HydroFLOW TECHNICAL INFORMATION AREA - NAVIGATION
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Physical Conditioning and
the HydroFLOW Technology
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Hard Water - the Cause of the Problem
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Rainwater is slightly
acidic. In heavily industrialised regions, emissions make the rainwater
more acidic. The hardness in water comes from the calcium and magnesium
salts, that are dissolved into the water, from soluble rocks through
which the rain water flows.
Hardness : Temporary and Permanent
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Temporary
Hardness in most cases is associated with calcium and magnesium
carbonates and bicarbonates. These crystal forming salts are held
in solution and will remain so, unless there is a change in pressure
or temperature, which will cause the water to become supersaturated,
resulting in the precipitation of encrusting scale on hot or rough
surfaces, such as pipes and heat exchangers.
Permanent
Hardness is due mainly to calcium and magnesium sulphate and is
not effected by heat or pressure change. However if the water is
evaporated it will remain and will encrust.
The water hardness
problem is sometimes exacerbated by being stored in reservoirs constructed
from different materials and is also further exacerbated seasonally
as the water table rises and falls resulting in concentrations.
Chemists are concerned
with the chemical reaction of elements and compounds that have formed
as a result of the reactions. To gain an understanding of Physical
Conditioners, one has to take into account the physical effects
that occur before the reactions take place. Hence Physical Conditioning.
Stable chemical compounds
are normally electrically neutral. When they dissolve in water to
form solution, they may separate into oppositely charged particles
called ions. This process is known as dissociation and can be partial
or complete. Although ions are independent particles, the connection
to their opposite is maintained and is re-established following
crystallisation. This process of dissociation in water is used widely
in industry to separate metals from their compounds, for electroplating
and the separating of the elements of water itself, Oxygen and Hydrogen
gasses.
The mineral salts
found in water can be determined in type and quantity by simple
evaporation and weighing the residue. In addition to hardness salts
- and by other techniques - sodium chloride, sodium sulphate and
silica can be found. These substances do not exist in solution as
definite compounds, but as "ions" - charged soluble particles of
metal (known as cations) or as acid radicals (know as anions).
The most commonly
occurring cations are:
Calcium |
Ca2+ |
Magnesium |
Mg2+ |
Sodium |
Na+ |
The most commonly
occurring anions are:
Chloride |
Cl- |
Sulphate |
SO42- |
Bicarbonate |
HCO3- |
The negative and
positive signs indicate polarity of electron charge. The negative
sign indicates electron gain, positive sign electron loss. Contaminants
can be grouped according to polarity and magnitude of charge.
Neutrality of Water pH Value
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Pure water in its
liquid state is also slightly dissociated into its constituent ions.
H2O -------> H+ + OH-
hydrogen ion, hydroxyl ion
This equation suggests
that water contain hydrogen ions moving freely within the liquid
however a hydrogen atom with one electron removed is simply a proton.
It is now recognised that the protons attach themselves to water
molecules to form a hydronium ion H3O+. For simplicity,
H+ ions will be referred to below, although the physical reality
is, that such species do not have an independent existence in water.
Both hydrogen and
hydroxyl ions are present in exactly the same quantity, so that
pure water is "neutral". In a unit weight of pure water there will
be 0.0000001 unit weights of Hydrogen ion and of Hydroxyl iron,
or 10-7 parts of each. The pH value - the index of acidity, alkalinity
or purity - uses the figure 7 as a neutral or purity point of the
scale. Natural pure water is said to have a pH value of 7.
pH = - log
10 (H+) (where H+ is the hydrogen ion concentration).
As hydrogen ion concentration
is increased the pH value decreases. As Hydroxyl concentration increases
the pH value increases.
Acidity is due to
hydrogen ions so the more acid the water becomes the lower its pH
value Alkalinity is due to hydroxyl ions so the more alkaline the
water becomes, the higher its pH value. This is because acids give
hydrogen ions in solution, while alkalines give hydroxyl ions:
H2SO4 ------> 2H+ + SO42-
sulphuric acid
NaOH
------> Na+ + OH-
caustic soda
The pH scale covers
the range of 0-14, from strongly acid to strongly alkaline.
