| SLIDES
& TRANSCRIPTS
Friday,
December 05, 2003
Bladder
Cancer
Lee Moore, M.D.
|
| Slide
1: |
Hello. I am
going to talk today and change a little bit from just straightforward
epidemiology to talk about molecular epidemiology of bladder cancer
and focus on some research that we recently conducted on two known
bladder carcinogens, arsenic exposure, environmental arsenic exposure
and tobacco
TOP
|
| Slide
2: |
| and
the type of study designs that were used for this research is the
case-case study design using tumor tissue.
We use micro-dissected
tumor tissue and they are very useful for etiologic studies when animal
models are not appropriate and this is particularly the case with
arsenic exposure because in arsenic exposure inorganic arsenic is
not a known carcinogen in rats or mice but in humans it is carcinogenic
at several sites, and they can also be used to determine if the genetic
alterations observed are different, in this case the arsenic exposed
group or tobacco-exposed group than unexposed cases thus strengthening
the causal inference
TOP |
| Slide
3: |
| and
the study I am going to talk about is these cases from an Argentine
population-based study which was conducted in a region of Argentina
where people had drinking water arsenic concentrations between 0
and 300 micrograms per liter and the second region of Chile in the
region of Antofagasta where people were historically exposed for
about 30 years to very high levels, very high concentrations. So,
the arsenic exposure in these cases, the Chileans were all over
600 micrograms per liter and the Argentine group was between 50
and 300 for the exposed and then I had unexposed cases from each
population that were exposed throughout their lifetime to less than
10 micrograms per liter, and just for those of you who aren't into
public health the current maximum contaminant level now is 50 and
it was recently lowered to 10 micrograms per liter.
So, these are very
highly exposed people TOP |
| Slide
4: |
| and
in the study I used two bladder tumor markers.
The first method was called comparative genomic hybridization which
is a method of looking at the entire genome, gross chromosomal changes,
gains and losses as well as amplifications and also p53 mutational
spectrum analysis to look at one particular gene and look for mutational
patterns within a gene and determine if those correlate with exposure.
TOP |
| Slide
5: |
|
So, just to explain to you how comparative genomic hybridization
works we extract DNA from tumor tissue and also normal tissue and
you label the tumor tissue in this case with green, add normal tissue
with red and then you co-hybridize the two DNA samples together
and areas where you see more tumor DNA you see a green-to-red ratio
of greater than one. If they are the same the ratio is one. In the
area where there is a loss, where there is a deletion in the tumor
you see a ratio of less than one,
TOP |
| Slide
6: |
| and
this is just a picture of what it looks like and you use a digital
camera to take pictures of your images and also to measure the amount
of fluorescence which is emitted by either the green or red probes.
TOP |
| Slide
7: |
|
So, this is the clinical variables for all bladder cancer patients
but the groups are very similar except for gender. There were more
females in the Chilean group
TOP |
| Slide
8: |
| and
when we looked at stage and grade there were increases of CGH alterations
with both stage and grade suggesting that there are more alterations
with disease progression which is pretty well known and this has
already been published, but with smoking we didn't see any type
of difference in the number of CGH alterations.
TOP |
| Slide
9: |
| But
when you look at arsenic exposure category we saw a positive trend
with maximum 5-year peak arsenic concentration in drinking water
and this is the number of CGH alterations per tumor.
TOP |
| Slide
10: |
|
Then when we stratified the group by high-grade tumors versus low-grade
tumors and there was virtually no trend in the low-grade tumors,
but then in the high-grade tumors that is where we saw all of the
association and what was very interesting is that even some of the
tumors that were TA tumors which normally are superficial tumors
and have between zero and two changes per case we had some with
almost 27 alterations, and this is almost unheard of in non-arsenic
exposed countries,
TOP |
| Slide
11: |
|
and we also looked at particular chromosome alterations, gains that
were associated with smoking history and arsenic exposure and you
can see that there were particular gains here at 8q. I think that
is cycline D1. A lot of the alterations correlated with grade and
stage
TOP |
| Slide
12: |
| and
with arsenic exposure the most strongly correlated loss was this
loss of 17p.
So, we decided
to look at the p53 gene and see if there was any type of a mutational
pattern that was associated with exposure. TOP |
| Slide
13: |
| So,
just in conclusion patients with higher arsenic exposure showed
higher levels of chromosomal instability with the exposure and that
most arsenic associated changes were also associated with stage
and grade and this could suggest that people who are exposed to
arsenic may have more tumors that may behave more aggressively and
perhaps that may explain some of the higher mortality that is seen
in countries with arsenic exposure, and the strongest association
was seen in the chromosome arm 17p.
