| Literature DB >> 19242548 |
Abstract
BACKGROUND: MS pathogenesis seems to involve both genetic susceptibility and environmental risk factors. Three sequential factors are implicated in the environmental risk. The first acts near birth, the second acts during childhood, and the third acts long thereafter. Two candidate factors (vitamin D deficiency and Epstein-Barr viral infection) seem well suited to the first two environmental events. METHODOLOGY/PRINCIPALEntities:
Mesh:
Year: 2009 PMID: 19242548 PMCID: PMC2644781 DOI: 10.1371/journal.pone.0004565
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
Prevalence of antibodies to EBV in the sera of patients and controls.
| Study | EBV+ MS Cases (%) | EBV+ Controls (%) | p value |
| Sumaya, 1980 | 155/157 (98.7%) | 76/81 (93.8%) | 0.05 |
| Bray, 1983 | 309/313 (98.7%) | 363/406 (89.4%) | 0.0001 |
| Larson, 1984 | 93/93 (100%) | 78/93 (83.9%) | 0.0001 |
| Sumaya, 1985 | 104/104 (100%) | 23/26 (88.5%) | 0.007 |
| Shirodaria, 1987 | 26/26 (100%) | 24/26 (92.3%) | - |
| Munch, 1998 | 137/138 (99.3%) | 124/138 (89.9%) | 0.0004 |
| Myhr, 1998 | 144/144 (100%) | 162/170 (95.3%) | 0.008 |
| Wagner, 2000 | 107/107 (100%) | 153/163 (93.9%) | 0.01 |
| Ascherio, 2001 | 143/144 (99.3%) | 269/287 (93.7%) | 0.008 |
| Sundström (2004) | 234/234 (100%) | 693/702 (98.7%) | ns |
| Haahr, 2004 | 153/153 (100%) | 50/53 (94.3%) | 0.05 |
| Ponsonby, 2005 | 136/136 (100%) | 252/261 (96.6%) | 0.05 |
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Study measured antibodies against the Epstein-Barr nuclear antigens (EBNA), the viral capsid antigen (VCA), and the early antigens (EA).
Study measured antibodies only against VCA.
Study measured antibodies only against EBNA and EA.
Study measured antibodies only against EBNA and VCA. One person was antibody negative to each antigen but it is unclear from the text whether they were the same person. The review by Haahr in 2006 [81] suggests they were not.
Study measured antibodies only against EBNA and VCA.
Figure 1Possible causal pathways (1–4) leading to MS, which include genetic factors (G), vitamin D deficiency (VD), Epstein-Barr virus (EBV) infection, and other unidentified environmental factors (O1–O4).
The other environmental factors along the different pathways to MS have been designated O1–O4 because these relevant (but unknown) factors need not be the same along each path. In the Figure, the first two environmental events are represented as an appropriately‐timed vitamin D deficiency and an appropriately‐timed EBV infection. However, the association of these specific events with the first and second environmental events (discussed in the text) is not a necessary part of the Model itself.
Definition of Terms used in the Model.
| Time Period 1 | = | the period of (1941–1945) |
| Time-Period 2 | = | the period of (1976–1980) |
| R | = | Percentage of women in the MS population (i.e. if the ratio of women to men in the population is 3.2∶1, then: R = (3.2)/(4.2) = 0.76). |
| PG | = | the probability (i.e., the prevalence) of genetic susceptibility (gender not specified) |
| PGW | = the probability of genetic susceptibility in women | |
| PGM | = the probability of genetic susceptibility in men | |
| PE | = | probability that a “sufficient” environmental exposure occurs (all factors; gender not specified) |
| PEW | = probability that a “sufficient” environmental exposure occurs (all factors; in women) | |
| PEM | = probability that a “sufficient” environmental exposure occurs (all factors; in men) | |
| PG,E | = | the probability that both genetic and environmental exposures occur (gender not specified) |
| CRMZ | = | the proband-wise monozygotic-twin concordance-rate (gender not specified) |
| Zm | = the proband-wise concordance-rate (CRMZ) in men | |
| Zw | = the proband-wise concordance-rate (CRMZ) in women | |
| PE* | = | (PE|G)(PMS|G, E) = CRMZ |
| = | the probability of an “effective” exposure in a “susceptible” individual, including both the necessary environmental and random events (gender not specified) | |
| PEW* | = (PEW|GW)(PMS|GW, EW) = Zw | |
| = the probability of an “effective” exposure in a “susceptible” individual, including both the necessary environmental and random events in women | ||
| PEM* | = (PEM|GM)(PMS|GM, EM) = Zm | |
| = the probability of an “effective” exposure in a “susceptible” individual, including both the necessary environmental and random events in men | ||
| PVD | = | probability of a “sufficient” vitamin D deficiency at an appropriate time |
| PEBV | = | probability of a “sufficient” EBV infection at an appropriate time |
| PO | = | probability of a “sufficient” exposure to other unidentified factors at an appropriate time |
| PMS | = | the probability (prevalence) of MS in the population (expressed in cases per 100,000 population; gender not specified). |
| C | = | (PMS1) / (PMS2) |
| = | the ratio of the previous to the current prevalence (probability) of MS in the population; (C≥0). | |
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| = | the hazard-rate for “effective” exposure to environmental factors |
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| = | the level of actual environmental exposure experienced by the population. |
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| = | the difference in threshold level of actual environmental exposure between men (i.e., when: | |
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| = | the product of the actual level of exposure and the hazard-rate for “effective” exposure to environmental factors. One exposure unit (whatever this represents) is defined such that: |
Subscripts are used to designate the level of different parameters at different time-periods [e.g., X1, Zw1, Zm1, R1, PEW1*, PEM1*, and PMS1 are the levels of these parameters in (1941–1945); and X2, Zw2, Zm2, R2, PEW2*, PEM2*, and PMS2 are the levels of these parameters in (1976–1980)].
