October 18, 2011
Abstract
Background
Recent reports have drawn attention to increases in congenital birth anomalies and cancer in Fallujah Iraq blamed on teratogenic,
genetic and genomic stress thought to result from depleted Uranium contamination following the battles in the town in 2004.
Contamination of the parents of the children and of the environment by Uranium and other elements was investigated using Inductively
Coupled Plasma Mass Spectrometry. Hair samples from 25 fathers and mothers of children diagnosed with congenital anomalies
were analysed for Uranium and 51 other elements. Mean ages of the parents was: fathers 29.6 (SD 6.2); mothers: 27.3 (SD 6.8).
For a sub-group of 6 women, long locks of hair were analysed for Uranium along the length of the hair to obtain information
about historic exposures. Samples of soil and water were also analysed and Uranium isotope ratios determined.
Results
Levels of Ca, Mg, Co, Fe, Mn, V, Zn, Sr, Al, Ba, Bi, Ga, Pb, Hg, Pd and U (for mothers only) were significantly higher than
published mean levels in an uncontaminated population in Sweden. In high excess were Ca, Mg, Sr, Al, Bi and Hg. Of these only
Hg can be considered as a possible cause of congenital anomaly. Mean levels for Uranium were 0.16 ppm (SD: 0.11) range 0.02
to 0.4, higher in mothers (0.18 ppm SD 0.09) than fathers (0.11 ppm; SD 0.13). The highly unusual non-normal Fallujah distribution
mean was significantly higher than literature results for a control population Southern Israel (0.062 ppm) and a non-parametric
test (Mann Whitney-Wilcoxon) gave p = 0.016 for this comparison of the distribution. Mean levels in Fallujah were also much
higher than the mean of measurements reported from Japan, Brazil, Sweden and Slovenia (0.04 ppm SD 0.02). Soil samples show
low concentrations with a mean of 0.76 ppm (SD 0.42) and range 0.1-1.5 ppm; (N = 18). However it may be consistent with levels
in drinking water (2.28 μgL-1) which had similar levels to water from wells (2.72 μgL-1) and the river Euphrates (2.24 μgL-1). In a separate study of a sub group of mothers with long hair to investigate historic Uranium excretion the results suggested
that levels were much higher in the past. Uranium traces detected in the soil samples and the hair showed slightly enriched
isotopic signatures for hair U238/U235 = (135.16 SD 1.45) compared with the natural ratio of 137.88. Soil sample Uranium isotope
ratios were determined after extraction and concentration of the Uranium by ion exchange. Results showed statistically significant
presence of enriched Uranium with a mean of 129 with SD5.9 (for this determination, the natural Uranium 95% CI was 132.1 <
Ratio < 144.1).
Conclusions
Whilst caution must be exercised about ruling out other possibilities, because none of the elements found in excess are reported
to cause congenital diseases and cancer except Uranium, these findings suggest the enriched Uranium exposure is either a primary
cause or related to the cause of the congenital anomaly and cancer increases. Questions are thus raised about the characteristics
and composition of weapons now being deployed in modern battlefields
Keywords:
Fallujah; Iraq; congenital anomaly; cancer; heavy metals; Depleted Uranium; hair analysisBackground
Health effects from wars in Iraq
There have been reports of increased rates of cancer and congenital anomaly (CA) from Fallujah, Iraq [1,2]. This spectrum of health conditions points to the existence of some historic exposure which has caused significant teratogenic,
genetic or genomic stress to the population. In addition to the increased cancer and rates and infant deaths, the epidemiological
study [1] showed that there was a sudden significant drop in the sex ratio (an indicator of genetic stress) in the cohort born in 2005,
one year after the battles which occurred in the city, suggesting that the cause of all these effects is related to the time
of the US led invasion of the city in 2004. Because of the lack of knowledge of the respondents in this questionnaire about
the precise cause of death of their children, that study focused on infant mortality as an indicator of birth defects. Results
showed levels of infant mortality of around 80 per 1000 live births in children, which can be compared with a figure of 17
in Jordan and 9 in Kuwait. However, it seems that the findings in Fallujah may only reflect general deterioration in birth
outcomes and child health in Iraq. The Iraqi child and maternal mortality survey [3] covered 46,956 births in Iraq from 1994-1999. Results were obtained by questionnaires filled out by the mothers and results
were given for all children aged 0-4 who died in 1994-1999. Effects found in this period, if due to environmental agents,
would, of course, follow exposures in and following the first Gulf War, GW1. Using data presented in the tables in this publication
it is easy to show that the results indicated a marked increase in deaths in the first year of life with an infant mortality
(0-1) rate of 93 per 1000 live births. 56% of deaths in all the children aged 0-5 occurred in the first month after birth
but since the results were from self reporting, it was difficult to draw conclusions as to the underlying causes of death
except in the case of oncology/haematology. For example, the largest reported proportion of deaths in the neonates were listed
as "cough/difficulty breathing" which might result from many different underlying causes. The low rates from congenital malformation
reported are hardly credible (Table 1). However, using data published in the report [3] it appeared that the cancer and leukemia death rates in the entire all-Iraq 0-4 group were about three or four times the
levels found in western populations for this age group (Table 1). These rates were three times higher in the South where Depleted Uranium (DU) was employed in the major tank battles near
the Kuwait border (53 per 100,000 per year) than in the North (18 per 100,000 per year) where there was less fighting and
where DU was not employed to such an extent [4]. Furthermore, cancer and leukemia rates were highest in the 0-1 year group, which is unusual; the main peak in childhood
cancer is generally found at age 4.
