Bioactive and cyanuric acid loss or degradation over winter

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^I was thinking the other way around, the mineralization or oxidation of organics and CYA until it stops when the O2 runs out as it turns anaerobic. But its been studied quite extensively and is due to the anaerobic degradation by facultative anaerobic bacteria using the CYA as a carbon, nitrogen and energy source.

Here it is.

CYA Degradation by Bacteria

Degradation of Cyanuric Acid (CYA))

This thread explores some of the ways that Cyanuric Acid (CYA) can degrade since many users report seeing CYA drop under various conditions.

CYA Degradation by Bacteria

Some pool users find that their CYA levels drop over the winter when their pool is let go (i.e. no chlorine added). Many of these pools have algae, but some do not. The degradation pathway for CYA by some bacteria and fungi (normally under anaerobic conditions) is well understood and described here (an early article describing the degradation but incorrectly attributing urea as an intermediate is in this paper while the correct pathway is described in this paper). In summary, it is the following:

CYA + 2H2O --> Biuret + H+ + HCO3-
Biuret + H2O --> Allophanate- + NH3 + H+
Allophanate- + H+ + H2O --> 2NH3 + 2CO2

so the net result is:

CYA + 4H2O --> H+ + HCO3- + 3NH3 + 2CO2
Cyanuric Acid + Water --> Hydrogen Ion + Bicarbonate Ion + Ammonia + Carbon Dioxide

For every mole of CYA, 3 moles of ammonia are produced. This is equivalent to 10 ppm CYA producing 3.26 ppm ammonia (measured as ppm Nitrogen). Sometimes the ammonia will dissipate (probably outgas or get consumed by algae) over time, but any leftover ammonia would appear as unusual chlorine demand upon opening and take a LOT of chlorine to get rid of. For every 10 ppm CYA that is degraded and produces around 3 ppm ammonia, it would take nearly 30 ppm cumulative FC to get rid of (see this thread and this thread). One can buy an inexpensive ammonia test kit from a pet/fish/aquarium store.

Because ammonia has an equilibrium with ammonium cation (NH4+) with a pKa of around 9.2 in pool water (accounting for ionic strength), the net result is that the pH rises from the above reaction of CYA degradation as shown below (and the pH actually goes up even more than shown since the primary starting species is cyanurate ion):

CYA + 6H2O --> 2OH- + HCO3- + 3NH4+ + 2CO2
Cyanuric Acid + Water --> Hydroxyl Ion + Bicarbonate Ion + Ammonium Ion + Carbon Dioxide

Some of the carbon dioxide may dissolve in the water to form carbonic acid so if that occurred completely then the following would be the result:

CYA + 6H2O --> 3HCO3- + 3NH4+
Cyanuric Acid + Water --> Bicarbonate Ion + Ammonium Ion

In the above situation, the pH does not change very much, perhaps rising some since the starting species is actually cyanurate ion, not CYA as shown. The TA rises as well.

H2CY- + 7H2O --> 3HCO3- + 3NH4+ + OH-
Cyanurate Ion + Water --> Bicarbonate Ion + Ammonium Ion + Hydroxyl Ion

[EDIT]
This paper and this paper describe some of the anaerobic conditions and rates for oxidation of CYA into carbon dioxide and ammonia. Under certain conditions, there are two mechanisms by which bacteria can further oxidize ammonia or ammonium ion. The first is nitrification which is an aerobic process (i.e. requiring oxygen) with two types of bacteria with the following examples shown to produce nitrate (the Nitrosomonas bacteria in the first reaction can also use ammonium ion):

Nitrosomonas Bacteria: 2NH3 + 3O2 --> 2NO2- + 2H+ + 2H2O
Nitrobacter Bacteria: 2NO2- + O2 --> 2NO3-

The second is an oxygen-limited autotrophic nitrification-denitrification (OLAND) which combines the nitrification of nitrosomonas bacteria (above) or other sources of nitrite or nitrate with subsequent denitrification under anaerobic conditions. Nitrate and nitrite are used in place of oxygen for metabolic processes. Three conditions are required for significant denitrification: low oxygen, high nitrate concentration, and a supply of organic carbon. Pseudomonas aeruginosa is an example of denitrifying bacteria. The following are half-reactions where the other half is the oxidation of organic material.

NO3- + 2H+ + 2e- --> NO2- + H2O
NO2- + 2H+ + e- --> NO + H2O
2NO + 2H+ + 2e- --> N2O + H2O
N2O + 2H+ + 2e- --> N2 + H2O

There is also anaerobic ammonium oxidation (annamox) to produce nitrogen gas.

