AUSCHWITZ LIES - Holocaust Handbooks

POLISH PSEUDO-SCIENTISTS 55
cyanide per kg sample material, whereas the moist, cold, CO2-loaded alleged
gas chambers of crematoria II and III, also newly put into operation, would
show a level of 0.388 mg/kg, a figure greater than that of the delousing chambers
by a factor of 16. With all other combinations of materials the factor is
always greater than 1 as well (cement/cement: 2.2; cement/lime: 72;
lime/lime: 533). If the Polish authors claim nevertheless that the alleged homicidal
gas chambers did not have a higher reactivity to bind hydrogen cyanide
than the delousing chambers, then they turn their own research results upside
down!
Facing the fact that the Poles’ maximum analytical values of their samples
from delousing chambers are comparable to those from the underground morgue
no. 1 of crematorium II – the alleged homicidal gas chamber – they force
themselves to conclude that this is hardly surprising since large areas of this
underground morgue are protected from environmental influence. Therefore
the cyanide, once bound, would have as little reason to disappear from the
morgue as from the delousing chambers. That we can agree upon. We can also
agree on the implicit conclusion that the traces of cyanide remaining in the delousing
chambers would be present in the same order of magnitude as in the
alleged homicidal killing gas chambers, if the latter were used to kill hundreds
of thousands of inmates with HCN. However, considering the amount of total
cyanide, this is absolutely not the case. Rather there is a world of difference
between the analytic values – a factor of 1,000 or more – and this in spite of
the higher reactivity of the alleged homicidal gas chambers.
Another point reflects even worse on the chemical competence of the three
Polish authors: They say once more that they cannot explain how the brick on
the outside of the delousing chambers in Birkenau came to have patchy blue
discolorations. The Polish authors have confirmed the relative inertness of
bricks to the formation of detectable cyanides in their own gassing experiments,
which I had determined as well. But they do not seem to have read attentively
my expert report or my book, which they cite. It should be clear that
the high concentrations of soluble cyanide compounds on the inner side of the
walls of the delousing chambers would slowly diffuse to the outer side of the
wall, driven by moisture rising from the soil through the walls and evaporating
preferably at the outside. Once deposited at the outside of the walls, soluble
iron cyanide compounds would be quickly converted into long-term stable
Iron Blue under environmental influences. Whoever inspects the surface of the
bricks of this building would realize that they have been eroded on their surface,
probably mostly because of acid rain, which occurs frequently in Upper
Silesia, one of the dirtiest industrial regions of the world until the late
1980s/early 1990s. In chemical terms, iron oxides in the brick, which had been
physically fixed by the sintering process during production, were physicochemically
activated by an acid medium and thus could more easily react with
cyanide compounds migrating to the surface to form Iron Blue.