NO3 18.77, PO4 .18
Not sure where the PO4 average of 0.18 comes from. Even using the high end of any value shown as ranges I only come up with an average of 0.094.
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NO3 18.77, PO4 .18
Not sure where the PO4 average of 0.18 comes from. Even using the high end of any value shown as ranges I only come up with an average of 0.094.
What do they mean ratio below 29? 29 what? Whats the ratio cyano favor?
do those numbers really average out to .18 on po4?here are the "MASTERS" of reefing average numbers:
Alk was 8.19, Ca 419. Mg 1361, NO3 18.77, PO4 .18, Sr 8.6 and temp 77
Masters included are:
Julian Sprung of Two Little Fishes NO3 10-15, PO4 .015
front tank WWC NO3 10-15, PO4 .03-,08
Julian and Cruz of Elegant Corals NO3 5, PO4 .05
Stuart Bertram NO3 15-20, PO4 .046
Jeff Leung NO3 54, PO4 .04
Brad Syphus NO3 20, PO4 .10-.20
Jason Fox NO3 5-10, PO4 .08-.10
Dr. Sanjay No3 20-40, PO4 .12-.22
All credit to @Mike Paletta and this orignal thread at: https://www.reef2reef.com/threads/tank-parameters-of-some-masters.295215/
did you hack my apex and see my test results? and my tank? lol my cyano is finally gone because I've increased my nitrate dosing recently. I didnt even realize it was happening because of ratio between these nutients. Cool stuff.Nitrogen / Phosphorus ratio. But the main point here is not about specific numbers...
Since we do not have very specific targets, Nitrate / Phosphate ratio serves as a reasonable guide. The older studies actually used that.
My personal belief is not actually to chase a ratio nor specific numbers. Just take them as a guide to understand things. If the reef goes well just forget it.
There goes a practical example:
Nitrates always around 0.5 and phosphates around 0.08. You keep having cyano problems. Phos seems ok but actually a bit unbalanced.
In that case you can lower more your phosphates and maybe considering raising nitrates a bit to get a better ratio (been there and done that). You will see a bit of green algae proliferation with cyano reduction with time...
My bold and Nitrate is NO3, Phosphate is PO4
I do not know where you get ppb from - I read @Thales post as it is ppm both values and I do my calculation like this
NO3 molar weight is 14 +3*16 = 62. NO3-N will be 14/62 = 0,225 = 22,5 %
50 ppm NO3 will be 50 * 0.225 = 11.25 ppm as NO3-N
PO4 molar weight is 31+4*16 = 95 P will be 31/95 = 0.326 = 32,6 %
0,91 ppm PO4 will be 0.91*0.326 = 0.296 ppm as PO4-P
11,25/0.296 = 38 N/P ratio
Yes if @Thales meant ppm in his post - your wrong. and only he can thale if its wrong assumption of me or not
Sincerely Lasse
Did you lost all of your macros? I would not be surprised if the "micro algae" in your pictures in reality are cyanobacteria - not the mat forming type - just an other form.To enrich the discussion, it is what happened in my fuge in a 2 month period while dosing nitrates raised from 0 to 3 and lowered phosphate from 0.26 to 0.05.
Don’t worry about this algae, there’s none on my display this works as an open ATS...
Did you lost all of your macros? I would not be surprised if the "micro algae" in your pictures in reality are cyanobacteria - not the mat forming type - just an other form.
Sincerely Lasse
Thank you for the big post. I want to recognize your effort to synthesize the “big picture” on this hot topic. I appreciate the title.Paulo Mallard Scaldaferri, João Carlos Basso, Marcos Augusto Bizeto, Miguel Mies, Roberto Denadai, Junio Melo
Introduction
Possible applications of the Redfield ratio in the management of the marine aquarium have been discussed over the year. Many have considered that knowledge very helpful while others consider it completely dismissible and useless to the reef keeping hobby. Our objective with this systematic literature review was to obtain the best information that could help clear this concept in terms of aquarium reef keeping.
It has been stated in the past that the well-known 106: 16: 1 carbon : nitrogen : phosphorus ratio should be aimed in order to keep a healthy aquarium. It has been suggested that it would prevent nuisance algae and cyanobacteria by many respected authors like Julian Sprung (1) and João Carlos Basso (2) among others (3). However, many hobbyists have questioned the actual usefulness of these predictions and possible corrections.
