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Filter requirements and calculations
Calculating ideal flow rates and filter retention times for koi pond
filtration systems can sometimes be contradictory and for the average
koi keeper with modest stocking levels and a reasonable filter there
shouldn't be a problem. But there are a lot of over-stocked ponds with
pretty poor filtration systems - find out why.
Let's get complicated
When it comes to filter sizing, life can get complex. As I've said,
if we only wanted simple nitrification, it is probable that filter sizes
would be small. However, as well as nitrification koi-keepers want:
gin-clear' water
breakdown & removal of DOC,
conditions which discourage
filamentous algae (blanketweed)
generally optimal water conditions for
fish.
In trying to meet these wide-ranging demands filters are built far
larger than they would be if based on the required SSA of filter media
alone.
The longer the better
Broadly speaking, the effectiveness of
biological filtration is improved the longer the 'polluted' water is
held in the filter - i.e. the longer the
retention time. The most time-consuming process in filtration is the
breakdown of dissolved organic carbon compounds into simple inorganic
compounds. These compounds are ultimately incorporated back into living
organisms. This complex chain of processes is not instantaneous and
will, even under ideal circumstances, take some time. If insufficient
filtration time is available, intermediate products will be pumped out
of the filter back into the pond. This is clearly undesirable and rather
defeats the object of having a filtration system. Indeed, this may well
be the reason why excessive algal growth occurs in some ponds, with the
filter merely producing an endless supply of plant nutrients!
So for how long should water be retained in the biological section?
This depends on how polluted the water is in the first place. Certainly,
industrial water treatment plants - which handle much higher levels of
pollution from sewage etc. - would retain water in the plant for many
hours before it was deemed sufficiently clean to return to the nearest
water-course. Given that pond water is likely to be only mildly
polluted, a retention time of ten minutes, possibly longer, will usually
suffice.
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the more polluted the water is, the longer it
needs to be retained in the filter. Most koi ponds will require
a retention time of at least a few minutes |
So how do you calculate the retention time of your filter? This is
determined by the flow rate and the volume of water in the filter. If
water output from the filter is 2,000 gallons/hour and the filter
contains 500 gallons (when full of media) of water then:
filter
retention time = filter size/pump rate,
so, in our example:
retention
time = 500 (litres) / 2000 (litres / hour flow rate) = 0.25 hours (which
is 15 minutes).
so a
given sample of water will take 15 minutes to pass through the filter
and back to the pond
In the above, the filter capacity represents the amount of water
in the filter - not the physical size of the filter, which will be
greater. The retention time or the size of the filter will depend to a
very large extend on the type of filtration medium used. A solid medium
with low void space such as gravel will occupy much more filter space
than large-pored, lightly packed media and therefore leads to a lower
retention time.
More calculations! Using our same example of a 500 gallon filter. If
we now nearly fill it with gravel, the volume of water it will hold will
be reduced substantially - maybe to as little as 150 to 200 gallons.
Using the above example, the retention time of such a filter would now
become;
200/2000 = 0.1 hours (6 minutes) or less
This compares the original estimate of a
retention time of 15 minutes
In comparison, if the same filter was filled instead with matting or
plastic, there would be hardly any displacement and the filter will
probably still hold in excess of 450 gallons, giving a retention time
over double that of gravel. So a filter with a
dense, low-void medium, such as gravel, will need to be substantially
larger than one based on light-weight media, in order to achieve the
same retention time, which explains why koi filters were
traditionally so large.
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the retention time and therefore the filter size
will depend on the filter media used. Cheaper, dense media such
as gravel will need larger filters to achieve the same
efficiency as lightweight media |
The quicker the better?
Just when everything starts to make sense, along comes a
complication. While a longer filter retention time will produce better
water quality we also have to consider pond turnover times. Why? Because
polluted water is produced in the pond and, if there was a slow turnover
at the filter, it would take longer for pond water to get processed by
the filter.