Table 1. Data on child mortality, congenital anomaly and oncology/haematology as causes of death reported by mothers in the Iraqi Child
and Maternal Mortality Survey 1994-1999 [3]
As far as Fallujah is concerned, we have ourselves made a study [Alaani S.; Busby C; Hamdan M; Al-Fallouji M: Infant mortality, sex ratio, congenital anomaly and environmental contamination in Fallujah, Iraq, submitted] of the levels of different types of congenital anomalies diagnosed by one pediatrician in an 11 month period
in the Fallujah General Hospital. Results, confirm the existence of high rates of congenital anomaly in this birth cohort.
Anomalous health effects of Uranium weapons
Since the use of Depleted Uranium in GW1, there has been a research focus on contamination by this material as a potential
cause of increases in congenital anomaly (CA) and cancer rates [5]. When Depleted Uranium weapons are employed, sub-micron aerosolized particles of ceramic Uranium oxides are created [6,7]. These are respirable and the inhalation of Uranium involves a 200-fold increased radiation dose conversion coefficient (the
committed effective radiation dose per unit intake) compared with ingested Uranium. This is due to the long biological half
life of internal Uranium and the very low gut transfer factor for ingested Uranium [6-8]. Of course, the troops were also exposed to DU aerosols. A number of studies of the GW 1 veterans have shown statistically
significantly increased rates of congenital malformation in their children [9-11]. For example, Doyle et al. [9] reported rates of congenital malformations in a group of 13,191 offspring of male and 360 offspring of female UK Gulf war
veterans, finding relative risks of 1.5 (95% CI 1.3-1.7) for all CA's. Araneta et al. [10] reported significant excess congenital heart defect and hypospadia rates in 11,961 US Gulf war veteran live-born offspring
compared with military controls. Relative risks were between 2.7 (1.1-6.6) for tricuspid valve insufficiency and 6.0 (1.2-31.0)
for aortic valve stenosis. Kang et al. [11] compared 3371 US Gulf War veteran offspring with 3625 non Gulf War veterans and reported higher prevalence of moderate to
severe birth defects RR1.78 (1.19-2.66) with father as veteran and RR 2.8 (1.26-6.25) with mothers as veterans. Other studies
have found similar results but there have also been studies which do not find any increased risks although many of these latter
studies suffer from problems with small numbers [9]. An interesting and relevant study is that of significant excess rates of cancer and congenital birth anomalies in the Quirra
polygon in Sicily where NATO is believed by the authors of the study to test Uranium weapons [12]. Nevertheless, besides DU, there may also be a number of other potential causes for any increased risks of congenital anomaly
in Fallujah or in Southern Iraq. Modern warfare involves the deployment of novel weapons systems which create contamination
of the environment and the local inhabitants of the war zones by a range of heavy metals and other substances. For example,
analysis of wound tissue of war injuries produced in Gaza in 2009 revealed traces of elements which have been argued by the
authors to be associated with carcinogenicity and fetotoxicity, including As, Cd, Sn, Pb, Hg, U, Cr, Ni, Co and V [13]. To investigate this issue we examine the concentrations and isotopic ratios U238/U235 of Uranium and other elements in the
hair of the parents of the CA children. To provide information about environmental levels of Uranium we also measured the
Uranium content and U-238/U235 isotopic ratio of surface soil samples and content of tap water, well water and water from
the River Euphrates which flows though the city.
