Active IQ Level 2 Certificate in Leisure Operations (sample manual)
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- Page 2 and 3: as would be the case of the backwas
- Page 4 and 5: The Langelier method This method re
- Page 6 and 7: It is recommended that pools should
as would be the case of the backwash<strong>in</strong>g of the filters, the <strong>in</strong>com<strong>in</strong>g pH of the ma<strong>in</strong>s water may well be<br />
different to that of the pool, and therefore the pH will change.<br />
• pH can be raised by add<strong>in</strong>g sodium carbonate<br />
• pH can be reduced by add<strong>in</strong>g an acid, for example, hydrochloric acid, sodium bisulphate, carbon<br />
dioxide (CO 2<br />
)<br />
The ability of chlor<strong>in</strong>e to kill bacteria is directly related to the pH of the water. As the pH <strong>in</strong>creases, the<br />
efficiency of chlor<strong>in</strong>e decreases. This effectively means that the pool operator will use more chemicals if<br />
they allow the pH to cont<strong>in</strong>ue to run at high levels.<br />
The follow<strong>in</strong>g diagram illustrates the l<strong>in</strong>k between pH and active dis<strong>in</strong>fectant with<strong>in</strong> the pool. The yellow<br />
l<strong>in</strong>e relates to hypochlorous acid (HOCl), which is the effective dis<strong>in</strong>fectant when us<strong>in</strong>g chlor<strong>in</strong>e and the<br />
red l<strong>in</strong>e relates to hypobromous acid (HOBr), which is the active <strong>in</strong>gredient when the pool is dis<strong>in</strong>fected<br />
with a brom<strong>in</strong>e compound.<br />
At a pH of approximately 7 active dis<strong>in</strong>fectant levels of hypochlorous acid are approximately 62%.<br />
However, this drops to 22% at pH 8.<br />
pH effect on dis<strong>in</strong>fection<br />
% 100<br />
90<br />
80<br />
70<br />
ACTIVE DISINFECTANT %<br />
60<br />
50<br />
40<br />
H0Cl<br />
H0Br<br />
30<br />
20<br />
10<br />
0<br />
4 5 6 7 8 9 10 11<br />
pH VALUE<br />
Source: Pool Water Treatment Advisory Group (PWTAG)<br />
pH and the efficiency of dis<strong>in</strong>fection<br />
There is a l<strong>in</strong>k between pH and the efficiency of dis<strong>in</strong>fection, <strong>in</strong> that as the pH rises, the less efficient the<br />
dis<strong>in</strong>fectant is. So, put simply, if the pH is allowed to rise, the pool operator will need to use more<br />
dis<strong>in</strong>fectant to ma<strong>in</strong>ta<strong>in</strong> the dis<strong>in</strong>fection level than they would with a pH between 7.2 and 7.4.<br />
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General pr<strong>in</strong>ciples<br />
It is absolutely essential that the pool operator takes care to ensure that pool water test<strong>in</strong>g is as accurate<br />
as it can be. Good quality results cannot be obta<strong>in</strong>ed by guess<strong>in</strong>g water quantities, us<strong>in</strong>g dirty equipment<br />
or contam<strong>in</strong>at<strong>in</strong>g <strong>sample</strong>s by allow<strong>in</strong>g f<strong>in</strong>gers to touch tablets.<br />
Chlor<strong>in</strong>e read<strong>in</strong>gs and pH read<strong>in</strong>gs are carried out with either a piece of equipment referred to as a<br />
comparator or a piece of equipment referred to as a photometer.<br />
The follow<strong>in</strong>g guidance applies to both:<br />
• test tubes and test cells must be kept clean and r<strong>in</strong>sed thoroughly after each test<br />
• never touch the tablets with your f<strong>in</strong>gers<br />
• wash hands before carry<strong>in</strong>g out water test<strong>in</strong>g, this is particularly true for the photometer method<br />
• test tubes and test cells should be fitted with rubber caps<br />
