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Trail:

Ecosystems

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Scientific papers - Ecosystems - page 2


 
TSEs and the misfolded metallo-glycoprotein, prion protein
 
Metalloproteins require specific complementary metals which assist in their folding, catalytic and/or metabolic activities (12). Alternative ‘foreign’ metals can sometimes substitute for the correct metal partner during periods of deficiency. For instance, Mn2+ or Fe2+ can also ligate onto the nitrogen of the histidine imidazole rings of certain Cu metalloproteins (12), resulting in the formation of misfolded isoforms which can no longer perform their correct metabolic functions


TSEs are considered to result from the accumulation of an abnormal protease resistant misfolded isoform of a nerve membrane metalloglycoprotein called prion protein (PrP) (5). PrP is largely expressed in the CNS and lymphatic systems (5).


It is proposed that TSE pathogenesis is initiated (Fig. 1) once Mn2+ or Mn3+ substitutes for Cu at the ‘vacated’ histidine sites of Cu domains on PrP (15) and other cuproproteins such as the beta amyloid precursor protein. This could occur during periods of Cu deficiency, when PrP subsequently looses its correct conformation, ‘metamorphosing’ into a misfolded PrP-foreign transition metal complex, whereby Mn2+, or its oxidised Mn3+ species, serves as the ‘so called’ infectious transmissible agent whose potentially lethal auto-oxidative capacity (7,11) is carried along with PrP like a ‘trojan horse’ until the introduction of oxygen re-activates its latent oxidative capacity. At this point Mn3+ initiates a more aggressive auto-oxidative cascade of free radical chain reaction, involving the auto-oxidation of dopamine, serotonin and adrenaline; it is recognised that Mn3+ readily oxidises these catecholamines (10,7,11) forming 6-hydroxy-dopamine, etc, which, in turn, oxidise more rapidly, forming quinones and superoxide/hydroxyl radicals which modify the catecholamine terminals, which could theoretically modify various amino acids on PrP and other membrane proteins. Such radical chain reactions would be prone to proliferate in mammals living in environments that are depleted in Cu, Fe, Zn, Se. Such deficiencies cause a down regulation in the turnover of the SOD, catalase, peroxidase and vitamin E scavengers (10).).

Fig. 1   The multifactorial aetiological template underpinning the pathogenesis of sporadic TSEs, where an Mn3+ initiated chain reaction of auto oxidation invokes a multi site radical attack on PrP and other CNS membrane/cytoskeletal proteins.


The pathogenic scenario involving the cycling of the stable Mn2+ and Mn3+ species can be likened to the redox cycling of the paraquat herbicide molecule and its role in initiating a Parkinsons-like pathogenesis (10,13,14,16). Alternating double bonds and ‘resonance energy’ within paraquat provides a stable ‘dormant’ radical which auto oxidises once oxygen is introduced. After reduction within the cell it reacts with oxygen to generate the lethal superoxide radical.(17)


Mn is also recognised to activate some species of lectin, such as phytohemagglutinins and concanavalin A (4), where high levels of free Mn can accelerate the normal rate of concanavalin A interaction with cell surface glycoproteins, such as PrP. Interestingly, the action of concanavalin A and phytohemagglutins mediates a 3.5 fold increase in the surface abundance of PrP (18). Furthermore, increases in both the surface expression of PrP and CNS membrane receptor capping with concanavalin A are consistently recorded in the early stages of the TSE disease process (19), suggesting that an excess of available Mn in the CNS could putatively perform a key role (via lectin activation) in initiating these facets of TSE pathogenesis.
 
CU CHELATING CHEMICALS INDUCE SPONGIFORM ENCEPHALOPATHIES
 
Cuprizone, neocuproine, mercaptoethanol, dithiophosphates and triethyltin are ‘true’ Cu chelating chemicals (20-22) which deplete Cu supplies in the CNS producing a ‘non-transmissible’, reversible type of spongiform encephalopathy. Cuprizone was actually utilised as a research tool for inducing a scrapie-like spongiosis in mice at Compton laboratories during the 1970s (23). CNS Cu deficiency could therefore represent one of the key prerequisites underlying TSE pathogenesis - albeit one which fails to account for the transmissible facet of TSEs.
On the other hand, treatment with the ‘pseudo’ types of Cu chelating chemical such as diethyldithiocarbamate (DEDTC) (24) which chelate and redistribute Cu around the body rather than chelating and excreting it, do not produce spongiform encephalopathy (25); Allain et al. (24) treated rats with DEDTC which resulted in a 77% increase of Cu levels in the brain. Furthermore, DEDTC redistributes Cu into regions of the CNS that do not normally exhibit Cu binding ligands, thereby depositing free Cu in the extracellular space so it can initiate lipid peroxidation and chain reactions of hydroxyl and Cu 3 radical formation (10). Exposures to DEDTC and its parent compound sulfiram has been associated with the development of Parkinson’s disease and other extrapyramidal disorders (24, 26-28), supporting the proposal that CNS Cu deficiency rather than CNS Cu overloading is associated with TSE aetiology.
 