It is not our intention here to exhaustively discuss the arguments relating to the genotoxicity and fetotoxicity of Uranium;
these have been rehearsed at some length in the literature. However, since Uranium is the only known radioactive heavy metal
exposure in Iraq, it must be considered to be a major suspect for the cause of the effects found in Fallujah and also in the
rest of Iraq. Such a suspicion is also supported by other evidence of birth defects in Gulf War Veterans and increasingly
from studies of the genotoxicity of Uranium in cell and animal studies. Induction of genetic and genomic damage by ionizing
radiation has been recognized since the early work of Muller on the genetic effects of X-rays on Drosophila [14,15]. Increased levels of genetic and genomic based conditions have been reported in those exposed to internal contamination from
fallout from the Chernobyl accident [16-19]. It should be noted that the radiation doses in these Chernobyl affected territories were not considered high [20] and were generally less than natural background. However the concept of absorbed dose itself may not be valid for the internal
exposures from the Chernobyl fallout [21-23]. Indeed, significant effects of the Chernobyl fallout were reported for infant leukemia rates in those children who were
in utero during the fallout period reported by 5 different research groups for Greece, Germany, Scotland, Wales and Belarus; taken
together and because the absorbed doses were so low, these raise questions about the application of the concept of dose used
for risks from external exposures in the A-Bomb lifespan studies for internal substances like Strontium-90 and Uranium which
have high affinity for DNA [24,25]. For example, the fetotoxic effects of internal exposures to Strontium-90, a radionuclide that binds to DNA, were investigated
in the period of atmospheric testing [26]. In mice, Sr-90 exposure of fathers caused high rates of fetal death whereas the same dose from the radionuclide Cs-137 which
does not bind to DNA produced no effect. Uranium, as its molecular species in tissue, the UO2++ ion, also binds strongly to DNA having an affinity constant of 1010 M-1 [27] a fact which has been known since the 1960s when it was first used as an electron microscope stain for chromosomes [28]. For this and a number of other reasons Uranium may be considered theoretically to show enhanced levels of genomic damage
relative to that which its absorbed dose might predict [29]. Such anomalous genomic damage has, indeed been found at low concentrations in cell cultures [30-32] rodents [33,34] in Uranium miners [35] and Gulf War veterans [36]. Given this evidence for the genomic effects of Uranium, since the respirable aerosol form of DU is far more effective in
becoming internalized and the particles may remain in the body for more than 10 years [6] it is not surprising that there is considerable evidence emerging that the effects of exposure to DU, or aerosolized Uranium
weapons involve a wide range of adverse human health conditions [37,38].
These considerations provide a general background for our examination of Uranium levels in the mothers and fathers of the
children with CA in Fallujah. In order to attempt to characterize the source of any Uranium we also determined the U238/U235
isotopic ratio which for natural Uranium is always exactly 137.88. Pure Depleted Uranium in anti-tank ammunition may be considered
to have an isotopic ratio of over 400 but mixtures with natural environmental Uranium will of course show lower ratios [6,38].
Hair analysis
With advances in technology in the last 10 years, analysis of hair contamination has become a valuable tool in assessing environmental
exposures, particularly for Uranium [39-43]. We determined Uranium and other elements the hair of mothers and fathers of children who had been born with major congenital
anomalies.
In principle, contamination in hair represents excretion into the hair strand at the time of exposure; thus it might be expected
that analysing hair along the lock from scalp to distal end, might reveal information about changes in exposure with time.
It is of value in this regard that the Moslem women in the group all had long hair, 30-80 cms in length. Since hair grows
on average, 1 cm per month, this means that the distal end of the hair of an 80 cm lock taken in February 2011 began growing
in 2005. For this reason and also to investigate the accuracy of the initial determinations we obtained a second sample of
hair about 9 months after the initial sample from a group of women whose analysis had shown the presence of Uranium in the
first analysis. In this second investigation, we divided the hair locks into 12-14 cm sections, each of which was separately
analysed from its mid point.
Subjects and methods
Hair analysis; initial study
Parents of children born in 2009-2010 with major congenital anomalies in Fallujah General Hospital volunteered to take part
in the study. Mothers and fathers separately gave hair samples in May 2010 and also completed a questionnaire. Details from
the questionnaire were filed with the clinical details of the child's congenital anomaly. In two cases, hair from the child
was also obtained. We obtained the clinical details of the congenital anomaly, the age of the parents, their smoking history
and alcohol drinking history and where they had lived. All of the parents were from Fallujah and had been present at the time
of and after the attacks in 2004. Hair was cut from the nape of the neck with stainless steel scissors and placed in a sealed
polythene bag. The centre of the first 15 cm of the scalp end of the lock was employed in the case of the mother. Fathers'
hair as received was generally very short, less than 2 cm. There were 25 samples from parents and two samples from children.
In all cases, samples were physically brought to the UK where they were opened in the laboratory, the samples divided in two
longitudinally and one half placed in a second polythene bag and re-coded. The re-coded half-sample was then posted to Germany
for analysis. There, samples were removed from the plastic bags, washed well with a de-ionized aqueous detergent solution
(Triton X-100) and dried before cutting and weighing. In the initial study, for about half the cases, and where there were
only small quantities of sample, mother and fathers hair were mixed together. This was because the quantity of hair available
from some of the fathers was very small and because it was believed it would give gave a more representative value for the
population with fewer determinations. Each determination was based on about 100 mg of hair precisely weighed. Samples were
dissolved in 3.0 ml A/R Nitric acid containing 10% of 30% hydrogen peroxide solution by microwave digestion at 80 degrees
for 1 hour to give a clear solution. The solutions were diluted to 10 ml with ultra-pure water and examined by Inductively
Coupled Plasma Mass Spectrometry ICPMS (Agilent 7700 with Octupole Reaction System).