• crush<strong>in</strong>g rods, used for crush<strong>in</strong>g the tablets, should be cleaned and dried after use<br />
• discoloured test cells/test tubes should be discarded<br />
• the shelf-life of tablets must not be exceeded<br />
• use the correct tablets for the equipment that is be<strong>in</strong>g used<br />
• pool operators must be tra<strong>in</strong>ed <strong>in</strong> the use of the equipment used on the site<br />
• pool water <strong>sample</strong>s should be taken from the pool itself at a depth of 300mm at a po<strong>in</strong>t which has<br />
been found to be typical of the chemical conditions <strong>in</strong> the pool<br />
Comparators<br />
The traditional method of pool water test<strong>in</strong>g for pH and<br />
chlor<strong>in</strong>e is us<strong>in</strong>g the comparator. This is a very simple piece<br />
of equipment where the test <strong>sample</strong> conta<strong>in</strong><strong>in</strong>g the reagent<br />
dye is compared aga<strong>in</strong>st a circular disc conta<strong>in</strong><strong>in</strong>g different<br />
coloured glass.<br />
Ideally, the comparator should be fitted with a portable backlight<br />
which provides good quality white light to accentuate the<br />
colour or it should be viewed aga<strong>in</strong>st a bench-mounted white<br />
light source.<br />
The comparator is supplied with discs appropriate to the test be<strong>in</strong>g carried out, for example, pH discs<br />
(phenol red) and chlor<strong>in</strong>e discs. It is also possible to obta<strong>in</strong> a disc which will measure brom<strong>in</strong>e levels.<br />
Chlor<strong>in</strong>e disc for use<br />
with comparator<br />
pH disc for use with<br />
comparator<br />
Brom<strong>in</strong>e disc for use<br />
with comparator<br />
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The Langelier method<br />
This method requires the use of a factor table and the application of simple formula to determ<strong>in</strong>e the<br />
balanced water <strong>in</strong>dex.<br />
The formula is:<br />
Langelier Index = TF + CF + AF + pH - TDSF<br />
Where:<br />
TF = temperature factor<br />
CF = calcium hardness factor<br />
AF = total alkal<strong>in</strong>ity factor<br />
pH = value (not factor)<br />
TDSF = total dissolved solids factor<br />
The factor table is as follows:<br />
Temperature TF Calcium CF Alkal<strong>in</strong>ity AF TDS TDSF<br />
mg/1<br />
mg/1<br />
19 0.5 75 1.5 50 1.7 1,000 12.1<br />
24 0.6 100 1.6 100 2.0 2,000 12.2<br />
29 0.7 150 1.8 150 2.2 3,000 12.3<br />
34 0.8 200 1.9 200 2.3<br />
41 0.9 300 2.1 300 2.6<br />
400 2.3<br />
800 2.5<br />
When the calculation is completed the results will either be positive (plus) or negative (m<strong>in</strong>us). A positive<br />
<strong>in</strong>dex <strong>in</strong>dicates that the pool is scale form<strong>in</strong>g, a negative result <strong>in</strong>dicates the pool is corrosive.<br />
An <strong>in</strong>dex of zero would <strong>in</strong>dicate that the pool is balanced, provid<strong>in</strong>g that all of the tests are with<strong>in</strong> the<br />
agreed range for the tests. It is generally considered acceptable to have an <strong>in</strong>dex of between 0 and +0.5.<br />
A balanced water test is normally carried out on a weekly basis. An example of how to carry out the<br />
balanced water calculation if given below.<br />
Test Test result Factor<br />
Temperature 29 o C 0.70<br />
Calcium hardness 75mg/l 1.50<br />
Alkal<strong>in</strong>ity 50 mg/l 1.70<br />
pH 7.1 7.10<br />
Sub Total 11.00<br />
TDS 1000 12.10<br />
Langelier Index -1.1<br />
The results of the above test <strong>in</strong>dicates that the pool is corrosive and therefore, out of balance.<br />
