In
September 2004, a letter was written to the River Falls Journal
expressing concern over the algae problems in Lake George.
Included in that letter was a feeling that the dams should be removed
because of this problem. We have posted here our responses to
some common algae and dam removal questions.
Q: What Causes
Algae?
A: The
development of an algae bloom depends upon local conditions and site-specific
characteristics. But they generally occur where there are high levels of
nutrients, principally phosphorus, together with warm, sunny and calm
conditions.
The
main source of nutrients in Lake George is sediment, which has
accumulated behind the dams since they were constructed over 100 years
ago. This sediment
resulted from poor upland soil conservation practices that were
generally followed prior to 1960. It
has been estimated that in the 1950’s, sediment was accumulating in
Lake George at a rate of 2,500 cubic yards per year.
In the 1990’s the estimated rate of sediment accumulation had
dropped to 500 cubic yards per year.
The
Kinnickinnic Priority Watershed Project
indicated that the current sources of sediment in the
Kinnickinnic River at River Falls are:
All
Uplands.............................
83%
Streambank
Erosion................ 3%
Erosion
of Dry Runs................ 6%
Urban
Runoff...........................
5%
Construction
Sites.................... 3%
Q: How much of the algae problem is caused by the two dams on the river?
A: The
algae is caused by nutrient rich soil that is accumulated behind the
dams. Without the dams in
place, this nutrient rich soil would have been transported further
downstream.
Q: What
kinds of changes have been observed over the years as far as the amount of algae
goes?
A:
The
delivery of nutrient rich soil to the Kinnickinnic River has been significantly
decreased over the past 30-years and continues to get better.
This directly leads to less production of algae in both the rivers and
the lakes because they are receiving less nutrient rich sediment.
However, significant nutrient rich sediment deposits remain and lakes
are very slow to recover after excessive phosphorus inputs have been
eliminated.
Q: Is
there a possibility of removing the dams to help remove the algae?
Why or why not?
A: Removing
the dams would result in the reduction of algae present on the lake
because the lake would no longer be there.
If the dams were no longer there to trap the nutrient rich
sediments that are being transported in the river, the algae problem
would simply move downstream,
therefore it would be critical to implement new measures that prevent
nutrient rich sediments from entering the river.
Q: What
kinds of options are there for removing the algae?
Is it harmful?
A: Typically, the first steps taken target the control of the external
sources of phosphorus and can include: encouraging the use of phosphorus free
fertilizers; improving agricultural practices, reducing urban run-off; and
restoring vegetation buffers around waterways.
Lakes are very slow to recover after excessive phosphorus inputs have
been eliminated. Furthermore, it’s extremely difficult to
achieve recovery of lake conditions without additional in-lake
management. This is due to the fact that lake sediments become
phosphorus rich and can deliver excessive amounts of phosphorus to the
overlying water. When dissolved oxygen levels decrease in the bottom
waters of the lake (anaerobic conditions), large amounts of phosphorus
trapped in the bottom sediments are released into the overlying water.
This process is often called internal nutrient loading or recycling.
Alum is used primarily to control this internal recycling of
phosphorus from the sediments of the lake bottom that result in algae.
On contact with water, alum forms a fluffy aluminum hydroxide
precipitate called floc. Aluminum hydroxide (the principle ingredient
in common antacids such as Maalox) binds with phosphorus to form an
aluminum phosphate compound. This
compound is insoluble in water under most conditions so the phosphorus
in it can no longer be used as food by algae organisms. As the floc
slowly settles, some phosphorus is removed from the water.
The floc also tends to collect suspended particles in the water
and carry them down to the bottom, leaving the lake noticeably
clearer. On the bottom of the lake the floc forms a layer that acts as
a phosphorus barrier by combining with phosphorus as it is released
from the sediments.
Q: How
long have the dams been around for? What
is their purpose?
A: The
power plant started here in 1900, that’s when the first hydro was
put in. The upper dam
produces 250-kilowatts/hr maximum and the lower dam produces 125-kw/hr
maximum. The amount
produced is based on the flow in the river.
The dams are operated in “run of the river” fashion. This means that they do
not store additional water behind the dams during times of low
energy use in order to generate more energy at peak times. Instead, the hydro plants use whatever natural flow exists in
the river to produce energy.
There was a smaller rock and crib dam built in 1865, which is located
between the upper dam and the Winter Street Bridge.
It is currently under water, but still there.
This dam provided electricity to convert gas streetlights on
Main Street into electric streetlights to prevent fires, which is how
the utility was first started.
Q: How
long of a process would removing the dams be?
A: The process would involve a significant number of entities and
agencies. The process
would probably take between 3 and 6 years.
Q: As
far as the city is concerned, how much of a problem is the algae and how much of
a prerogative for the city is the issue?
A: The City is concerned with anything that results in adverse
water quality impacts to the Kinnickinnic River. Arguments could be made that the algae in the lakes results
in minor adverse water quality impacts on the Kinnickinnic River.
However, if dam removal is to be considered, measures must be
taken to offset the sediment removal function that the dams currently
provide so that nutrient rich sediments are not unnecessarily
introduced into the lower Kinnickinnic River.
Such measures are currently being evaluated by the City through a
grant from the Wisconsin Department of Natural Resources.
The scope of this work is to conduct a detailed feasibility
study focused on reconfiguring Lake George to act as a storm water
quality facility for runoff and also to determine if a concept can be
developed that would be viable whether or not the dam remains in place
long-term. The study is
also considering alternative treatment options that will identify the
alternative treatment system that could be implemented in this
watershed without reconfiguring Lake George.