Hair analysis; long hair study
In the case of the long hair study, samples were obtained in February 2011 from 4 women whose hair had already been analysed
in the first study plus two other women (not with children with birth defects) who lived in Fallujah and who volunteered to
take part. The hair was divided longitudinally and cut into equal sections of 13 to 15 cm (depending upon the initial length)
and labeled from the scalp end. The re-coded half-sample was then posted to Germany for analysis using the same procedure
already outlined.
Drinking and local water samples
Tap water, well water and water from the river Euphrates in the city were also analysed in Germany by ICPMS after treatment
with nitric acid/hydrogen peroxide and filtration.
Soil analysis
For soil samples, the analysis was carried out by the Harwell Scientifics Laboratory in Oxford, UK. Six samples of surface
soil from the top 1 cm were obtained from various representative areas in that part of Fallujah where there had been bombardment
and fighting in 2004. Gamma dose rates at each site were checked at 30 cm from the ground with a calibrated Russian SOSNA
twin chamber Geiger Counter which has a thin window and responds to beta and gamma radiation. Initially, three separate aliquots
of each sample were digested in concentrated nitric and hydrofluoric acids in fluoropolymer vessels by microwave. Following
digestion, samples were made to a known volume of demineralised water having resistivity of 18.2 MOhm cm. All samples were
analysed for total Uranium and Uranium isotopes at the same laboratories using Inductively Coupled Plasma Mass Spectrometry
ICPMS (Perkin Elmer Agilent 7500CE) on the above nitric acid/hydrofluoric acid digestions. Calibration was achieved using
standard addition of a certified Uranium standard and instrumental drift was corrected with a Bismuth spike. Quality Control
standards at 5.0, 10 and 20 micrograms per litre were prepared from an alternative stock source solution to that used to prepare
the calibration standard. Three independent preparations were made from each sample and each was run three times on the system.
After obtaining initial concentration data, the U-238/U-235 isotope ratio was obtained in a separate determination where an
acid dissolution of a larger quantity of material was passed onto an ion exchange column to separate and concentrate Uranium
from the matrix. Approximately 3 g of sample was ashed overnight at 450 C, and the residue digested in concentrated nitric
and hydrofluoric acids. After co-precipitation of the Uranium with iron hydroxide, ion-exchange chromatography (Eichrom 1
× 8 100-200 mesh) was used to further purify and separate the Uranium. This Uranium extract (which had about 50 times the
Uranium channel counts than the initial sample was then further analysed for Uranium isotope U238/U235 ratios.
Results
Initial hair study
Results were obtained for all the elements listed in Table 2. The listed range of normal background values (95% CI) for the comparison levels in hair were obtained from an unpublished
database created through studies carried out by the present laboratory on 1000 healthy subjects living in Germany and the
USA. Also shown are the limits of detection of the element at these laboratories. In addition for further comparison are shown
means and ranges taken from Rodushkin and Axelsson [43] which are slightly different for some elements. The mean ages of the fathers was 29.6 (SD 6.2) and the mothers 27.3 (SD 6.8).
Only 5 fathers and 3 mothers in were over the age of 30 and only two parents (a father and mother) over 40. None of the parents
(all of whom are Moslems) reported drinking alcohol. Four fathers and none of the mothers were smokers. These individuals
did not show higher than average amounts of Uranium than the non smokers. In Table 3 are shown results for individual parents for elements of interest which are found at levels which are higher than the normal
range, together with details of the child anomaly. Mean levels for Uranium were 0.16 ppm (SD: 0.11) range 0.02 to 0.4, higher
in mothers (0.18 ppm SD 0.09) than fathers (0.11 ppm; SD 0.13). It was also of interest to examine the variation in concentration
of these elements between the mothers and fathers. Table 4 gives details of some comparisons of mothers and fathers of the same children.
Table 2. Limits of Detection (LOD) Mean and Standard Deviations of concentrations mg/kg of elements measured in the cohort of 26 parents
of children from Fallujah with congenital anomalies
Table 3. Individual cases with concentrations of selected elements of interest, Calcium, Strontium, Bismuth, Mercury and Uranium
Table 4. Comparisons of pairs of mothers (M) and fathers (F) of the same children for concentrations of selected contaminants in hair
Long hair study
To further investigate the idea that historic exposure changes may be looked for along the length of hair, data for 4 women
with long hair from the original group and two new women are given in Table 5. The results for Uranium in the scalp end of the lock for the women whose hair was taken in May 2010 and measured in the
first set of tests agree well with the results obtained in the second set of measurements on hair taken 9 months later in
February 2011. Figure 1 shows the variation in Uranium concentration along the length of the hair of the different individuals plotted against the
mean period of the hair growth. In Figure 2 for comparison is the normalized concentration of Uranium along the length of locks of hair reported in a study of children
living in Northern Sweden [42].
