The pH of water
determines the solubility (amount that can be dissolved in the water)
and biological availability (amount that can be utilized by aquatic
life) of chemical constituents such as nutrients (phosphorus, nitrogen,
and carbon) and heavy metals (lead, copper, cadmium, etc.). For example,
in addition to affecting how much and what form of phosphorus is most
abundant in the water, pH may also determine whether aquatic life can
use it. In the case of heavy metals, the degree to which they are soluble
determines their toxicity. Metals tend to be more toxic at lower pH
because they are more soluble.
Reasons for
Natural Variation
Photosynthesis
uses up dissolved carbon dioxide which acts like carbonic acid (H2CO3)
in water. CO2 removal, in effect, reduces the acidity of the water
and so pH increases. In contrast, respiration of organic matter produces
CO2, which dissolves in water as carbonic acid, thereby lowering
the pH. For this reason, pH may be higher during daylight hours and
during the growing season, when photosynthesis is at a maximum. Respiration
and decomposition processes lower pH.
Like dissolved oxygen concentrations,
pH may change with depth in a lake, due again to changes in photosynthesis
and other chemical reactions. There is typically a seasonal decrease
in pH in the lower layers of
a stratified lake because CO2 accumulates.
There is no light for plants to fix CO2 and decomposition releases
CO2.
Fortunately, lake
water is complex; it is full of chemical "shock absorbers" that
prevent major changes in pH. Small or localized changes in pH are quickly
modified by various chemical reactions, so little or no change may be measured.
This ability to resist change in pH is called buffering capacity.
Not only does the buffering capacity control would-be localized changes in
pH, it controls the overall range of pH change under natural conditions. The
pH scale may go from 0 to 14, but the pH of natural waters hovers between
6.5 and 8.5.
Expected Impact
of Pollution
When pollution
results in higher algal and plant growth (e.g., from increased temperature
or excess nutrients), pH levels may increase, as allowed by the buffering
capacity of the lake. Although these small changes in pH are not likely to
have a direct impact on aquatic life, they greatly influence the availability
and solubility of all chemical forms in the lake and may aggravate nutrient
problems. For example, a change in pH may increase the solubility of phosphorus,
making it more available for plant growth and resulting in a greater long-term
demand for dissolved oxygen.
Values for pH
are reported in standard pH units, usually to one or two decimal places depending
upon the accuracy of the equipment used.
Since
pH represents the negative logarithm of a number, it is not mathematically
correct to calculate simple averages or other summary statistics.
Instead, pH should
be reported as a median and range of values; alternatively the values could
be converted to hydrogen ion concentrations, averaged, and re-converted to
pH values.
Generally, during
the summer months in the upper portion of a productive or eutrophic lakes,
pH will range between 7.5 and 8.5. In the bottom of the lake or in less productive
lakes, pH will be lower, 6.5 to 7.5, perhaps. This is a very general statement
to provide an example of the differences you might measure.
The Case of
Acid Rain
An important
exception to the buffering of pH changes in lakes is the case of lakes
affected by acid rain. Lakes that have received too much rain with a
low pH (acid
rain), lose their buffering capacity. At a certain point, it takes
only a small bit of rain or snowmelt runoff for the pH to change. After
that point, change occurs relatively quickly. According to the EPA,
a pH of 5-6 or lower has been found to be directly toxic to fish (for
additional information, see our acid rain
links).
REFERENCES
Michaud, J.P.
1991. A citizen's guide to understanding and monitoring lakes and streams.
Publ. #94-149. Washington State Dept. of Ecology, Publications Office, Olympia,
WA, USA (360) 407-7472.
Moore, M.L. 1989.
NALMS management guide for lakes and reservoirs. North American Lake
Management Society, P.O. Box 5443, Madison, WI, 53705-5443, USA (http://www.nalms.org).