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The operator needs to count the number of tablets it takes for the colour changes to occur. In the case of<br />
a 50ml <strong>sample</strong>, each tablet has a value of 40mg/l and hav<strong>in</strong>g determ<strong>in</strong>ed the number of tablets, this<br />
number multiplied by 40 is then corrected by the subtraction of 20 from the end result.<br />
Example - 5 tablets to achieve the colour change would be 5 x 40mg/l, which is 200mg/l m<strong>in</strong>us 20<br />
(correction factor). Result 180mg/l.<br />
Total alkal<strong>in</strong>ity test us<strong>in</strong>g 50ml <strong>sample</strong>,<br />
colour change method<br />
When measur<strong>in</strong>g <strong>in</strong>com<strong>in</strong>g ma<strong>in</strong>s water it may be useful to measure alkal<strong>in</strong>ity us<strong>in</strong>g a 100ml <strong>sample</strong> <strong>in</strong><br />
which case, the formula is adjusted to 20mg/l for each tablet value, less 10 as the correction factor.<br />
Calcium hardness is tested <strong>in</strong> exactly the same way but <strong>in</strong> this case the operator is look<strong>in</strong>g for a violet<br />
colour.<br />
Calcium hardness test us<strong>in</strong>g 50ml<br />
<strong>sample</strong>, colour change method<br />
Total dissolved solids (TDS) levels are measured us<strong>in</strong>g an electronic TDS tester. For best practice TDS<br />
levels should be ma<strong>in</strong>ta<strong>in</strong>ed no higher than 1000mg/l, higher than the <strong>in</strong>com<strong>in</strong>g ma<strong>in</strong>s water.<br />
Typical TDS tester<br />
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It is recommended that pools should be tested for chlor<strong>in</strong>e levels and pH levels:<br />
• before the pool opens to the public<br />
• every 2-3 hours dur<strong>in</strong>g the hours of operation<br />
• test<strong>in</strong>g the pool at the end of the day is also good practice<br />
The test<strong>in</strong>g protocols should be <strong>in</strong>cluded with<strong>in</strong> the normal operat<strong>in</strong>g procedures and will take <strong>in</strong>to account<br />
bather load<strong>in</strong>g, the type of the pool, the open<strong>in</strong>g hours and whether or not the pool is dis<strong>in</strong>fected via an<br />
automatic dos<strong>in</strong>g plant.<br />
A pool treated with a fully automatic dos<strong>in</strong>g plant which is work<strong>in</strong>g correctly, requires less frequent test<strong>in</strong>g<br />
than a pool which is <strong>manual</strong>ly dosed with chemicals. Pool Water Treatment Advisory Group (PWTAG)<br />
guidance should be followed <strong>in</strong> relation to this.<br />
The tests for balanced water i.e. total alkal<strong>in</strong>ity, calcium hardness and total dissolved solids would normally<br />
be carried out once per week.<br />
The importance of ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g swimm<strong>in</strong>g pool water quality<br />
If pH or chlor<strong>in</strong>e levels are out range, the pool could become unsafe.<br />
If the pH, total alkal<strong>in</strong>ity, calcium hardness or TDS levels are out of range, the pool could become<br />
unbalanced i.e. became corrosive or scale form<strong>in</strong>g.<br />
The optimum ranges for the pool water tests are as follows.<br />
Test<br />
Free chlor<strong>in</strong>e<br />
Comb<strong>in</strong>ed chlor<strong>in</strong>e<br />
Optimum range<br />
Never lower than 0.5mg/l<br />
Best <strong>in</strong>dustrial practice is based upon the m<strong>in</strong>imum use of chemicals <strong>in</strong> order to ensure<br />
bacteriological quality<br />
Normally, pool operators tend to set free available chor<strong>in</strong>e levels at 1.5mg/l for typical<br />
swimm<strong>in</strong>g pools<br />