Table 5. Uranium levels ppm (mg/kg) in samples of hair taken in Feb 2011 along the length of the lock of women with CA children tested
in the first study and two women volunteers N1 (with very long hair) and N2
Figure 1. Uranium (mg/kg, ppm) along the length of the hair locks of individuals in the long hair study (data from Table 4).
Figure 2. Reduction of Uranium concentration along the hair lock for Swedish cases reported by Rodushkin and Axelsson[46].
Soil and water
Concentrations of Uranium in soil and water samples are given in Table 6. Soil samples show low concentrations with a mean of 0.76 ppm (9.4 Bqkg-1) SD 0.42 ppm and range 0.1-1.5 ppm; (N = 18). Levels in tap water were 2.28 μgL-1, water from a well was 2.72 μgL-1 and from the river Euphrates as it flows though the town by the bridge 2.24 μgL-1.
Table 6. Literature data and this study on Uranium concentrations in hair of occupationally unexposed persons
Discussion
Elements found in excess in the hair
The results show that the parents of the children from Fallujah diagnosed with major congenital defects have significant excess
concentrations of a range of elements. The following elements were present in concentrations that were more than two standard
deviations from the mean levels in an uncontaminated Swedish population: Ca, Mg, Co. Fe, Mn, V, Zn, Sr, Al, Ba, Bi, Ga, Pb,
Hg, Pd and U (for women only). Some of these were present in very high excess relative to both the laboratory control ranges
and also the Swedish controls: Ca, Mg, Sr, Al, Bi and Hg. In examining the data we have chosen to focus on Calcium, Strontium,
Bismuth, Mercury and Uranium, the first three since they are unusual and might be associated with earlier environmental exposures,
and the latter as it is a known cause of damage to the developing foetus. Methyl Mercury has been associated with congenital
neurological disease in Japan, but the types of congenital anomaly concern brain development and learning difficulty and do
not match those found in Fallujah, which are dominated by heart and circulatory system and neural tube defects [44]. Matrix analysis for cross correlations between all these elements in the cohort do not reveal any significant relationships
between them. However there is one interesting finding. The concentrations of these elements in the fathers are generally
significantly lower than the concentration in the mothers. For the specific case of Uranium, the statistical boxplot is given
in Figure 1 of the concentrations in mothers, fathers and the mixed samples of hair. The difference between mothers and fathers is significant
at the p < 0.05 level.
The increased levels of contamination in the mothers relative to the fathers is generally quite marked for all of the excess
contaminants examined, as can be seen in Table 4. This dependence of elemental concentration on sex was found for a wide range of elements by Rodusshkin and Axelsson [42,43] who found that women had roughly twice the levels of all the elements studied here than men and this included Uranium.
However, Gonnen et al [45] measured Uranium in a group of individuals living in southern Israel and found no significant difference in Uranium levels
in hair between men and women. The relatively low levels of Uranium found in the two children we studied might be expected
on the basis of measurements made on aborted fetuses which showed that they had 10% of the Uranium content of their mothers
[44]
Uranium in the hair: the initial study
In attempting to identify the cause of the cancer and congenital disease in Fallujah we cannot believe that the elements found
in excess and listed above could, under normal conditions of exposure, be the cause of such a remarkable level of disease,
since none of them, including Uranium, are present at levels which exceed the various environmental limits placed on contamination
by government regulations in the USA or Europe. As far as Uranium is concerned, there are many parts of the world where Uranium
levels in drinking water and human hair exceed those found by us in this study and levels of congenital disease and cancer
in such areas are not markedly increased; as an example we may contrast the 38-fold excess leukaemia rates found in the questionnaire
study [1] with the study of Auvinen et al of leukaemia in Finland in those drinking well water high levels of Uranium [46]. The mean level of Uranium water in the leukaemia cases in Finland was 7 μgL-1 and that of the controls was 5 μgL-1. However, this approach begs a number of questions. The arguments relating to the health effects of Uranium from weapons
use have been predicated on a different type of Uranium exposure which seems to be inhalation of nanoparticle ceramic oxides.