Crystallisation normally
occurs when a solution becomes supersaturated. A supersaturated
solution is one that contains a higher concentration of solute than
its equilibrium concentration (saturation). However supersaturation
alone is not sufficient for a system to begin to crystallise. It
is generally accepted that two steps are involved in the formation
of microscopic crystals from supersaturated solutions: First, nuclei,
minute crystalline entities of definite size, must be formed (nucleation);
and second, these nuclei must grow (crystal growth). There are many
other variables that influence the nucleation and growth of crystals
such as the presence of the impurities; turbulence within the system;
the nature and state of the surfaces in contact with the solution
etc.
There are two basic
nucleation mechanisms:
- Homogeneous nucleation
- where the nucleus is formed spontaneously from the mother solution;
and
- Heterogeneous
nucleation - where a foreign substance, such as a metal surface
or another nucleus, acts as a seed for precipitation.
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Any
charged species (ions) can be regarded as a dipole and will
be attracted to each other's opposite pole. Ions are completely
dissociated and distributed randomly throughout a solution
(see above). Ions become associated due to diffusion and electrostatic
attraction. This attraction is increased by orientation of
the dipoles in an electric field. |
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An
electric field is the force field that exists between any
concentration of charges. HydroFLOW can create
such concentration of charges throughout the system by creating
the electric field, as will be described below. |
HydroFLOW
produces an electric field which is switched on and off. The length
of the off sequence is randomly controlled. By switching
the electric field off, adjacent species move together to
form clusters (see above). These clusters, themselves representing
larger dipoles, are affected by the electric field during the on
sequence, and are joined together to form localised areas of high
concentration. The internal forces generated by these larger clusters
result in a contraction and concentration of the attraction forces,
this causes the collapse of the clusters into nuclei, which are
the seed crystal.
The presence of the
HydroFLOW electric field throughout the solute will enhance
the formation of these large clusters by orientating them, in both
the saturated and unsaturated solutions. This process attracts more
charged species and stable nuclei are formed (see Fig. 6). The attraction
forces of such nuclei become much greater and as ions diffuse to
the nuclei surface, a diffusion layer is formed and the ions become
incorporated into the crystal lattice. Crystals are formed and grow,
again helped by the effect of orientation of the ions by
the applied field, and aggregate to form larger crystals. (When
HydroFLOW is used, the diffusion is enhanced because
the ions are orientated by the electric field being applied.)
For this process
to occur throughout the system, the field has to be present throughout
the solution, especially closer to the area where the solution will
experience changes in temperature or pressure which are responsible
for the precipitation of the salts from solution. When HydroFLOW
is present, crystals are formed and grow helped by the orientation
of the ions in the applied field. Small crystals aggregate to form
larger crystals that grow at the expense of smaller crystals.
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The
energy and time necessary to orient and move the charged species
together will vary for different species. Any crystallising
system is characterised by the generation of a spectrum of
differently sized particles. The electric field applied by
HydroFLOW allows for these differences. |
If hard scale deposits
are to be avoided, heterogeneous nucleation has to be minimised
and homogeneous nucleation under supersaturation conditions has
to be prevented. This can be achieved by the installation of HydroFLOW
that will start the generation of large numbers of nuclear clusters.
These clusters will grow and then collapse into nuclei that will
act as seed crystals. In the presence of a large quantity of seeds,
homogeneous crystallisation can occur in the solution. This will
cause the formation of large crystals as soon as the solution approaches
super-saturation. Large crystals then grow at the expense of smaller
crystals. The bulk of crystallisation will occur in suspension,
and heterogeneous crystallisation on the surfaces is thereby minimised.
Any heterogeneous
crystallisation that does form on the surfaces, will be such a thin
layer that it will be returned to solution, as soon as the solution
becomes unsaturated.
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To
be effective, a physical conditioner has to cause total precipitation
of scale for the temperature at which the water is being heated
in a heat exchanger. This will prevent the formation of supersaturated
water.
If supersaturated
water is allowed to form and then flows to other parts of
the plumbing system, scaling will occur on surfaces that
will be in contact with the supersaturated water. This will
continue until normal saturation is achieved.
