, but they lack high cytotoxicity. These preliminary studies demonstrate that the cell death mechanism induced by the two non-toxic RIPs is partially caspase-dependent apoptosis, but other mechanisms seem to be involved

Effects of pesticides on honey bees (Apis mellifera L.): study of a specific route of exposure and evaluation of biochemical-physiological changes in the assessment of the pesticides toxicity

In this study, some important aspects of the relationship between honey bees (Apis mellifera L.) and pesticides have been investigated. In the first part of the research, the effects of the exposure of honey bees to neonicotinoids and fipronil contaminated dusts were analyzed. In fact, considerable amounts of these pesticides, employed for maize seed dressing treatments, may be dispersed during the sowing operations, thus representing a way of intoxication for honey bees. In particular, a specific way of exposure to this pesticides formulation, the indirect contact, was taken into account. To this aim, we conducted different experimentations, in laboratory, in semi-field and in open field conditions in order to assess the effects on mortality, foraging behaviour, colony development and capacity of orientation. The real dispersal of contaminated dusts was previously assessed in specific filed trials. In the second part, the impact of various pesticides (chemical and biological) on honey bee biochemical-physiological changes, was evaluated. Different ways and durations of exposure to the tested products were also employed. Three experimentations were performed, combining Bt spores and deltamethrin, Bt spores and fipronil, difenoconazole and deltamethrin. Several important enzymes (GST, ALP, SOD, CAT, G6PDH, GAPDH) were selected in order to test the pesticides induced variations in their activity. In particular, these enzymes are involved in different pathways of detoxification, oxidative stress defence and energetic metabolism. The results showed a significant effect on mortality of neonicotinoids and fipronil contaminated dusts, both in laboratory and in semi-field trials. However, no effects were evidenced in honey bees orientation capacity. The analysis of different biochemical indicators highlighted some interesting physiological variations that can be linked to the pesticide exposure. We therefore stress the attention on the possibility of using such a methodology as a novel toxicity endpoint in environmental risk assessment.