To make sense of pond turnover rates it is helpful to return to the
original analogy of koi being sewage-making machines: expensive food in
one end and sewage out the other. Our seemingly impossible aim should be
to remove this pollution as fast as it is produced. If we can manage
that then we would have perfect water conditions most of the time.
When we are considering pollution the primary concern is not so much
the volume of water, but rather the number of fish and the amount
of food we feed - because this is what determines both the amount of
metabolic ammonia and the quantity and quality of solid waste.
There are several ways to calculate ammonia production in a koi pond. A
rough and ready estimate can be made based on the amount of food fed
each day.
Each kilogram of fish food will result, on average, in 37 grams of
ammonia being produced, together with copious faeces. And there is other
organic waste, such as that from decomposing algae and microorganisms.
The important point is that as the stocking, and thereby feeding level,
is increased the water will have to be treated at an ever quicker rate
if water quality is to be maintained.
If, for instance, we had a pond of 20,000 litres (4,500
gallons) and the fish were fed 200 grams of food per day, this
would produce approximately 7.5 grams (7,500mg) of ammonia per
day, an average of say 300 mg per hour. (In reality the ammonia
level would fluctuate throughout the day, being highest shortly
after feeding).
At this feeding rate, if no ammonia was removed, at the end of
a day the ammonia content of the water would be 24 x 300 mg
ammonia = 7 200 mg in 20,000 litres of pond water, giving an
ammonia concentration of 0.37 mg/litre, which is too high.
Conversely, if it was possible to remove the ammonia at the
same rate as it is produced - namely, 300 mg per hour - the steady
state ammonia level would be zero. To remove ammonia this quickly
we would have to pass the entire contents of the pond through the
filter every hour, giving a flow-rate of 20,000 litre/hour,
otherwise there will always be some residual ammonia present.
Deep breath! - If, instead of a
flow-rate of 20,000 litre/hour, we had a flow rate of the pond
volume every two hours - or half the pond volume every hour (same
thing), an oversimplified calculation would give:
300 mg
ammonia / 20 000 litres (pond volume) x 10000 (flow rate
litre/hour) = 150 mg ammonia removed per hour, leaving 150mg in
the pond, or a steady state of >0.01 mg / litre. (This makes
the simplifying assumption that there is no nitrification
occurring in the pond.)
We can see the effects of increased
stocking and / or feeding levels if we take an exaggerated example in
which we treble the feeding rate to 600 mgs of food per day
600 grams of
food per day would produce around 900 mg ammonia per hour. With
the same flow rate we would remove 900 mg ammonia / 20,000 litres
(pond volume) x 10 000 (flow rate litres /hour) = 450 mg
ammonia removed per hour leaving 450 mg in the pond, or a steady
state of 0.02 mg /litre, an increasingly unacceptable level.
Clearly the only way to balance the
increased ammonia production would be to 'feed' the ammonia to the
filter at an ever increasing rate.
I should stress that the above examples are an over-simplification of
what actually happens since other factors, such as nitrification in the
pond rather than in the filter, also have to be taken into account.
Indeed, where the flow rates or filter retention times are less than
optimum, an increasing proportion of the ammonia nitrification will take
place in the pond rather than the filter. While it is not immediately
important where in the system nitrification takes place – it does help
to explain why some ponds are more upset as a consequence of disease
treatments than others. However, if flow-rates are kept constant and the
feeding rate is increased, there will be a steady increase in the
background level of ammonia.
It is not necessary to get any further involved in calculations, the
important point is that when high feeding/stocking levels are involved, the flow-rate is an important factor in determining the
ammonia removal rate.
Adequate flow-rate
So what is an adequate flowrate? As explained, it depends on the
feeding rate. The most commonly quoted advice is: turn over the volume
of the pond between 8 and 12 times a day. But it is important to
remember that this is a rule of thumb and flow-rates may well need to be
increased for higher feeding and/or stocking rates. Certainly,
koi-keepers who feed in excess of 0.25 kg of food per day may have to
consider increasing flow rates, particularly if there is a periodic
ammonia problem. Conversely, it may be possible to have a slower rate
when feeding levels drop, as they do in winter.