Below about 1 micrometer diameter these will be translocated to the lymphatic system where part of it may remain for more
than ten years [6,7]. The excretion into urine (or hair) from the bloodstream of Uranium derived from this source is likely to be very slow [6,7,38]. The ionisation damage close to such a particle is likely to significantly higher than would be calculated on the basis of
the molecular concentration in tissue, and the local molecular concentration of the UO2++ ion, the solubilised form of Uranium in the body, very high. A similar argument has been made by Zuchetti in relation to excess
cancer and congenital anomalies found near the Quirra range in Sardinia where DU weapons are believed to be tested [12]. This would drive an equilibrium concentration of Uranium bound on the DNA which would locally be very high. In addition,
it has been argued, and indeed established, that Uranium amplifies the natural background gamma radiation owing to its high
atomic number, though there is a question about the level of local radiation dose enhancement this produces [29,47-50]. Furthermore the predicted photoelectron enhancements [29] from this molecular source have not been addressed or measured although theoretically it can be predicted that they may be
significant [49,50].
In looking to see whether the levels of Uranium in the hair of the mothers and father of the children with congenital disease
could indicate a cause of the health problems in Fallujah there are three questions that must be asked. First, do these levels
seem to be higher than control populations living in uncontaminated areas of the world? Second, are these levels representative
of an unchanging natural background exposure though drinking water containing natural Uranium which is a result of high natural
levels of environmental Uranium? Third, are the Uranium isotope ratios indicative of a natural Uranium source? We will attempt
to address all three of these questions in turn.
Are the levels of Uranium in hair in Fallujah too high?
There are a number of literature sources for Uranium in hair listed in Table 7. If we omit the Finland data (which was from an area with high natural Uranium) the mean level of the other 5 studies is
0.04 ppm with a standard deviation of 0.023. The mean level in our initial study was 0.16 ppm and so this is almost five standard
deviations from this mean and for a normally distributed population this would highly significant. The highest levels in Table
7 apart from the Finland sample are from an apparently uncontaminated control population studied by Gonnen et al. who measured
Uranium in a population of 99 individuals living in Southern Israel, in the Negev Desert in 1999 [45]. The mean and median values were found to be 0.062 and 0.05 ppm respectively and results showed that those younger than age
45 had significantly lower values than those who were older. Comparing means in a non parametric distribution may not be correct
way of comparing two groups. Because we have the distribution and the Israeli study distribution is given [45] we compared the Fallujah distribution results with those reported in the Israeli study. The histogram distributions for Fallujah
and the Israeli cases younger than age 45 (which should be strictly comparable with the parents of the Fallujah children who
were all younger than 45) are shown in Figure 4. Since these are clearly not normal distributions we employed the Mann-Whitney U-Wilcoxon non-parametric statistical test
to determine whether the concentration of Uranium in the Fallujah parents were significantly higher than those in the Israeli
control group. The results show a significant (2-tailed) excess in the Fallujah cohort p = 0.016.
Table 7. Uranium concentrations, beta gamma dose rate at 30 cm (μGyh-1) and activity ratios (where measured) in surface soil river sediment and water samples (μgL-1) from Fallujah, Iraq
Are the levels in hair a consequence of a locally high level of Uranium?
To examine this we measured Uranium in water samples from a well, from the river Euphrates and from tap water. The results
in Table 6 show that there was 2.3 μg L-1 total Uranium in the tap water and much the same level in both water from a local well and from the River Euphrates where
it flowed through the town. It is generally accepted that the main source of Uranium in humans is from drinking water [45]. A compartmental biokinetic model of Uranium in human hair has been developed by Li et al. [51] and these authors show a correlation between Uranium intake in water and concentrations in hair for intakes greater than
10 μg per day. There is a very wide degree of scatter in the data at the low end with results falling between 0.2 and 1.0
ppm in the hair. However no data is given for intakes below 10 μg per day. Nevertheless since we have compared the Fallujah
group with the Israeli group of Gonnen et al we may also note that these authors also measured Uranium in the drinking water.
They reported that the Uranium in drinking water varied between 0.7 and 5 μg L-1 [45]. It is therefore rather curious that at these levels the hair concentrations should be lower than the level in the Fallujah
group but we cannot make too much of this since the standard deviations of the Uranium in drinking water in the Gonnen et
al study were not given. Levels of total Uranium in the soil were measured and these were also not high in terms of natural
background levels of Uranium in the world environment (Table 6). Levels in soil were generally less than 1 ppm (12 Bqkg-1) in Fallujah compared with average global soil levels of 1.8 ppm (22 Bqkg-1) [52]. Therefore the soil levels do not explain the total Uranium levels in the group. However there is a final question which
is asked: is the Uranium natural?