Annamox Bacteria: NH4+ + NO2- --> N2(g) + 2H2O

So each stage of bacterial degradation after the initial one to create ammonia lowers the chlorine demand as follows.
10 ppm CYA --> 3.07 ppm Ammonia nitrogen --> 24-30 ppm FC chlorine demand left to oxidize ammonia
3.07 ppm Ammonia nitrogen --> 3.07 ppm Nitrite nitrogen --> 16 ppm FC chlorine demand left to oxidize nitrite
3.07 ppm Nitrite nitrogen --> 3.07 ppm Nitrate nitrogen --> 0 ppm FC chlorine demand left
3.07 ppm Nitrite or Nitrate nitrogen --> Nitrogen gas --> 0 ppm FC chlorine demand left

So while the Nitrosomonas bacteria somewhat reduce the chlorine demand, it is the combination of that bacteria with Nitrobacter or with denitrifying bacteria or annamox bacteria that reduce the chlorine demand to zero. Of course, there will still be some chlorine demand from needing to oxidize the bacteria itself.
[END-EDIT]

CYA Degradation by Oxidation from Chlorine

Though the above can explain a loss of CYA when bacteria are allowed to grow, such as when chlorine is not added over the winter, it does not explain why some pools also experience a loss of CYA over the summer or during other times when chlorine is present and bacteria should not be growing. There is oxidation reaction of Cyanuric Acid by Hypochlorite Ion described by John A. Wojtowicz in the Journal of the Swimming Pool and Spa Industry (JSPSI) Volume 4, Number 2, pp. 23-28 (2001) reprinted in "The Chemistry and Treatment of Swimming Pool and Spa Water" in Chapter 5.3 "Oxidation of Cyanuric Acid with Hypochlorite". [EDIT] This is now available online here. [END-EDIT]

2(HNCO)3 + 9ClO- ---> 3N2 + 6CO2 + 9Cl- + 3H2O
Cyanuric Acid + Hypochlorite Ion --> Nitrogen Gas + Carbon Dioxide + Chloride Ion + Water

[EDIT] On a molar basis, 4.5 chlorine oxidize 1 CYA. On a ppm basis this is 2.47 ppm FC for every 1 ppm CYA. [END-EDIT]

The primary step is the cleavage of the triazine ring and it is proposed by Wojtowicz that this primarily involves a fully chlorinated isocyanurate species Cl2CY-. The decomposition was first order with respect to average chlorine and increased with pH. The decomposition rate was a decrease in Free Chlorine at a rate of 0.0147 per hour or 1-EXP(-0.0147*24) = 30% per day while the calculated rate of loss of CYA at 4 ppm FC was 0.87 ppm per day [EDIT] (I get 4*0.30/2.47 = 0.49 ppm CYA per day) [END-EDIT], but that was at FC/CYA ratios (in ppm units) of 0.34 (close to shock levels) whereas the more typical ratio in our pools is around 0.1. His experiments at lower FC/CYA ratios of 0.029 with 4 ppm FC and 138 ppm CYA showed a lower CYA decomposition rate of 0.24 ppm/day which is a factor of 3.6 lower. At 4 ppm FC and 11.76 ppm CYA (a ppm ratio of 0.34), the concentration of Cl2CY- (at temp 85F) is a factor of 9.9 higher while HClCY- is a factor of 6.9 higher than the concentrations at 4 ppm FC and 138 ppm CYA which might mean that HClCY- is the rate-critical species that degrades (this is speculation on my part). In another paper "Effect of Cyanuric Acid on Swimming Pool Maintenance" (in the same JSPSI collection), Wojtowicz describes a chlorine loss rate due to oxidation of CYA at 12.5% per day at 85F which is roughly consistent with a 30%/3.6 = 8.3% rate especially since his 12.5% number came from FC levels starting higher (5.4 ppm for indoor pools, 7.6 to 9.2 ppm for outdoor pools). So, assuming a CYA loss rate of around 0.4 ppm/day in our pools this comes to 12 ppm per month which is clearly enough to be noticeable as the months pass during a swim season. If one shocks the pool, then the rate of loss could be about 2-3 times faster.

Wojtowicz also shows a strong temperature dependence on the chlorine oxidation of cynauric acid where every 10F increase in temperature results in roughly doubling the rate of degradation. So his data was with pools at 85F so pools at 90F could have degradation rates about 1.4 times higher.