Origins
In 1934 Alfred Redfield published a widely known study (4) comparing the rates of oceanic organic compounds collected on the path of the "Dana" ship, between 1928 and 1929. Samples were obtained on the surface, and at depths of 700 and 1500 meters. The original publication identified the stoichiometric N : P ratio of 20:1, offering a light on a possible balance between these components in the ocean. In 1958, the same author (5) based on new published data recognized that a new C: N: P ratio of 106:16:1 was obtained and these are the numbers often referenced in our hobby.
A more recent and larger study (6) was made with extensive data collection (5336 distinct oceanic points). It showed a significant variation in ratios among different sites and revealed a more accurate global average for this relationship: 163:22:1. There was found a significant variation of rations between different sites.
The marine aquarium community has been using information from the original study to keep a healthier environment within the tanks. However, applicability of the original study values is very questionable since it was carried out in ocean waters.
The new interpretations of the N : P ratio
Every day more and more nitrogen-fixing organisms are studied and different N : P gradients have been identified in the nature and tested in laboratory (7). Different species benefit differently from various N : P ratios. Mathematical models have been developed to predict the prevalence of microorganisms where limiting factors are nitrogen, phosphorus or both (8).
A large number of studies include analysis of the carbon component of this equation. In order to simplify our focus, I will report more frequently the data specifically on the N : P ratio. These are the most available and practical parameters to the marine hobbyist (we usually use nitrates and phosphate tests, which are quite representative of the N: P ratio in the water column).
Could a ratio of nutrients really promote or limit the prevalence of different microorganisms in marine aquariums? Apparently yes, but it is not as simple as we previously thought.
Let's look at the biochemical basis for the different demand and composition of N : P (8). The largest pool of N is present in proteins and nucleic acids. It is also present in chlorophylls a, b, c and amino acids, and appears in diatoms chitin. In contrast, nucleic acids and phospholipids are the largest pool of P and it is less present in proteins. The main macromolecule that makes up for the cellular content in phosphate is the RNA.
But it is even a little more complex than that. Cyanobacteria have a high N: P cell ratio (> 25) comparing to most other eukaryotic microorganisms due to their significantly bulky light uptake apparatus (9). In contrast, other genera of eukaryotic phytoplankton such as green algae, diatoms and dinoflagellates have a higher content of phosphate. Evaluating just the cellular content of cyanobacteria, a high demand for nitrogen would be expected, but studies have shown exactly the opposite. Through repeated observation, it was hypothesized that cyanobacteria could supplement N deficiency with diazotrophic N2 fixation capacity (10). This N2 fixation capability also offers a better explanation for the competitive advantage of cyanobacteria over other microorganisms in nitrogen-deprived environments.
Relationships between N: P ratios and cyanobacteria
The unbalanced proliferation of cyanobacteria in estuarine and marine waters have been related to environments rich in nutrients, but lacking the N fraction of this equation. Smith has already verified in his studies that the N : P ratio below 29 favored the proliferation of cyanobacteria, which were more efficient in fixing N (11, 12).
Cyanobacteria are ubiquitous in marine aquariums, but their excessive proliferation is considered very problematic. Usually, some species are more prevalent in aquariums such as Oscillatoria , Lyngbya and Phormidium (3, 13, 14). Like other marine planktonic microorganisms, after an accelerated growth, cyanobacteria also develop a competitive advantage through secretion of allelopathic substances. These substances can inhibit the growth of other algae and cyanobacteria (15), even evidencing antimicrobial properties. This observation may partially explain the success of cyano treatment with macrolides, such as azithromycin or erythromycin. Other drugs from this group (macrolides) have already been isolated from different cyanobacteria (16). Could their mechanism of action have any similarity to allelopathy? Although it is interesting, we have not identified specific studies to verify the veracity of this hypothesis.
The initial imbalance that leads to accelerated cyano growth seems to be influenced by the N: P ratio. Ahlgren tested this hypothesis in closed environments, which we could call small aquariums (0.5L glass tubes). The researcher evaluated the proliferation of Oscillatoria agardhii in environments with limited nitrogen or phosphorus (17). He observed that in the studied species phosphorus depletion was a greater growth limit factor than nitrogen, evidencing a competitive advantage in nitrogen deprived environments. Levich (18) also studied the proliferation of cyanobacteria in detriment of other microorganisms with various N : P ratios and found very interesting balances: above 20 : 1 green algae was favored; on the other hand, cyano grew more rapidly in ratios below 5 : 1.
