In the
absence of any living organisms, a lake contains a wide array of molecules
and ions from the weathering
of soils in the watershed,
the atmosphere, and the lake bottom. Therefore, the chemical composition
of a lake is fundamentally a function of its climate (which affects
its hydrology)
and its basin
geology. Each lake has an ion
balance of the three major anions
and four major cations
(see Table 4).
|
Table
4. ION BALANCE FOR TYPICAL FRESH WATER
|
|
Anions
|
Percent
|
Cations
|
Percent
|
|
HCO3-
|
73%
|
Ca+2
|
63%
|
| SO4-2
|
16%
|
Mg+2 |
17% |
| Cl- |
10%
|
Na+ |
15% |
|
  |
  |
K+ |
4% |
| other |
<
1% |
other |
<
1% |
Ion balance
means the sum of the negative ions equals the sum of the positive cations
when expressed as equivalents. These ions are usually present at concentrations
expressed as mg/L (parts per million, or ppm)
whereas other ions such as the nutrients phosphate, nitrate, and ammonium
are present at µg/L (parts per billion, or ppb)
levels.
Humans
can have profound influences on lake chemistry. Excessive landscape
disturbance causes higher rates of leaching
and erosion by removing vegetative cover, exposing soil, and increasing
water runoff velocity. Lawn fertilizers, wastewater and urban stormwater
inputs all add micronutrients
such as nitrogen and phosphorus,
major ions such as chloride and potassium, and, in the case of highway
and parking lot runoff, oils and heavy metals. Emissions from motorized
vehicles, fossil fuel-burning electric utilities and industry, and other
sources produce a variety of compounds that affect lake chemistry.
Perhaps
the best understood ions are H+ (hydrogen
ion, which indicates acidity),
SO4-2 (sulfate) and NO3-
(nitrate) which are associated with acid
rains. Mercury (Hg) is another significant air pollutant affecting
aquatic ecosystems
and can bioaccumulate
in aquatic food
webs, contaminating fish and causing a threat to human and wildlife
health (see also the Minnesota
Pollution Control Agencys
section on Hg).
Lakes with
high concentrations of the ions calcium (Ca+2) and magnesium
(Mg+2) are called hardwater
lakes, while those with low concentrations of these ions are called
softwater
lakes. Concentrations of other ions, especially bicarbonate,
are highly correlated with the concentrations of the hardness ions,
especially Ca+2. The ionic concentrations influence the lake's
ability to assimilate pollutants and maintain nutrients in solution.
For example, calcium carbonate (CaCO3) in the form known
as marl
can precipitate phosphate from the water and thereby remove this important
nutrient from the water.
The total
amount of ions in the water is called the TDS
(total dissolved salt, or total dissolved
solids concentration). Both the concentration of TDS and the relative
amounts or ratios of different ions influence the species of organisms
that can best survive in the lake, in addition to affecting many important
chemical reactions that occur in the water. One example of particular
interest in the Great Lakes region involves the calcium requirement
of the exotic zebra mussel that is causing profound changes in Lake
Erie (see National
Aquatic Nuisance Species Clearinghouse or Sea
Grant Nonindigenous Species Site). Lake Superior appears to be relatively
immune to infestation by this invader because of low calcium concentration.
Its bays, however, such as the lower St. Louis River and Duluth-Superior
Harbor, may not be immune to zebra mussel infestation.