| Three
experiments were performed to assess the behaviour of Monkiskin
- Industrial Absorbent as a pollution control/containment medium.
|
| 1.
Oil Sorption capacity |
|
In
this experiment used motor oil was used to check the maximum
amount of oil that Monkiskin - Industrial Absorbent can hold.
This is important when making recommendations for its use
to soak up spills. The Air Filled Porosity/Water Holding Capacity
(AFP/WHC) method and apparatus of AS 3743 was used.
Firstly
the WHC of the particular batch of Monkiskin - Industrial
Absorbent was measured using the conventional AS 3743 methodology.
It found that 710 mls of Monkiskin - Industrial Absorbent
(the volume of an AFP/WHC core) would hold about 400mls of
water against gravity or a WHC of 56.3%. Note that this occurs
with a suction height of 12 cm (ie 12 cm deep Monkiskin -
Industrial Absorbent).
In
the oil experiment 4 treatments were set up. Firstly 710 mls
of Monkiskin - Industrial Absorbent was measured into each
of 4 large trays. To each of the treatment trays 100mls, 200mls,
400mls, and 800mls of oil was poured and thoroughly mixed
in. Monkiskin - Industrial Absorbent plus oil was then placed
back into a 710ml AFP core which rested on a rack to allow
oil to drain. The cores were left over the weekend (60 hours)
for oil to drain and then the oil draining into the tray was
weighed. The density of oil had previously been measured at
0.85g/ml allowing this to be converted to a volume of oil.
Results are expressed in Table 1.
|
| Table
1. Oil Holding Capacity of Monkiskin - Industrial Absorbent.
|
| |
100mls
oil |
200mls
oil |
400mls
oil |
800mls
oil |
| Oil
drained after |
0.0 |
0.0 |
75 |
396 |
| 60
hours mls |
|
|
|
|
| Oil
retained or held mls |
100 |
200 |
325 |
404 |
| Oil
holding capacity as % v/v |
14.1 |
28.2 |
45.8 |
56.9 |
|
|
Discussion
and Conclusions: These results appear to show an unexpected
“enhancement” effect ie that the more oil that is added the
more will be held. Plotting the results on a graph (see appendix)
demonstrates that there is actually an asymtote to this, ie
that the maximum oil holding ability levels off at about 405
mls /710mls Monkiskin - Industrial Absorbent or 57%.
One
explanation for this “enhancement effect” is that the material
swells in the presence of oil quite noticeably and this would
increase its oil holding ability.
An
interesting observation is that the oil holding capacity is
not dissimilar to the water holding capacity.
A
fair conclusion to allow for all situations would be that
the material will hold a minimum of 40% of its volume of oil
in all conceivable circumstances. To claim 50% would be reasonable
in nearly every conceivable circumstance.
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|
| 2.
Separation of oil/water mixtures |
|
A
potentially important application is to use the material to
remove oil from the surface of waters or to separate by filtration
oil from water.
In
this experiment three AFP/WHC cores were filled with 710mls
of Monkiskin - Industrial Absorbent. These were then emptied
into each of three tough plastic bags and emulsified oil/water
mixtures were added. This was achieved by rapidly shaking
500mls water with each of 100, 200, and 400mls of oil and
rapidly pouring the milky emulsion into the plastic bag before
the oil and water separated again. Contents of the bag were
stirred and shaken thoroughly and left for about one hour
to full soak up their contents.
Contents
were then emptied carefully back into the three AFP cores
and left 60 hours to thoroughly drain. The volumes of water
and oil draining from the cores was then measured. Results
are given in Table 2.
|
| Table
2. Oil/Water separation results. |
| treatment |
100mls
oil/500mls water |
200mls
oil/500mls water |
400mls
oil/500mls water |
| Total
Volume added |
600 |
700 |
900 |
| Water
Drained mls |
235 |
300 |
345 |
| Oil
Drained mls |
0 |
25.6 |
170 |
| Water
held mls and (as % of added) - A |
265
(53%) |
200
(40%) |
155
(31%) |
| Oil
held mls and (as % of added) - B |
100
(100%) |
174.4
(87.2%) |
230
(57.5%) |
| Total
Volume held |
365 |
374.4 |
385 |
| Fluid
holding capacity % |
51.4 |
52.7 |
54.2 |
| Oil
to water partitioning ratio B/A |
1.89 |
2.18 |
1.85 |
|
|
Discussion
and Conclusions: The “enhancement effect” of increasing
fluid holding capacity with increasing oil addition is also
evidence here but to a smaller extent than with adding oil
alone. Also, swelling was again seen with added oil.