Implications of N : P ratios in carbon dosing
Carbon dosing is a widely used technique by marine aquarists for nutrient export and nitrate and phosphate reduction. Several carbon sources have already been tested such as sugar, vodka and vinegar. Principles of carbon dosing also seem to be explained with C : N : P ratio knowledge. Addition of carbon provides the limiting growth factor for the aquarium's bacterial population. Through this incorporation, bacteria also consume nitrate (in greater proportion) and phosphate, being later exported by the skimmer.
We also identified some studies (19) that investigated the C : N : P in these bacteria and found a ratio of 50 : 10 : 1. Exponential growth of marine bacteria in vitro was achieved when the ratio reached 32 : 6.4 : 1 in nitrogen rich and 45 : 7.4 : 1 in nitrogen poor environments.
In other words, we could expect in aquariums that the maximum export efficiency would theoretically occur in a ratio of 7 : 1 (N : P) and the expected theoretical result of consumption would occur in a ratio of 10 : 1 (N : P). This proportion was not the same in every single study, but it is closer to reality than the original Redfield (20).
Once nitrogen or phosphorus is eliminated, normally the increase in carbon supply will not remove the other residual element. Sometimes, over-dosing may stimulate the development of cyanobacteria, which can be well understood by the mechanism already mentioned: after removing the nitrogen source, cyanobacteria and others capable of fixing gaseous nitrogen (N2) could be stimulated.
Final considerations
We know that marine aquariums are closed environments with very diverse micro and macro fauna, and interpretation of this closed environment through studies carried out in nature is extremely complex. Alfred Redfield's initial studies were conducted in open waters, far away from coral reefs, so we discourage that the original Redfield ratio be taken as a rule for marine hobbysts. However, we identified the importance of his initial studies of C: N: P relationships, which were followed by the identification of new ratios in different environments.
However, many studies have demonstrated that different species usually preponderate under specific conditions. So we can check that the predominance of certain species with accelerated growth in marine aquariums seems to be influenced by the C : N : P ratio.
Higher N: P ratios (above 20 : 1) seem to favor green algae, while lower values (below 5 : 1) favor the growth of cyanobacteria. In situations where there is a critical limit in nutrients supply (a large reduction of both N and P), this interpretation seems to have less predictive value.
We must emphasize the limitations of these information and implications. The well-known imprecision of the tests that we usually use in the hobby demands that critical judgment should be used above all. Redfield did not predict with his studies events that occur in aquariums, neither it was his intention, but other studies already published seem to increasingly offer data that can help us manage marine aquariums. We believe that dissemination of this data may provide new horizons on nitrogen, phosphorus and carbon dynamics in aquariums.
Bibliography
1. Dellbeek JC, Sprung J. The Reef Aquarium: A Comprehensive Guide to the Identification and Care of Tropical Marine Invertebrates. 3: Two Little Fishies, Inc.; 1994. p. 274-5.
2. Basso JC. In: Aquaribasso, editor. O Aquário de Recife de Corais. 2017. p. 45.
3. Knop D. Algues en aquarium. Les guides Zebras. 2010:59-63.
4. Redfield AC. On the proportions of organic derivatives in sea water and their relation to the composition of plankton. James Johnstone Memorial. 1934;176:176-92.
5. Redfield AC. The Biological Control of Chemical Factors in the Environment. American Scientist. 1958;46(3):230A-21.
6. Martiny AC, Vrugt JA, Lomas MW. Concentrations and ratios of particulate organic carbon, nitrogen, and phosphorus in the global ocean. Scientific Data. 2014;1(1):140048.
7. Gruber N, Deutsch CA. Redfield's evolving legacy. Nature Geoscience. 2014;7(12):853-5.
8. Geider R, La Roche J. Redfield revisited: variability of C : N : P in marine microalgae and its biochemical basis. European Journal of Phycology. 2002;37(1):1-17.
9. M B, M S. Factors affecting the growth of cyanobacteria with special emphasis on the Sacramento-San Joaquin Delta.: Southern California Coastal Water Research Project; 2015.
10. Parrish J. The Role of Nitrogen and Phosphorus in the Growth, Toxicity, and Distribution of the Toxic Cyanobacteria, Microcystis aeruginosa. Master's Projects and Capstones: University of San Francisco; 2014.