TOP |
| Slide
14: |
|
So, next we looked
at the p53 gene and the p53 gene is a good candidate for looking
at mutational spectrum. It is mutated in between 30 and 50 percent
of bladder cancers and some suggest that in cancer in general that
the pathway is altered in about 90 percent of cancers and most of
the mutations are observed at CPG sites.
These are the
three hot spots in cancer in general. These are CPG sites. They
have lots of C's and G's but the cytosines that are heavily methylated
are the site of what is considered mostly endogenous mutations,
C to T mutations caused by deamination of cytosine and where environmental
carcinogens tend to form bulky adducts is at the guanine next to
the methylated cytosine. Nobody knows why but what happens is that
during the DNA repair sometimes there are errors because there is
this big bulky adduct sitting on the guanine.
So, in lung cancer
for example, PAH exposure which causes adducts causes primarily D
to T mutations and in other types of cancer like bladder you see more
G to A transitions, TOP |
| Slide
15: |
|
and this just shows you that in smokers we found an elevated hot
spot at codon 273 which was found only in smokers
TOP |
| Slide
16: |
|
and when we looked at the number of transitions which could be considered,
well, looking at smoking there is basically, well, with grade there
was an increase in the number of transitions and that is a G to
A transition. That was also seen with pack years and possibly difference
with smoking but when we looked at these G to A mutations at CPG
sites they were not found associated with grade, using that as a
mark, or stage using that as a marker of progression but they were
observed with the exposure and similarly this codon 273 mutation
was observed only in smokers but was not observed with grade suggesting
that this type of mutation is not caused by progression of disease
but may be an early marker of exposure to tobacco.
TOP |
|
Slide 17: |
| So,
in conclusion the prevalence of p53 mutations increased with stage,
grade and smoking and primarily there is a preference for G to A
mutations at CPG sites. This finding was recently corroborated by
a study with Jack Taylor's group at NIEHS and arsenic exposure,
I didn't show you that data but it was not associated with any p53
mutations.
TOP |
| Slide
18: |
| So,
what I have been doing in this research is combining markers, gross
markers like CGH changes and p53 mutations and looking at those
that are associated with disease progression and then looking at
different exposures and what you can see is that the majority of
changes are associated with progression, disease progression but
with arsenic only a subset was also associated with progression
and those were the gross chromosomal changes whereas with tobacco
more of the mutational changes were associated with the exposure
and there were some changes that were not associated with progression
but they were observed with the exposure, suggesting that these
are areas to look at as early markers in etiologic studies.
So, in the future
I plan on conducting more studies focusing on chromosome 9q. Also,
9p is not up here which is frequently lost in bladder cancer, but
that is because it was lost all the way across the board, and it didn't
have any relationship with exposure, but we plan to continue this
work with additional markers and also working on looking at additional
exposures. TOP |
| Slide
19: |
| In
future studies, right now I am working on two studies, a Spanish
bladder cancer study at NIH. Deborah Silverman and Mustaf Hydrosanichi
are the PIs in our Occupational and Environmental Epidemiology Branch
and this study has a heavy focus on occupational exposures and also
environmental exposures. So, we are going to be looking at disinfection
by-products, exposures in the textile industry, smoking, urinary
pH, urinary stasis.
The newest studies,
and now this study has 1200 cases and 1200 controls; the study I
just showed you had 114 case-control pairs. So, these studies are
much bigger to look at a number of genetic susceptibility markers.
We are looking at one carbon metabolism pathway, other types of
metabolic genes and the part that I am primarily going to be working
on and building a collaboration with Spanish collaborators is looking
at epigenetic changes which are some of the earlier changes that
don't associate with disease progression but may correlate directly
with specific early exposures as well as genetic tumor marker studies
looking very closely at chromosome 9p and 9q and I am also working
on a New England bladder cancer study which has a heavy environmental
component. This is a population-based study, and one hypothesis
for the excess incidence in bladder cancer in the New England states
is environmental arsenic exposure.
The levels are
not as high as what I have shown here, but they are still elevated.
Also, looking at tumor markers and genetic susceptibility enzymes
TOP |
| Slide
20: |
and this is just a list of all my collaborators.
TOP
|