The Uranium isotope ratios
The use of DU weapons as anti-tank penetrators in Gulf War 1 led to attempts to track its use by means of measuring Uranium
isotope ratios. One of us (CB) was involved with the UK Ministry of Defence in developing a urine test to study the levels
of DU in veterans [38]. The rapid advances in technology which occurred in the late 1990s led to the development of ICPMS for detecting DU on the
basis of its characteristic isotopic ratio signature and these machines became increasingly able to detect DU isotope signatures
in urine tests. The natural atom ratio of U238/U235 is 137.88. Pure DU has a signature greater than 400 [6] but for the purposes of the urine test developed with the instruments in use at the time (2003) any ratio above 142 was considered
to originate from a DU contamination [38]. If DU had been used in Fallujah, therefore, it might be expected that some deviation from the natural signature of 137.88
would be found if we looked. Measurements made on the soil samples quickly showed that although the total Uranium levels could
be accurately determined, because of interference from other elements taken up in the acid dissolution of the sample, the
concentrations of U235 needed to accurately define the isotope ratio were too low. Accordingly, an ion exchange extraction
technique was developed, and results of these measurements showed clearly that the Uranium in the soil was not natural. It
was not, however, depleted Uranium. It was, in fact, slightly enriched, with ratios varying from 118 to 132. Under the conditions
of the extraction we are able to assess the 95% CI limits from the count variance found in relation to the total counts. We
are able to say that for defining natural Uranium the Ratios must fall in the range 132.1 < Ratio < 144.1. Values below 132.1
are thus enriched, above 144.1 depleted with p < 0.05.
In the case of the hair samples for those samples with more than 0.1 ppm we were able to determine this ratio directly since
the solutions had less interference and the instrument employed (octupole reaction cell) had a greater intrinsic sensitivity.
At low Uranium levels, where overall U-235 concentrations become uncertain, it is technically possible to ignore overall accuracy
in concentration and obtain isotopic ratios directly by dividing out the counts per second per channel. ICPMS counts atoms
according to their mass, so the ratio of counts in the U238 channel to the U235 channel gives the isotope ratio without any
assumptions about concentration. Ultimately this method fails at very low concentrations where the counts drop towards a zero
concentration point of electronic amplifier background noise. This noise is a higher proportion of the U-235 channel counts
than the U-238 channel counts since the latter are 137.88 times greater in natural Uranium. Thus any material will begin to
appear enriched as the concentration falls towards the limit of detection. But as the concentration increases above this the
measurements will converge towards the accurate value. Figure 5 shows the isotopic ratio U238/U235 plotted against total counts for U238. If we employ the data based on counts in the U235
channel of above 1000 counts the result (n = 14) is an isotope ratio of 135.16 with a standard deviation of 1.45. Since this
is 2 standard deviations away from the natural Uranium value of 137.88, this results shows that the Uranium in the parents
is slightly enriched. If the single outlier at 138.89 is removed the mean falls to 134.9 with a standard deviation of 1.02
which suggests that the outlier is just that. The SD is now almost 4 standard deviations away from the mean and the data is
very tightly defined. This discovery of enriched Uranium in the hair might be expected since the soil sample data also shows
traces of enriched Uranium. Note that the limit of detection for the instrument is conventionally placed at 1000 counts and
that 4000 counts represents a concentration of approximately 0.003 ppm.
Long hair study
If the higher levels of Uranium in the mothers relative to the fathers reflects increases in historic exposures then we may
expect, under simplistic assumptions, to find an increasing trend in concentration in samples of hair taken from the proximal
(scalp) to the distal end of the mothers. But the concentration of Uranium along locks of hair from the scalp to the distal
end was investigated by Rodushkin and Axelsson [42,43]. These authors showed that for Uranium the concentration falls rapidly and regularly by distance from the scalp, presumably
as a result of washing the hair. The trend was found to be such that 20 cm from the scalp the concentration was about half
that at the scalp and at 37-39 cm from the scalp the concentration was about 15% of its initial value (Figure 2). In our study of the long locks of hair from 6 women from Fallujah we see clearly that the Uranium content does not fall
along the hair as would be predicted by the findings of Rodushkin and Axelsson [42,43]. Figures 2 and 3 show this clearly. In the results of the 6 women we find individual variations in trends: four women have increasing levels
of Uranium along the lock to the distal end, whilst two have falling levels. But even in the woman where the level falls most
rapidly, the reduction over a period of 40 months (40 cm) is modest, perhaps to about 50% of the initial value. The results
from Sweden suggest that the expected fall over this period should be 90% to a value about one tenth the original. Taken as
a whole, including the women where the trend is upwards or level we have to conclude that the Uranium exposure 40 months before
we took the samples was conservatively about five to ten times what is indicated now. Thus if we assume that (because of hair
washing) the Uranium is lost from the women in Fallujah at the same rate as it is lost from the individuals in Sweden examined
by Rodushkin and Axelsson [52] then 40 months before February 2011 (i.e. in Summer 2007) the levels would have been about 2.6 ppm rather than the 0.26 ppm
measured in February 2011. And we looked for a woman with very long hair to investigate this historic exposure. This woman,
NM1 has hair which is more than 80 cms long. It is clear that the trend in Uranium in her hair is fairly uniform, or maybe
even rises. It is clear that the Uranium level in her hair at 40 cm indicates that if it had been measured in June 2007 it
would have contained over 4 ppm of Uranium. We must assume that the loss of Uranium (through washing) is related to the number
of washes, and so in this case, where the hair takes us back to 2005 (Table 4) the levels in the hair at that time must have been very high indeed.