11. Smith VH. Low Nitrogen to Phosphorus Ratios Favor Dominance by Blue-Green Algae in Lake Phytoplankton. Science. 1983;221(4611):669-71.
12. Smith VH. Nitrogen, phosphorus, and nitrogen fixation in lacustrine and estuarine ecosystems. Limnology and Oceanography. 1990;35(8):1852-9.
13. Sprung J. Algae: A Problem Solver Guide: Two Little Fishies; 2001.
14. Nienaber MA, Steinitz-Kannan M. A guide to cyanobacteria: identification and impact: Univeristy Press of Kentucky; 2018.
15. Chauhan VS, Marwah JB, Bagchi SN. Effect of an antibiotic from Oscillatoria sp. on phytoplankters, higher plants and mice. New Phytologist. 1992;120(2):251-7.
16. Wang M, Zhang J, He S, Yan X. A Review Study on Macrolides Isolated from Cyanobacteria. Mar Drugs. 2017;15(5):126.
17. Ahlgren G. Growth of Oscillatoria agardhii in Chemostat Culture: 1. Nitrogen and Phosphorus Requirements. Oikos. 1977;29:209.
18. Levich AP. The role of nitrogen-phosphorus ratio in selecting for dominance of phytoplankton by cyanobacteria or green algae and its application to reservoir management. Journal of Aquatic Ecosystem Health. 1996;5(1):55-61.
19. Vrede K, Heldal M, Norland S, Bratbak G. Elemental Composition (C, N, P) and Cell Volume of Exponentially Growing and Nutrient-Limited Bacterioplankton. Applied and Environmental Microbiology. 2002;68(6):2965-71.
20. Chrzanowski TH, Kyle M. Ratios of carbon, nitrogen and phosphorus in Pseudomonas fluorescens as a model for bacterial element ratios and nutrient regeneration. Aquatic Microbial Ecology - AQUAT MICROB ECOL. 1996;10:115-22.
[/QUOTE]And why do we assume we have a cyanobacteria, a diatom or A dinoflagellate problem instead of a local ecological problem started by bacteria growth which made the isolated area friendly to cyanobacteria, diatoms or dinoflagellates? For one thing we can measure a nitrate concentration but not a bacteria colony.
Eppur si muove
Thanks for your reply. I thought my “tweaking“ comment might entice you to replyMay I use a old quote?
In this case - tweaking the NO3 and PO4 concentrations in the water column is still the most effective way to handle all of these three photosynthetic organisms when they form monocultures.
Sincerely Lasse
Thanks for your reply. I thought my “tweaking“ comment might entice you to reply
On this topic, I remain a skeptic. Anecdotal data and uncontrolled experiments are just hard for me to accept as evidence. Also, these organism growths are unlikely to be “monocultures”. The monoculture notion is an assumption, possibly supported by casual microscopy observations, but still an assumption.
Respectfully,
Dan
Understand that - but you will maybe also understand why I´m sceptical to statements that´s not even is based on anecdotal data - just based on a statement that x and y may not act that way - they must act in this way.Anecdotal data and uncontrolled experiments are just hard for me to accept as evidence.
Of course! I totally understand where you are coming from.Understand that - but you will maybe also understand why I´m sceptical to statements that´s not even is based on anecdotal data - just based on a statement that x and y may not act that way - they must act in this way.
Sincerely Lasse
Of course! I totally understand where you are coming from.
What sort of experiment could we set up to test the notion that NO3 and PO4 level adjustments actually alter microorganism populations?
How could we possibly create 6 identical systems with nuisance organism growth, 3 would receive no intervention, 3 would receive our best estimate for the right level of NO3 and PO4 adjustment? Basically, how do we reproducibly create a cyanobacteria, diatom or dinoflagellate bloom in six small containers at the same time with roughly the same size bloom, maybe in 5-20 liters of water? Or would it be smarter to create a large bloom and divide it in 6 equal parts for the study?
Dan
It is impossible - and you know it. It is like saying that Colombus should have taken an airplane around the world in order to find another way to India.How could we possibly create 6 identical systems with nuisance organism growth, 3 would receive no intervention, 3 would receive our best estimate for the right level of NO3 and PO4 adjustment? Basically, how do we reproducibly create a cyanobacteria, diatom or dinoflagellate bloom in six small containers at the same time with roughly the same size bloom, maybe in 5-20 liters of water? Or would it be smarter to create a large bloom and divide it in 6 equal parts for the study?