Is CNS Cu deficiency a prerequisite for TSEs?
 
Certain facets of TSE pathogenesis, such as tissue increase of Fe store, found as Ferritin (29), indicate a state of Cu/Fe deficiency.


Furthermore, Lung tissues of copper deficient chicks have demonstrated abnormal variations in the concentration of various types of glycoaminoglycans (30). The possibility of an ‘in vivo’ metabolic relationship between PrP reduction within the cell, it reacts with oxygen to generate the lethal superoxide radical (17) and the glycoaminoglycans becomes evident after studying the TSE disease process (5); where concentrations of the sulphated glycoaminoglycans are raised in the CNS of diseased animals, whilst dramatic therapeutic benefits are witnessed ‘in vitro’ when TSE affected cell cultures are treated with these molecules. It seems likely that the normal cellular form of PrP (PrPc) binds with a specific co-species of glycoaminoglycans ‘in vivo’, which might serve as a means of protecting PrPc against conversion into its abnormal TSE isoform. This hypothesis proposes that CNS Cu deficiency is integral to the aetiology of TSEs, where the depleted supply of Cu to PrP’s Cu domain renders the protein vulnerable to invasion with alternative cations, such as Mn, which could ligate to the Cu domain and lead to the development of the misfolded, pathogenic prion associated with TSE.


CNS Cu deficiency can be invoked via various naturally occurring or artificially invoked mechanisms, or combinations thereof:

  1. due to indigenous copper deficiency in the external food chain (influenced by seasonal, climatic and/or other geological (3, 4, 31) characteristics such as high soil molybdenum levels).

  2. due to an oxidant mediated upregulation of the expression of Cu-metalloproteins, such as PrP, placing demands on the supply of available Cu in the CNS (32, 15, 33, 34).

  3. due to chelation of available Cu in the CNS by certain foreign organo pollutants (21).

  4. due to the inhibitory effects placed on Cu absorption by excesses of Ca or estrogens (35, 36) as in feeds such as alfalfa/soya respectively.

  5. due to the accelerated excretion of Cu resulting from therapeutic treatment with steroids, etc (37). due to a foreign organic pollutant induced covalent modification of (or binding to) the active histidine/tyrosine residues (10 p45) (12) (38) (39) on PrP’s Cu domain; thereby preventing Cu from accessing its binding domain on PrP (15, 34).

Experimental evidence indicates a role for PrP's Cu domain in protecting the cell against oxidative stress; via a PrP-mediated regulation of SOD1 activity.

D Brown and others have provided strong ‘in vitro’ and ‘in vivo’ experimental evidence that supports a functional role for PrPc in protecting CNS cerebellar cells against the deleterious impact of oxidative stress (33). Treatment with the antioxidant vitamin E has also been shown to protect cells lacking PrP expression against oxidant mediated cell death (33).


Brown proposes that PrPc influences the activity of SOD1 (40) and points to the Cu domain that has been identified at the N terminal octapeptide repeat region of PrP (15, 34) , suggesting that PrP may perform a role in the transportation of Cu to the sites of SOD 1 synthesis, Cu and Zn act as co factors in the synthesis of the SOD 1 superoxide scavenger. Mice devoid of PrP due to genetic ablation demonstrate a reduced resistance to oxidative stress. Cu and Zn act as co factors in the synthesis of the SOD 1 superoxide scavenger. Mice devoid of PrP due to genetic ablation demonstrate a reduced resistance to oxidative stress.

The key biochemical and pathological facets of TSE suggest a pivotal role of oxidative stress in TSE pathogenesis.