Figure 3. Box plot of Ranges of Uranium concentrations in (1) Fathers (2) Mothers and (3) Mixed hair from both.
Figure 4. Frequency histograms of Uranium concentration in two populations. (1) Israeli control group (13) and (2) Fallujah congenital anomaly parents.
Figure 5. Uranium isotope ratio plotted against the counts per channel for U235. for all the parents in the study. Note effect of low counts and convergence of ratio R. for all points greater than 1000
cps towards a value of R = 135.16; SD 1.45 (n = 14). dotted line shows natural ratio of 137.9.
Thus we can provisionally conclude that the levels of Uranium in the hair of the parents of the congenital anomaly children
are higher than could be easily explained by the environmental levels but more important the Uranium in the hair, the drinking
water and in the environment has a component which is man-made and is enriched in the isotope U-235.
Weaponised Uranium as a cause of the health effects in Fallujah
The use of passive DU munitions in Iraq (and also in the Balkans) has been admitted by the USA and UK forces and recent research,
as outlined above, has suggested that Uranium may demonstrate anomalously high genotoxicity [53]. We have found high genotoxicity in this population: high cancer levels and high congenital anomaly levels. High childhood
cancer levels in 1994-98 were also found in southern Iraq, where the main exposures to DU occurred in 1991. Significant excesses
of congenital anomalies have been reported in the offspring of the Gulf veterans. However, DU has not been found. What we
have found is slightly enriched Uranium (EU). We have found this in hair and in soil samples, using different instruments
in different laboratories and employing different methods. We suggest that the levels in the hair seem to be high for the
levels in the drinking water to be the sole source. In addition, we have found from the long hair study that the excretion
into hair was much higher in the past than it is now. From the calculations made by the Royal Society [6,7] and the analyses of the UK DUOB [38] it would seem that the most likely explanation is that these excretions were the consequence of the slow dissolution and
excretion of Uranium from some depot in the human body following an initial acute exposure. There remain two questions. Why
use Uranium weapons in Fallujah? Why use enriched Uranium?
The military have been clear that although they used 350 tonnes in Gulf War 1, they did not employ Depleted Uranium weapons
to any extent in Gulf War 2. That is they did not use DU. And indeed, no DU was found in the urine of GW2 veterans; one of us (CB) obtained the data from the 400 or so UK troops
and although the urine Uranium levels were significantly high, the isotopic ratios showed them not to contain DU [38]. If anything, the distribution was rather broad and suggested that the ratios might contain some degree of enrichment. So
one suggestion that may occur is that the use of EU or natural Uranium in weapons, although costly, enables the military to
employ Uranium weapons and avoid subsequent detection [53]. They can truthfully say that they did not use DU.
But what of the second question? Uranium weapons are passive anti-armour weapons. Why would they be employed in house to house
fighting against insurgents?
To examine this issue we turn to accounts of the Battle of Fallujah and the weapons used.
The Battle of Fallujah
In 2004 Fallujah experienced two major military operations. The first siege and battle of Fallujah - Operation Vigilant Resolve - ran from 4th April to 10th May after the death of four US contractors. US forces attempted to control the city with ground operations and air support
bombing but had to withdraw. The second siege and battle of Fallujah - Operation Phantom Fury - ran from 7th November to 23rdDecember. US and Iraqi forces were involved in the most intense urban combat operations in Iraq since April 2003.
US Marines carried out ground operations with support from armoured vehicles, mortars, tanks and artillery. Air support was
provided from Cobra and Apache helicopters, AV-8B Harriers, F-16 and F-18 fighter-bombers, AC130s and UAVs [54]. A wide range of guided weapons were used to destroy suspected insurgent targets before infantry troops entered strongly
defended buildings.
CAS (Close Air Support) weapons included AGM-114 Hellfire, AGM-65 Maverick and TOW missiles. These mainly use shaped charge
warheads believed to contain Uranium shaped charge liners (concept identified in US Patent 4441428 [55,56]. CAS operations in Fallujah also used 500lb GBU-12, 38 and possibly larger hard target guided bombs e.g. GBU-24 for hard
targets and suspected bunkers. The advanced penetrator warhead versions of these (BLU-110, 111) use high-density metal ballast
- either tungsten or Uranium [54,55,57]. Undepleted or low enriched Uranium contamination has been found in samples from heavily bombed locations in Afghanistan,
Iraq and Lebanon [53,56,58].
US forces also used Fallujah to combat-test prototypes of at least two new types of thermobaric weapons - Thermobaric Hellfire
missiles - AGM-114N