At 5mg/l the automatic dos<strong>in</strong>g plant should be switched off<br />
At 10 mg/l or above the pool must be evacuated<br />
This should be as low as possible. Ideally, never more than 1mg/l and half the value of<br />
the free chlor<strong>in</strong>e or less<br />
pH Ideally should be ma<strong>in</strong>ta<strong>in</strong>ed between 7.2-7.4<br />
Total alkal<strong>in</strong>ity <strong>Level</strong> is determ<strong>in</strong>ed by the dis<strong>in</strong>fectant used but will be with<strong>in</strong> the overall range 80-<br />
200mg/l<br />
Calcium hardness<br />
Total dissolved solids<br />
Temperature<br />
Never lower than 75mg/l, not higher than 500mg/l<br />
Ma<strong>in</strong>ta<strong>in</strong>ed no higher than 1000mg/l, higher than the <strong>in</strong>com<strong>in</strong>g ma<strong>in</strong>s water<br />
Dependent upon activity and type of pool<br />
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Pseudomonas aerug<strong>in</strong>osa<br />
Pseudomonas aerug<strong>in</strong>osa is capable of grow<strong>in</strong>g <strong>in</strong> water even at relatively<br />
low temperatures, and they can readily form colonies of bacteria <strong>in</strong> filters.<br />
They have been associated with pool water play <strong>in</strong>flatables, plastic surfaces<br />
and pool covers. P. aerug<strong>in</strong>osa can cause sk<strong>in</strong> and ear <strong>in</strong>fections, so its<br />
presence <strong>in</strong> pool water is undesirable.<br />
Bacteriological sampl<strong>in</strong>g - <strong>in</strong>terpret<strong>in</strong>g the results<br />
In order to ensure that the pool is operat<strong>in</strong>g safely, acceptable levels for bacteria are as below.<br />
Aerobic colony count (ACC)<br />
The aerobic colony count (ACC) should normally be 10 or less colony form<strong>in</strong>g units per millilitre of pool<br />
water. If the colony count is above 10 cfu/ml, and it is the only unsatisfactory microbiological result,<br />
provid<strong>in</strong>g the residual chlor<strong>in</strong>e and pH values are with<strong>in</strong> recommended range, it is recommended that the<br />
water should be re-tested.<br />
Total coliforms<br />
Coliforms are sensitive to dis<strong>in</strong>fectant and should be absent, <strong>in</strong> other words zero, <strong>in</strong> 100 ml of pool water.<br />
A coliform count of up to 10 cfu/100 ml is acceptable provided that:<br />
1. Coliforms are not found <strong>in</strong> the repeat <strong>sample</strong>.<br />
2. The aerobic colony count is less than 10cfu/ml.<br />
3. There are no E coli present.<br />
4. The residual dis<strong>in</strong>fectant and pH values are with<strong>in</strong> recommended ranges.<br />
E. coli<br />
E. Coli should be absent (i.e. zero) <strong>in</strong> a 100millilitre <strong>sample</strong>. A s<strong>in</strong>gle positive <strong>sample</strong> may be the result<br />
of recent superficial contam<strong>in</strong>ation by a bather, which had not been dealt with by the dis<strong>in</strong>fection process.<br />
Under these circumstances a repeat <strong>sample</strong> should then be taken.<br />
Pseudomonas aerug<strong>in</strong>osa<br />
Well operated pools should not normally conta<strong>in</strong> P. aerug<strong>in</strong>osa. If the count is over 10 per 100 ml repeat<br />
the test.<br />
Where repeated <strong>sample</strong>s conta<strong>in</strong> P. aerug<strong>in</strong>osa the filtration and dis<strong>in</strong>fectant processes should be exam<strong>in</strong>ed<br />
to determ<strong>in</strong>e whether there are areas with<strong>in</strong> the pool circulation where the organism is able to multiply.<br />
Where counts exceed 50, pool closure should be considered.<br />
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