Prevalence (probability) of genetic susceptibility in populations in different geographic regions.
| Location | MS Prevalence | MZ Concordance | Latitude | % Susceptible |
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| Canada | 68–248 | 25.3% | N45–60° | 0.3–1.0 |
| Canadian Women | 152.4 | 34.0% | 0.45 | |
| Canadian Men | 47.6 | 6.5% | 0.73 | |
| Northern US | 100–160 | 31.4% | N41–45° | 0.3–0.5 |
| Southern US | 22–112 | 17.4% | N30–41° | 0.1–0.6 |
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| Finland | 52–93 | 46.2% | N60–70° | 0.1–0.2 |
| Denmark | 110 | 24% | N55–58° | 0.5 |
| British Isles | 74–193 | 40.0% | N50–59° | 0.2–0.5 |
| France | 32–65 | 11.1% | N44–50° | 0.3–0.6 |
| Sardinia | 144–152 | 22.2% | N39–41° | 0.6–0.7 |
| Italy | 38–90 | 14.5% | N38–46° | 0.3–0.6 |
Per 100,000 population. The prevalence of MS (i.e., the measure used to estimate PMS) for each region is taken from data provided in [51]. A range is given because, often, a range of estimates are available for a particular region.
Studies (9,11, and 12) reported pair-wise monozygotic-twin (MZ) concordance-rates and these have been converted into proband-wise rates assuming a random sampling of twin-pairs (see Appendix S1). Also, the error associated with the estimate of CRMZ for each region has not been taken into account.
Calculated according to Equation (3):See text for details. Because the prevalence of possessing at least one copy of the HLA DRB1*1501 susceptibility allele is 30% in the general populations of northern Europe and northern North America(i.e., PHLA+) and 55% in the MS populations(i.e., PHLA+ MS) from these regions [2], [103] and assuming approximately equal penetrance for the different susceptibility genotypes [10], the observation that (PG≈0.5%) indicates that only about 1% of individuals who carry this allele are even susceptible to MS. Thus:.
Because both men and women come from the same Canadian population, the actual disease prevalence is irrelevant and, therefore, a range of estimates is unnecessary. Nevertheless, the current prevalence of MS in Canada (for the purpose of these calculations) was taken to be 100 per 100,000 population [10] and divided according to the current sex ratio of 3.2∶1 in Canada [65].
Parameter estimates using different the sex-ratios (Female∶Male) reported in Canada over the period from 1931 to 1980*.
| Time-Period | a | b | b/a | λ | Cmax
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| 1931–1935 | 0.083 | 0.477 | 5.73 | −0.270 | 0.76 |
| 1936–1940 | 0.079 | 0.465 | 5.86 | −0.396 | 0.73 |
| 1941–1945 | 0.078 | 0.449 | 5.75 | −0.373 | 0.76 |
| 1946–1950 | 0.075 | 0.434 | 5.77 | −0.462 | 0.75 |
| 1951–1955 | 0.074 | 0.417 | 5.60 | −0.377 | 0.80 |
| 1956–1960 | 0.072 | 0.403 | 5.58 | −0.448 | 0.79 |
| 1961–1965 | 0.072 | 0.385 | 5.37 | −0.231 | 0.89 |
| 1966–1970 | 0.070 | 0.370 | 5.31 | −0.188 | 0.92 |
| 1971–1975 | 0.067 | 0.356 | 5.37 | −0.772 | 0.75 |
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Values derived from reference [65] for the condition where (C = 0.5) and assuming the change in the environmental factor (whatever this is) has been steadily increasing (i.e., linear) over the time-interval (sd = standard deviation). The estimates for the parameters a and b trend downward in the more recent time-intervals because the definition of a unit of environmental change (see Table 2) becomes smaller with more recent observation periods. The other estimates are unaffected by this circumstance (see Equations 14, 17, and 21).
Values for the maximum value that C could take (see text); extrapolated backward to the (1941–1945) time-period for comparison.
Figure 2Derived response curves for men and women of an “effective” exposure to the environmental factors (PE*) with increasing levels of actual exposure (x), as described in the text and in the Appendix.
These curves are based upon the “current” proband-wise monozygotic-twin concordance-rates for men and women in Canada [10] and upon the change in the sex-ratio observed in Canada between the two time-periods [65]. However, in deriving this set of curves, two further assumptions have been made. First it has been assumed that the currently observed values for Zw2 and Zm2 are accurate [10]. Second, it is assumed that C (defined in Table 2) is equal to one half (i.e., that the prevalence of MS has doubled between the two time intervals). Of course, the actual level of environmental exposure (whatever this represents) is unknown. Nevertheless, the environmental exposure has been scaled such that the difference in the actual exposure level between these two time-periods (whatever this is), multiplied by the unknown hazard rate, is assigned the arbitrary value of one exposure unit (see Table 2). In these curves, the probability of a “sufficient” exposure to the entire set of environmental events (PE) is assumed to have changed (in some manner) as the actual level of exposure (x) of the population has increased between the two time intervals of study. This change in (PE), however, could be due to a change in only one, in some, or in all of the relevant environmental factors. NB: Although the two time-periods of (1941–1945) and (1976–1980), which were used for parameter estimation, are shown along the x-axis, this axis represents an increasing (but unknown) environmental exposure. It is not a time-axis.