

More
on ORP – Part
2
(Please revlew Controller
Concepts: ORP and Oxidation - Part I)
In ORP and Oxidation we discussed the critical
importance of oxidation in pool water and the fact that
the potential to oxidize – expressed
as ORP in millivolts – is
the only reliable measure of the quality, the “work value”,
of the chlorine or bromine in the water. ORP values
can be used to predict sanitation efficacy, organic consumption
(water clarity), even such things as the likelihood of
inactivation of that un-predictable, extremely tough
parasite called Cryptosporidium.
ORP is the medium of control for industrial, medical,
water, wastewater, and swimming-pool oxidants. That
little platinum electrode is found in more places than
you’d dream, serving the operators as a reliable measure
of what the chemical is doing, not necessarily the chemical
itself. In our swimming pools, the controller doesn’t
have any idea how much chlorine you have in the water,
indeed it doesn’t even know it is chlorine you are using!
What that smart machine does know, however, is what
it is that whatever you’re using is doing in the
water – the quality or
the resultant of the active compound doing the work.
It is simply called qualitative control.
We’re lucky that there’s only one chemical doing this
oxidizing work in a pool. If there were more than one
variable whose change would cause a significant ORP-reading
shift on the face of your controller, there would be
no way to control, by instrumentation anyway, the active
chemical product you’re interested in. Indeed, there
would be no automation industry at all. But since chlorine,
(if that’s the sanitizer in use,) is the only changeable
thing in the water that makes the needle move, or the
digits change, it is fully controllable. “If you can
read it and make it change, you can control it,” is an
old adage of the instrumentation profession. And, if
what you’re really reading is a measure of the work done
or about to be done, that’s better yet.
“About to be done”? Yes. ORP has another little-known
quality about which pool operators should be familiar.
There exists a lead time, where ORP reacts ahead of
the resultant residual. In a quiescent pool (everything
running, but no swimmer load) the ORP and the residual
quantity should “agree”. That is, the published interrelationship
between the pH value, the ORP level and the ppm required
to achieve that ORP should be right on. (We use this
relationship to set up, or “standardize” our machines,
right?) However, when the swim team jumps in or, worse,
the football team arrives at the pool after the sweaty
game, all bets are off. The potential to oxidize drops immediately as
oxidant needs are sensed and oxidation begins. But the
DPD test kit tells us that the residual, that amount
of un-used, ready-to-go chlorine in the water, has yet
to change. Consumption has barely begun, but the ORP
shows a sharp drop! You can see the value of this phenomenon,
where actual “demand conditions” could be analyzed.
However, don’t “standardize” your machine during
those high-demand times of the day. You’ll be mis-calibrating, not making
things more accurate.
What about the effect on ORP of potassium monopersulfate,
or ozone, or peroxide? The “oxy” products actually don’t
elevate the ORP much, so can be ignored. Ozone is a powerful
elevator of ORP, however it is short-lived and usually
introduced after the location of our ORP probe
- within the water in the pumproom still on its way back
to the pool - and is primarily used as a supplement,
not a controlled parameter. Peroxide does elevate ORP
too, and is, albeit rarely, used instead of chlorine
with ORP values in the realm of 500 mV or so – not adequate
for most public-pool needs.
While we brag about ORP and the marvelous qualitative
nature of its control, there is one final kicker that
can monkey up the whole picture. That’s the all-too-common
practice of “lying to the machine”! Again relating to
the screw-turning procedure called standardization, let’s
all understand something here - the only time that ORP
is an honest value is when some standard is
used to establish the starting point. If you tweek your
standardize pot, calibration screw or menu setting to
your liking, you quite likely are not basing the setting
on anything “standard” at all. If your electrode is
immersed in normal, un-stabilized pool water, and you’re
using a DPD kit for “free” chlorine values, you’re probably
going to be close. Better yet might be an ORP standard
signal from a calibrator, or calibrated “buffer solution”
into which you immerse your electrode, but neither of
these is commonly available. We have to count on our
own judgement regarding the accuracy of our starting
point.
If cyanuric acid is in the water, you can guarantee the
need to lie to the instrument, as CYA creates radical
drops in ORP for a given quantity of chlorine. Automation
on a stabilized pool is relegated to what we call “relative
control”; the only thing we can count on is if we turn
the knob clockwise, we’ll get more, if we turn it counter-clockwise,
we’ll get less. If the instrument attempts to calculate
ppm, it’s guaranteed to be wrong in the presence of CYA.
And any water containing 70 ppm CYA or more is un-automatable – that
is, increases in residual will not produce a rise in
ORP.
The last concern in the ORP story is related
to bromine and bromine-compounds used to produce HOBr
in your pool. We know that it takes about 2.2 times
the bromine residual to match a given amount of chlorine
in work value – even in
test kit readings – however,
conditions can exist that encourage the formation of
ineffective, sometimes offensive halide compounds as
well as other even less desirable “products of imcomplete
oxidation” such as trihalomethanes – carcinogens beyond
the scope of this article. In any case, we should expect
the active bromine in the water may result in much less
ORP than similar quantities of chlorine.
As pH is very much less influential on HOBr
(less OBr- Ion), the chlorine nomograph - that familiar
family of curves developed by STRANCO and discussed in PrP Number
6 – doesn’t apply. This
industry hasn’t developed a new nomograph for bromine,
so we’re whistlin’ in the wind for accurate relationships
between real ORP and bromine residuals. When they’re
developed, PPOA will be among the first to know...
For those states of the union (their respective
health departments, that is) now legislating minimum ORP
values, a noble endeavor indeed, they are going to have
one tough time insuring compliance. The World-standard
650 mV. is pretty easy to achieve, even with stabilized
chlorine or bromine, but 750 mV., now showing up in some
western health codes, is doggone difficult to manage with
bromine and near impossible with cyanuric stabilization.
Environmental health specialists will have to carry an
ORP standard to determine if the water, manually treated
or the product of a controller, is anywhere near the value
assumed or set by the operator.
~
kw
© 2007
Professional Pool Operators of America |