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In a previous post I demonstrated the use of a 2 liter aquarium to study carbon dosing with vinegar (acetic acid) and ethanol.
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Following the hobby protocol of weekly increases of the daily dose, nitrate was consumed as expected, even though the aquarium was not filtered nor attached to a skimmer. Ethanol dosing provided a greater reduction of nitrate than acetic acid (vinegar) on a molar basis (same number of molecules). Phosphate was also consumed at roughly 0.1 ppm per ppm of nitrate. In this post I want to share the results of the next study designed to determine how quickly nitrate is consumed after vinegar or ethanol is dosed. All experiments were performed at room temperature (20-23 C). Nitrate was measured with the Hanna low range nitrate Checker, phosphate with the Hanna low range Checker and oxygen with the Hanna oxygen test kit (modified Winkler titration).
In this study I used 150 mL BOD bottles, glass stoppered bottles designed to study oxygen consumption, instead of magnetically stirred 2 liter aquaria. The aquarium water used in the experiment was pre-dosed with either vinegar or ethanol and stirred for 24 hours to get past the lag phase in bacteria growth (a discovery for another post). The post lag phase water was then divided in half. One portion filled four BOD bottles (control), the other portion was dosed with either vinegar or ethanol before filling four additional BOD bottles (treatment). The size of the ethanol dose was scaled to obtain the same size nitrate consumption as vinegar dosed at 0.5 mL/gallon aquarium water. Here is the data.
The two charts show how quickly nitrate is consumed with either vinegar or ethanol, and equally interesting how fast oxygen is removed from the water. The good news is that oxygen consumption is smaller than what would be predicted from complete oxidation of the dose (100% respired), 7.4 ppm vs 1.5 for ethanol and 3.5 ppm for acetic acid. The table below summarizes the total consumptions of nitrate, phosphate and oxygen. To convert to ppm, multiply the entry by 62 for nitrate, 95 for phosphate and 32 for oxygen. The “organic residual”, the difference between the amount of organic dosed and the amount oxidized (calculated from the oxygen used and stoichiometry of the oxidation reaction), gives us an idea of how much of the dose could have gone into biomass. Phosphate consumption looks like it is very closely related to oxygen use.
What are the implications of this data for carbon dosing aquaria? The concern about oxygen depletion remains, especially for a vinegar doses nearing 0.75 mL/gallon where the system’s oxygen could be nearly depleted quickly. From an oxygen depletion perspective, ethanol is safer. I wonder whether oxygen depletion is one reason why coral and fish seem to be affected by carbon dosing. As for phosphate removal, about 0.1 ppm is removed with every 1 ppm of nitrate. That rate would be considered wonderful if large amounts of phosphate weren’t being released by aragonite surfaces and hiding this removal rate in aquarium carbon dosing.
What’s next? I feel that we still don’t have all the reasons for carbon dosing seeming to fail in practice. Unraveling that mystery should be fun.

Carbon Dosing A Model Aquarium
Two posts last year resulted in my interest in gaining a deeper understanding of how carbon dosing worked: @Miami Reef published the new organic carbon dosing schedule https://www.reef2reef.com/threads/new-vodka-and-vinegar-dosing-charts.1024056/ and @Randy Holmes-Farley posted a question...

Following the hobby protocol of weekly increases of the daily dose, nitrate was consumed as expected, even though the aquarium was not filtered nor attached to a skimmer. Ethanol dosing provided a greater reduction of nitrate than acetic acid (vinegar) on a molar basis (same number of molecules). Phosphate was also consumed at roughly 0.1 ppm per ppm of nitrate. In this post I want to share the results of the next study designed to determine how quickly nitrate is consumed after vinegar or ethanol is dosed. All experiments were performed at room temperature (20-23 C). Nitrate was measured with the Hanna low range nitrate Checker, phosphate with the Hanna low range Checker and oxygen with the Hanna oxygen test kit (modified Winkler titration).
In this study I used 150 mL BOD bottles, glass stoppered bottles designed to study oxygen consumption, instead of magnetically stirred 2 liter aquaria. The aquarium water used in the experiment was pre-dosed with either vinegar or ethanol and stirred for 24 hours to get past the lag phase in bacteria growth (a discovery for another post). The post lag phase water was then divided in half. One portion filled four BOD bottles (control), the other portion was dosed with either vinegar or ethanol before filling four additional BOD bottles (treatment). The size of the ethanol dose was scaled to obtain the same size nitrate consumption as vinegar dosed at 0.5 mL/gallon aquarium water. Here is the data.
The two charts show how quickly nitrate is consumed with either vinegar or ethanol, and equally interesting how fast oxygen is removed from the water. The good news is that oxygen consumption is smaller than what would be predicted from complete oxidation of the dose (100% respired), 7.4 ppm vs 1.5 for ethanol and 3.5 ppm for acetic acid. The table below summarizes the total consumptions of nitrate, phosphate and oxygen. To convert to ppm, multiply the entry by 62 for nitrate, 95 for phosphate and 32 for oxygen. The “organic residual”, the difference between the amount of organic dosed and the amount oxidized (calculated from the oxygen used and stoichiometry of the oxidation reaction), gives us an idea of how much of the dose could have gone into biomass. Phosphate consumption looks like it is very closely related to oxygen use.
What are the implications of this data for carbon dosing aquaria? The concern about oxygen depletion remains, especially for a vinegar doses nearing 0.75 mL/gallon where the system’s oxygen could be nearly depleted quickly. From an oxygen depletion perspective, ethanol is safer. I wonder whether oxygen depletion is one reason why coral and fish seem to be affected by carbon dosing. As for phosphate removal, about 0.1 ppm is removed with every 1 ppm of nitrate. That rate would be considered wonderful if large amounts of phosphate weren’t being released by aragonite surfaces and hiding this removal rate in aquarium carbon dosing.
What’s next? I feel that we still don’t have all the reasons for carbon dosing seeming to fail in practice. Unraveling that mystery should be fun.