To prevent
supersaturation conditions, a physical conditioner has to
produce sufficient seed crystals in the heat exchanger,
to ensure that all the crystal forming salts that can precipitate
will do so, and form stable crystals in suspension. As the
clusters that form the seed crystals are unstable and continually
return to solution, the conditioning field has to be present
close to and inside the heat exchanger to ensure the formation
of the clusters.
The crystal
HydroFLOW technology achieves this by efficiently
generating large numbers of seed crystals in the saturated
and unsaturated water. This process continues all over the
plumbing system all the time, and is due entirely to the
omnipresent propagating field replacing any seeds that are
continuously dissolving back into solution.
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In a scaling system
there are three processes that are at work: Heterogeneous crystallisation,
homogeneous crystallisation, and the return to return to solution
of the scale when the solute has become unsaturated.
Heterogeneous crystallisation
occurs primarily, on surfaces that are subject to increasing temperatures.
As not all the solute is in contact with the heating surface, convection
and circulating currents will carry supersaturated liquid away to
other surfaces. Scaling on other surfaces will continue until saturation
point is achieved. Homogeneous crystallisation occurs in large vessels
containing high volumes of solute, with a relatively small surface
area. As the solute is being heated, the solution becomes supersaturated.
The surface area is not sufficient to provide all the nucleation
necessary. The solute reaches a critical condition. At this point
any source of energy, such as turbulence in the solute, will cause
homogeneous nucleation. All the material that can precipitate does
so at once. A large number of small crystals are formed. These crystals
have high surface charges that cause them to adhere to all the surfaces,
including cold surfaces. The fine crystals that have adhered to
the surfaces will then become the nuclei for heterogeneous crystallisation
in subsequent heating cycles.
The third process
is the return to solution of the scale deposits. After the solute
has become unsaturated due to cooling or pressure change, a quantity
of the deposits will be returned to solution. The surface scale
that had been formed is not as stable as the crystals that have
been formed in suspension, due to the uneven way that nucleation
has occurred on the surfaces (see Fig. 7).
Descaling can only
occur if the water in contact with the scaled surface is unsaturated,
and is able to dissolve the carbonates to form bicarbonates. The
presence of CO2 is necessary for the formation of bicarbonates.
The CO2 which is present in solution in the water, comes
from two sources, one from the air in contact with the water and
the other, from the decomposition of bicarbonates due to the heating
process.
CaCO3 + H2O +CO2--------->
Ca (HCO3)2
unsaturated water
Descaling of the
heat exchanger using HydroFLOW relies totally on turbulence.
This is because the temperature of the water is increasing and would
normally only deposit scale. If turbulence is present, the water
experiences pressure changes that cause the water to change rapidly
from supersaturated to an unsaturated condition. While unsaturated
the water will dissolve the scale on the surfaces, and in the supersaturated
condition the deposits will grow in suspension due to the presence
of the clusters generated by the HydroFLOW applied
field.
In every system containing
solute, there is a balance of scale-formation and scale-solution.
In a system where the balance is in favour of scale-formation, the
system will experience scaling. In a system where the balance is
in favour of scale-solution, the system will remain free of scale.
Ca
(HCO3)2 + Heat + HydroFLOW ------> CAC3 + H2O + CO2
calcium bicarbonate, calcium carbonate, in solution in suspension
CaCO3 + turbulence + HydroFLOW + H2O + CO2--------->
Ca (HCO3)2
calcium carbonate, calcium bicarbonate, on the surfaces
HydroFLOW
simply tips the balance in favour of the scale-solution, by providing
a large quantity of unsaturated solution that dissolves the existing
surface scale. This process is repeated, dissolving surface scale
and forming suspended stable crystals. The heterogeneous crystallisation
is replaced by homogeneous crystallisation. However in this case
homogeneous crystallisation occurs as soon as the solute becomes
supersaturated, due to the presence of a large quantity of clusters
generated by HydroFLOW. As a result the old scale
will ultimately completely return to solution and is converted to
stable individual crystals. These stable amorphous crystals can
be removed by filtration in circulating systems. In open systems
they will pass harmlessly out with the flow
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