The
interesting effect also is the “partitioning effect” that
is, in the presence of an oil/water mixture the Monkiskin
- Industrial Absorbent preferentially absorbs oil over water.
The results also demonstrate a “competitive effect” in that,
if the preference for oil was absolute then no matter how
much water was added the oil would be exclusively held. This
is not the case and clearly, from the first experiment the
Monkiskin - Industrial Absorbent should have been able to
hold between 300 and up to 400mls of oil which it cannot do
in the presence of excess water. The net result is that while
oil is preferred over water increasing amounts of water have
an adverse effect on oil retention.
A
rough “partitioning ratio” can be estimated from the proportion
of oil added and held vs the proportion of water added and
held. These are given in the final row of the table. The average
of the three ratios is 1.97 or about 2. It is thus true to
say that Monkiskin - Industrial Absorbent shows twice the
affinity for oil as for water.
This
can be translated into a recommendation. The total fluid holding
capacity is about say 52%. If presented with say 2 litres
of 40% oil/ 60% water emulsion 1 litre of Monkiskin - Industrial
Absorbent could be predicted to absorb 520mls of the mixture
and of this 520 mls twice as much will be oil as water or
about 346 mls oil and 173mls water. Thus if the 2 litres was
40% oil or 800mls of oil then 1 litre of Monkiskin - Industrial
Absorbent would remove 43% of the oil.
How
much Monkiskin - Industrial Absorbent is required to remove
all the oil is a more difficult calculation. Actually a 40/60
oil water emulsion is higher in oil than most real life situations.
Take a 5% oil film on 95% water, say 10 litres of it or 500mls
oil on 9.5litres water. How much Monkiskin - Industrial Absorbent
is required to remove all the oil but leave as much water
as possible?
Assuming
the total fluid holding capacity of 52% is composed of 2/3
oil and 1/3 water (partitioning coefficient of 2) then while
holding 500mls oil the Monkiskin - Industrial Absorbent must
also hold 250mls water or a total fluid capacity of 750 mls.
Divide this by 0.52 (the fluid holding capacity) we get 1442
mls of Monkiskin - Industrial Absorbent. This should remove
all the oil and only 250mls of water. A check of this was
made adding 1500mls of Monkiskin - Industrial Absorbent to
a bucket containing 9.5 litres water and 500mls of oil. This
was then stirred for a few minutes every hour for 3 hours.
Upon removal of the floating Monkiskin - Industrial Absorbent
very little oil (less than 10mls) was left.
A
general recommendation would be that the maximum oil removal
can be obtained by adding three times as much Monkiskin -
Industrial Absorbent as the anticipated oil volume. For optimum
and complete removal this could be increased to say a factor
of four. ie to completely clean up 1 litre of oil off water
will require 3-4 litres of Monkiskin - Industrial Absorbent.
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|
| 3.
Landfill Leachate Tests |
| Landfill
leachate occurs as a result of water flowing through waste landfills’
especially uncontrolled landfills which are not caped properly.
It is common to find soluble zinc, phenols, cyanide, and ammonium
in landfill leachates. |
| Methodology |
| A
mock landfill leachate solution was made to the following approximate
specification- |
Zinc
Phenol
Cyanide
Ammonium |
10
mg/l using zinc acetate
50 mg/l
20mg/l using potassium cyanide
100 mg/l using ammonium chloride. |
| In
each of five 1 litre beakers 500mls of leachate solution was
added. To each beaker a series of Monkiskin - Industrial Absorbent
additives were made to give the following experimental design- |
Treatment
0
1
2
3
4 |
mls
leachate
500
500
500
500
500 |
mls
Monkiskin - IA
0
100
200
400
600
|
|
| Beakers
were stirred occasionally over 4 hours then filtered to obtain
test solution. Test solutions were then analysed for the four
contaminant components. Australian Government Analytical Laboratory
measured Cyanide and phenol, Sydney Environmental and Soil Laboratory
measured ammonium and zinc by routine methods. The following
results were obtained- |
| Treatment
mls MIA/500mls |
Ammonium
mg/l |
Zinc
mg/l |
Phenol
mg/l |
Cyanide
mg/l |
| 0,
0 |
70.6 |
10.3 |
20.0 |
12.0 |
| 1,
100 |
53.6 |
0.2 |
17.0 |
10.0 |
| 2,
200 |
44.4 |
<
0.2 |
19.0 |
12.0 |
| 3,
400 |
37.7 |
<
0.2 |
12.0 |
8.3 |
| 4,
600 |
34.3 |
0.2 |
11.0 |
5.9 |
|
|
Discussion:
All contaminants show a reduction upon the addition of coir
to the contaminated water. The absorption of ammonium is likely
to be by simple cation exchange and is characteristically
non linear. The pattern shown here of diminishing ammonium
removed as more Monkiskin - Industrial Absorbent is added
is very typical of an “exchange isotherm” (Sposito 1989).