The biochemistry, pathology and distribution of CNS abnormalities associated with the pathogenesis of TSEs suggests that oxidative stress plays a major aetiological role in TSEs;


Decreased amounts of phospholipids and gangliosides/increased levels of cholesterol in membranes (41, p.100), an abundance of lipofuscin inclusions in neurones (42), an upregulation of the signal transduction cycle and kinase C phosphorylation, increases in intraneuronal free calcium (43, 44), reduction in monamine oxidase/NAD diaphorase (45,46), an increase in citrulline/ornithine in blood sera (47), a decrease in membrane fluidity (41, p.106), rupturing of lysosomal membranes (46), an excessive CNS accumulation of iron in its Ferritin form (29), and a marked increase in multimeric mitochondrial DNA/DNA strand breakage (48). All of these abnormalities are characteristic of free radical disturbances (10, 49-52) and are shared in the pathogenesis of other neurodegenerative diseases similar to TSEs such as Parkinsons (PD), Alzheimer’s (AD) and Motor Neurone Disease (MND) - diseases which are now recognised to stem from a free radical-mediated pathogenesis (52, 53).


It is proposed that the different ‘strains’ of TSEs may be caused by different species of radical-generating divalent cation (Mn, Nickel, Fe or cobalt, etc.) that can successfully compete and ligate at PrP’s Cu domain during states of Cu deficiency. The greater the oxidative capacity of the metal species involved (e.g. Mn3+, Mn4+ or even radioactive species), the more virulent strain of TSE to emerge. This aetiological model operates in combination with various other multifactorial criteria:

  1. The duration and intensity of exposure to the different classes of divalent cation/organic chemical pollutant in the environment, (more directly related to the particular species of radical that they generate).
  2. The TSE-susceptibility of the exposed individual; relating to their PRP (41)/SOD 1,2,3/ceruloplasmin/cytochrome P450 genotype.
  3. Other external environmental variables which can ultimately influence the CMS uptake of Mn, e.g.:
    1. low Fe,
    2. levels of stress or environmental pollutants which mediate ACTH turnover, blood-brain barrier homeostatis and Mn uptake in CNS.
    3. Daylight interval in relation to the untra violet mediated regulation of melatonin turn over, which, in turn, mediates estrogen/corticosteroid turn over and Mn uptake.
    4. levels of estrogenic/steroid pollutants in the environment (4,54) and their ability to upregulate the expression of caeruloplasmin (55) which can lead to oxidation of increased amounts of Mn2+ into its more lethal Mn3+ species (7), particularly in the absence of its normal oxidation target, Fe2+.
  1. The developmental stage of the victim during intoxication (56).

    SPORADIC TSEs - AN ANALYTICAL SURVEY INTO THE LEVELS OF METALS IN ECOSYSTEMS SUPPORTING CLUSTERS OF TSE: DESIGN

    Foodchains supporting isolated, long standing clusters of sporadic TSEs were sampled by the author for analysis of mineral status in order to ascertain whether any elemental deficiencies or toxic excesses are common idiosncratic characteristics of these TSE foci, Adjoining TSE-free regions populated by significant numbers of the respective species associated with thee study were sampled as controls.


    The TSE clusters of chronic wasting disease (CWD) in wild deer/elk in N. Central Colorado (57,58), sheep scrapie in N Iceland (59,60) and CJD in Slovakia (61-64) were selected for this survey for various reasons:

    1. A long history of TSE being confined to specific well-defined regions.
    2. The dependence of TSE affected populations on the local foodchain.
    3. The relative freedom of those foodchains (excluding the Slovakia TSE foci) from excessive contamination by synthetic pro-oxidant industrial/agricultural pollutants which would complicate the study.

    The repeated failure of various Government TSE eradication programmes executed in the TSE endemic regions of Colorado/Iceland (57,59) - involving blanket slaughter, 4 year fallow, then restocking - suggests the persistent presence of a hitherto unrecognized environmental causal factor common to these regions.
    It is worth noting that high altitude, snow covered peaked mountain ranges of volcanic origin - with an abundance of coniferous trees - characterize the environments where sporadic TSE foci have traditionally arisen. This could be linked to the annual spring snow thaw and the resulting waterlogging of soils; where the main minerals utilized as antioxidant cofactors in biological systems are leached out of the soil, whilst others, like manganese/aluminium, readily accumulate in the plant horizon as a result of the temporary acidification of the soils due to increases in anaerobic conditions during the wet season.
    Furthermore, the hypoxia of high-altitude lining increases susceptibility to oxidative stress and increases permeability of the brain barrier to cations, etc.

     

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