The thing is that some of what Wojtowicz has seen does not seem to be consistent with some of what we have seen in our own pools, especially with regard to chlorine loss rates. Wojtowicz implies that there is little breakdown from sunlight of the chlorinated isocyanrates -- that only hypochlorous acid and especially hypochlorite ion are affected. Yet the experiments mas985 (Mark) made showed that higher levels of CYA did protect chlorine better in a non-linear way in sunlight and he did not see losses overnight (that is, without sunlight) which Wojtowicz saw in indoor pools. My own pool is at 86-90F and is exposed to sunlight 1-2 hours most days (it has an opaque electric safety cover on most of the time) and about a 1 ppm FC per day loss which includes use of the pool (1 person bather load most days). The rate of chlorine loss from oxidation of CYA is, in ppm units, about 2.5 times higher so even if I assume 1 ppm FC loss per day all oxidizing CYA, that would be 0.4 ppm CYA loss per day or 12 ppm per month. I should be able to measure that as I started with 30 ppm CYA when I opened and added more CYA around April/May. [EDIT] I just measured my pool's CYA level and it's a little above 25 ppm so even attributing a 5 ppm CYA drop over 3 months, that's pretty low and could be explained by the error tolerance of the test or some by splash-out (I have an oversized cartridge filter that is only cleaned once a year so the only dilution is from splash-out). It's certainly not near 12 ppm per month of loss. [END-EDIT]

So I can see that it is possible for CYA to degrade slowly over time in pools that are at higher temperature or at higher FC/CYA ratios such as extensive periods of shocking. The inconsistency is in how much degradation is occurring from sunlight vs. oxidation from chlorine.

CYA Degradation by Hydroxyl Radicals From Chlorine Breakdown in Sunlight

As described in this post, when chlorine (hypochlorous acid or hypochlorite ion) breaks down in sunlight, hydroxyl radicals are produced. This paper describes why CYA is not broken down quickly by hydroxyl radicals, but this paper demonstrates that CYA is broken down by hydroxyl radicals (though not via titanium dioxide because adsorption is required to be close to such radical generation). So it is possible that CYA is broken down slowly in pools exposed to sunlight. Some report rates of around 10 ppm CYA per month which is higher than the roughly 2-3 ppm CYA per month seen in pools not exposed to sunlight (or the 5 ppm CYA per month seen in hot spas) which would be the degradation rate from chlorine oxidation of CYA.

Richard
 
Re: My bio active experiment

I do agree with you on the stuff not doing much if anything but I know my pool and 1 gallon of bleach has never raised my FC this much.I will definitely say that if you need to drop cya significantly thend I think the best thing would probly be drain and fill. I can't speak for those that have cya that is only slightly elevated

Hi Barnns1, from what I can tell it doesn't appear you had any success with the bio active product. I would agree with Leebo that your higher than usual bleach use at the end of it is most likely due to an active algae bloom in the making. Agreed, the easiest method for CYA removal would be a drain and fill but if pucks and powdered bleach containing CYA were avoided in the first place even that shouldn't be necessary. However after going through the patent and the journal articles left by chem geek I'm convinced that theoretically the product could work and the pools that lose CYA over winter support this, both are the degradation of cyanuric acid by facultative anaerobic bacteria. But for the bio active product to have any chance of working a pool needs to be maintained at near full algae bloom conditions which goes against everything most pool owners do.

From the patent the bio active product is a mix of 7 viable species of Bacillus sp. and Lactobacillus sp. which are all facultative anaerobic bacteria meaning that they can survive with or without oxygen by changing their mode of respiration from aerobic (with oxygen) to anaerobic (without oxygen or low oxygen) where anaerobic respiration uses cyanuric acid as a carbon, nitrogen and energy source.

The patent covers a wide variety of uses for their product and the MSDS sheet suggests that it contains 1.0% - 0.1% of viable colony forming bacteria or non-viable bacteria cells that confer some enzymatic properties. 1.0% - 0.1% to me is a low to very low amount of 'active' ingredient. An end user could get lucky and get 1.0% but in order for the small volume of viable cells to be viable the right conditions for growth must be maintained, too much FC and you'll likely get nothing.

There is also a discrepancy in the patent that states for pool use, "[0096] The microbial composition from Example 5 is dissolved in water at a concentration of 100 g dried microbial product/liter. With the pump off, the microbial solution is poured into the filter unit of a residential swimming pool having a noticeable scum layer on the surface and allowed to stand for 1 hour before the pump is turned-on. Within 24 hours the scum is significantly reduced and in 48 hours there is no visible scum remaining." The patent does not say anywhere that the product can be used specifically for the removal of cyanuric acid.

The journal articles indicate that the bacteria involved in the degradation of cyanuric acid are facultative anaerobic bacteria of soil, sewage, mammalian intestinal tract or fermented plant origin, so it is likely that these bacteria could be found in a pool, blown in by the wind. The environment required is not completely anaerobic or totally void of oxygen, 1-3ppm oxygen, 3.5% sodium chloride and temperatures of both 4oC and 15oC were quoted which could easily be that of a pool closed down over winter. Degradation of CYA from microbial facultative anaerobes produces ammonia and CO2 which is exactly what is seen in the pools over winter.
 
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