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Manage pH Cycles To Maintain Animal Health

Manage pH Cycles To Maintain Animal Health
Author: Claude E. Boyd
Publish date: Friday. May 5th, 2017

pH levels in ponds are affected by such factors as time of day, vegetation and aeration activity.

Summary:

Waters with lower pH are acidic and those of higher pH are basic. The ideal pH for most aquaculture species is between 6.0 and 8.5. Lower pH values may result in decreased growth and survival, and greater susceptibil-ity to disease. pH typically is lowest in the early morn-ing, increases during the afternoon and declines at night. The most accurate way to measure pH is in situ with an electronic pH meter.

Pure water ionizes equally into hydrogen ions and hydroxyl ions. If the concentration of hydrogen ion increases, the concen-tration of hydroxyl ion must decrease and vice versa. Water is acidic if its hydrogen ion concentration is greater than its hydroxyl ion concentration and basic (alkaline) if the opposite is true. Of course, pure water is neutral – neither acidic nor basic.

To avoid the expression of very small concentrations of hydrogen and hydroxyl ions, it is customary to use the pH or negative log of the hydrogen ion concentration as a surrogate for the concentration. The negative logarithm of 10-7 molar, the hydrogen ion concentration of pure water, is 7. This pH is the middle or neutral point of the pH scale.

Waters with lower pH are acidic and those of higher pH are basic. Hydrogen ion concentration increases tenfold for each unit decrease in pH because the scale is logarithmic. For example, hydrogen ion concentrations at pH 6, 5 and 4 are 10, 100 and 1,000 times greater, respectively, than at pH 7. The converse is true for hydroxyl ion con-centration.

Natural Water pH

The pH of natural waters usually is between 5.0 and 9.0, but lower and higher values sometimes occur. Rainwater normally has a pH around 5.6, because it is saturated with carbon dioxide that has an acidic reaction in water. Lower pH may occur in rainwater because of air pollution – especially con-tamination of the atmosphere with sulfur compounds from the combustion of fossil fuels that oxidize to form sulfuric acid.

Sulfides in some soils and geological formations oxidize to form sulfuric acid that results in highly acidic conditions (pH 2 to 4) in water that contacts the formations. Highly leached soils are deficient in bases, and water in contact with them will have low alkalinity and pH as low as 5. Waters with high concentra-tions of humic substances also can have similarly low pH.

Soils may contain basic substances such as limestone, calcium silicate and feldspar that dissolve to increase alkalinity and pH in water. The pH of water tends to increase with greater alkalinity and total dissolved solids. Waters in arid and semi-arid regions typically have pH above 7.5 or 8.0. Normal seawater also has a pH near 8.0.

Acidity, Basicity

It is important to distinguish between acidity and basicity or alkalinity as defined by the pH scale (Figure 1) and the water quality variables mineral acidity, total acidity and total alkalinity (Figure 2). Carbon dioxide normally cannot lower the pH of water below 4.5, and waters with a pH lower than this are said to contain mineral acidity – usually sulfuric acid. Carbon dioxide exists in water up to pH 8.3, so water with pH between 7.0 and 8.3 contains acidity even though it is basic on the pH scale. 

The alkalinity of water results from titratable bases in a sample – mainly bicarbonate and carbonate. Bicarbonate can occur in water down to pH 4.5, so water with a pH between 4.5 and 7.0 contains alkalinity despite the fact that it is acidic on the pH scale. Carbonate does not occur in water until the pH rises above 8.3. The alkalinity serves to buffer water against pH change, and a portion of the carbon in bicarbonate is available to plants for use in photosynthesis.

Aquaculture, pH Fluctuations

The ideal pH for most aquaculture species is between 6.0 and 8.5 (Figure 1). Lower pH values may result in slower growth, poorer survival and greater susceptibility to disease in aquaculture species. Brief daily excursions of pH above 8.5 are common in ponds and apparently do not harm aquaculture species. However, long-term exposure to pH of 9.0 or above will have effects similar to those of suboptimal pH. The acid and death points for most species are pH 4 and pH 10, respec-tively.

Daily fluctuations in pH in ponds result from the net removal of carbon dioxide by plants for use in photosynthesis during the day and the release of carbon dioxide into the water at night by respiration. Because carbon dioxide has an acidic reaction, pH typically is lowest in the early morning. It increases to a maximum during the early afternoon and declines at night (Figure 3). Large daily pH fluctuations are favored by dense phytoplankton blooms and low-alkalinity, weakly buffered water. Aquaculture ponds typically have denseplankton blooms, so they should be limed if total alkalinity is lower than 50 mg/L.

Daytime pH is often highest in well-illuminated surface water, where photosynthesis is more rapid than in deeper water. The exception is clear water with underwater aquatic weed infes-tations where pH is greater within the weed beds. Of course, mechanical aeration in aquaculture ponds mixes the water col-umn and often prevents depth-related differences in pH from developing.

When pH rises above 8.3, no free carbon dioxide will be present, but plants can obtain inorganic carbon for photosynthe-sis from bicarbonate. Removal of carbon from bicarbonate results in the release of carbonate ions into water, and carbonate hydro-lysis causes pH to rise further.

In most waters, there is sufficient calcium to limit the car-bonate concentration through calcium carbonate precipitation that tempers pH increases. However, in water with low calcium but high total alkalinity concentrations, pH values of 11 or more can occur in the afternoon. Liming materials do not dissolve well in such waters, but calcium sulfate (gypsum) can be applied to increase calcium concentration.

A major reason for a decline in alkalinity in an aquaculture system is nitrification. Ammonia nitrogen – the major nitroge-nous waste of aquatic animals – is oxidized to nitrate by denitri-fying bacteria. The resulting hydrogen ions neutralize alkalinity, reducing buffering capacity and increasing the possibility of lower morning pH. Routine liming often is needed to maintain adequate alkalinity in highly intensive aquaculture systems, especially those with plastic-lined bottoms and no water exchange. Alkalinity also can decline in ponds built on acid-sulfate soils bearing pyrite, as the oxidation of pyrite yields sulfuric acid and lowers alkalinity and pH. The remediation of ponds built in acid-sulfate soils is too complex to discuss here.

Measuring pH

The most accurate way to measure pH is with a standard electronic pH meter. Litmus paper only indicates whether water is acidic or basic, and the pH estimated from pH strips only pro-vides an indication of the true pH. Small, pocket-sized pH meters are available from aquaculture supply houses, but these devices are generally unreliable after a short period of use.

It is more reliable to measure pH in situ, because this variable changes quickly during sample storage. The time of day obvi-ously influences the pH, with the lowest values typically found in the morning and the highest between noon and mid-afternoon.

The time of day obviously influences the pH, with the lowest values typically found in the morning and the highest between noon and mid-afternoon


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