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the pond flow rate is dependent on the total
ammonia produced within the system, With higher stocking
densities there has to be a corresponding increase in flow rate.
In an average koi pond, a flow rate of 1/2 to 1/3 of pond volume
per hour should suffice. |
Filter size
Taking retention times and flow rates into consideration, when it
comes to choosing the right filter size, there are two important but
conflicting factors:
the right filter retention time, which
ensures all the required biological activity occurs,
brisk water flow to prevent a high
pond ammonia level.
If we decide that a flow-rate of say 10,000 litres per hour (2,200
gal/hour) and a filter retention time of 10 minutes are required then
the volume of water in contact with the
filter media at any time will need to be;
10,000/60 (minutes) x 10
(minutes retention time) = 1666 litres or 1.6m3.
This means that the filter should be able to hold 1.6 m3 of
water after it is filled with media. This is in addition to settlement
and spaces below the media trays. The required size of filter will then
depend on the media used. Using a high-void medium, such as matting or
plastic, we would need a little over 1.6 m3
of media to compensate for the small amount of water displacement,
whereas, with a solid medium, we might need at least 3m3 to
ensure the same volume of water in contact with the media after
displacement.
Although this may seem complex, these are the factors which need to
be considered to avoid some of the most common filtration problems which
often beset koi-keepers - namely, fluctuating water quality, high levels
of opportunistic micro-organisms and excessive algal growth.
The size of a filtration system becomes more critical as stocking
level, and thereby feeding rates, increase. Even when no new fish are
added, the continued growth of the existing pond occupants will
gradually increase the demand on filter performance.
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Ideally, what we want is a fairly brisk
flow-rate, turning over the pond volume every 1 to 3 hours
(depending on feeding and stocking rate) but at the same time a
slow, almost imperceptible flow through the filter, allowing
sufficient time for the various important biological processes
to occur. Water passing through the filter should be in contact
with the filter media, and therefore the biofilm, for at least
ten minutes, possible longer. |
Other considerations
After all this discussion on retention times, flow-rates and filter
media, it is worth considering some other salient aspects of
filter design. Most purpose-made, retail filter units are practical and
well designed but I have to say that some are pretty poor, for the
following reasons.
Apart from overall filter size, which we have already
discussed, another important aspect is shape and water transfer
between the chambers. There is little point in having several
cubic metres of expensive filter medium if it is not properly
utilised. The design of a filter system should be such that water
passes evenly through all of the media and not just at one end or
through the centre.
Ideally, transfer ports should be the full width of the
chamber; otherwise there will be a tendency to create a narrow
channel of water flowing into the next chamber, leading to 'dead'
spots within the chamber. Square chambers are not the most
efficient, giving little water flow in the comers. This drawback
has been overcome in some cases by the used of curved or circular
chambers, giving a more effective 'working' area within the
chamber. With careful design it is also possible to create a
swirling motion as water is transferred from one chamber to the
next. This helps avoid dead spots, giving an even flow through the
media and, to a lesser degree, will help settle some of the finer
solids.
Just as important in filter design is ease and efficiency of
maintenance. The best design is for each filter chamber to have a
bottom-drain for easy cleaning, and the base should be benched or
sloped towards the drain. Regular flushing of the bottom drain in
each chamber will help clear away fine solids; and periodic
cleaning of chambers by emptying them and flushing the media with
pond water will prevent a build-up of unwanted mulm and other
organic debris.
So there we have it - the basic requirements for good filter design
and performance. All filters will comply with these guide lines to
a great extent. At the end of the day the proof of the pudding is in the
eating and if your filters provide consistent good water quality (to the
five point standard), nice clear water and you don't have to spend half
the week end cleaning it - then you probably have things about right. If
however, you are constantly having niggling water quality or fish health
problems..................
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