The relationship fundamentally says that as the concentration
of ammonium external to the Monkiskin - Industrial Absorbent
exchange sites increases the absorbent will absorb (or exchange)
more ammonium, or vice versa, as the ammonium level outside
the exchange site decreases it will absorb less ammonium.
This essentially says that while ammonium concentrations in
a landfill solution can obviously be reduced by Monkiskin
- Industrial Absorbent it can never be eliminated except at
infinite Monkiskin - Industrial Absorbent concentrations.
This is typical of exchange reactions and also phosphate removal
from solution which is also concentration dependant. It is
also dependant on the presence of other ions on the Monkiskin
- Industrial Absorbent and could be improved where certain
ions are absent (for example potassium which is much like
ammonium in size and shape).
From
this experiment the best we can achieve is to approximately
halve an ammonium concentration of 70mg/l by adding equal
quantities of Monkiskin - Industrial Absorbent to water. This
will change depending on the initial ammonium concentration.
Zinc
behaves differently to ammonium. This is essentially because
Zinc is a “preferred exchange ion” and does not compete with
sodium, potassium, calcium and all the other exchange ions
being greatly preferred over these other ions. This is typical
of all the high molecular weight (heavy) metals. It would
appear that levels of zinc significantly higher than 10 ppm
can be totally removed from the solution. This is likely to
be the case for a range of other high molecular weights metals.
It
can be calculated that the specific absorption capacity of
Monkiskin - Industrial Absorbent for zinc is at least 50.5mgZn
per litre of Monkiskin - Industrial Absorbent. As stated it
could be significantly higher than this, we did not use a
lower Monkiskin - Industrial Absorbent content than 100mls.
If we had used 50mls we might demonstrate greater capacity.
Phenol
and cyanide show a different trend with significant reductions
only occurring at 400 and 600mls/0.5l (800 to 1200 mls Monkiskin
- Industrial Absorbent per litre of water). The mechanism
for removal of these contaminants is likely to be physisorption
rather than cation exchange (both are weak acids which means
they are negatively charged).
In
a practical sense, once about 50/50 Monkiskin - Industrial
Absorbent and water ratio is exceeded the water has to be
squeezed out of the absorbent as no free water remains.
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|
| Summary |
|
Monkiskin
- Industrial Absorbent will absorb significant quantities
of oil. It is likely that its oil, solvent, or water total
holding capacity are all similar at around 55% by volume.
Applying a small safety margin a simple recommendation would
be that, for oil or solvent sorption in the absence of water,
twice as much Monkiskin - Industrial Absorbent as the volume
of oil to be absorbed is required. If you need to soak up
1 litre of oil use 2 litres of Monkiskin - Industrial Absorbent.
In
the presence of water there is competition for sorption sites
in the Monkiskin - Industrial Absorbent with oil. Oil is preferred
over water however and a rough partitioning coefficient of
2 can be calculated. This means that, in the presence of infinite
water the fluid sorbed onto the Monkiskin - Industrial Absorbent
from a mixture of oil and water will be 2/3 oil and 1/3 water.
A simple recommendation is to apply 3 to 4 times more Monkiskin
- Industrial Absorbent than the anticipate oil volume and
all the oil floating on water will be removed.
A
major advantage is that the oil/Monkiskin - Industrial Absorbent
mixture is buoyant and remains floating on the water where
it can be removed as a semisolid using, for example, a fine
scoop net rather than booms, skimmers, tankage etc.
For
the removal of contaminants from waters the product is likely
to prove highly effective for metals due to specific adsorption
on exchange sites. Even at a low absorbent to water ratios
it is likely that all metals will be removed at levels well
in excess of 10mg/l. This requires further work to find out
what maximum level of dissolved metal can be removed.
For
other contaminants the sorption is controlled by isothermic
adsorption which predicts that we can only remove all the
substance at infinite concentration of coir which is obviously
not practical. The material can, however, reduce and lower
the concentrations of a variety of organic and inorganic substances.
The
product generally appears worthy of consideration as an environmental
pollution control products for spill kits, oil removal, and
removal of metals from waters at least
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|