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September
23, 2010
Subject: A HLPOA Lake
Report
Dear HLPOA Board Members and Owners:
You know how some things grow and grow
and just don’t want to stop growing? Well, this lake report is kind of
like that.
It started out with the chronology of
Hidden Lake so that background data was available to board members to
make informed decisions about the lake. Then I asked a fellow property
owner, Susan Fakhrai, to help research
lake ecology to help explain the events in the chronology.
When the ecological and chronology were
finished, a few owners had more questions that I had paper to write on
so questions stemming from the chronology are included to show everyone
that lake management is not an easy job. When the questions were
completed, owners said we’d better come up with a draft implementation
plan because the questions would leave everyone wondering how to address
the lake issue. A draft plan, felt to be reasonable and achievable, was
added.
Susan Fakhrai
wrote the Ecological Background and she is well qualified to write this
article because she has worked as a science professional for over 30
years. I have been around Hidden Lake forever and experienced events
prior to the formation of the HLPOA so I wrote the Chronology and
compiled the questions. Susan was very helpful—providing ideas as well
as acting as a sounding board for me while I was developing the “Plan”.
This report grew and grew with so much
information that several owners felt that all owners should have access
to it, so here it is. Yes, yes, I know. It would be nice to have an
executive summary, but I am plumb out of steam and want to get this
information out before 2011 rolls around.
Thank you for taking the time to read
this document. I hope this information is informative and provides a
better understanding of the complexities involved in lake management.
Don’t hesitate to disagree, but if you do, please come up with helpful
corrections, a valid analysis based on fact, or new ways to improve the
lake.
Enjoy.
Marilyn
Borich
2010 Summer Site Manager
Ecological Background Information
Prepared by Susan
Fakhrai, 9/2010
1.
Hidden Lake formed in the remains of a
volcanic structure--maybe a caldera (according to NM geo map, underlying
rock = basalt). This agrees with appearance of area on topographic map.
2.
Over years, water naturally accumulated in
the depression--making a small lake/pond (it doesn't matter what you
call it).
o
Known sources of water include rainfall and
runoff from the surrounding area.
o
Additional water flowed into HL 1961 -1970's
from a drainage impoundment located on Lot 36.
o
Amount of inflow to HL may have been higher
prior to development of HL (ie: the
grading of roads and establishment of lot lines may have channeled water
to places other than the lake).
3.
HL has no known outflow.
4.
All lakes naturally accumulate sediments.
5.
All lakes naturally move towards becoming
completely filled-in and becoming marshes then meadows. This is called
succession and happens over many, many (hundreds? thousands? millions?)
of years.
6.
Lakes without
outflows, experience no or less throughput (flushing) and fill
with sediment faster.
7.
Lakes without
outflows, accumulate the products of decomposition faster because
there is no flushing.
8.
When plants and animals die, they sink to
the bottom of the lake where decomposers break them down into nutrients
that get dispersed throughout the lake.
9.
If there is a lot of biomass to be
decomposed, too much O2 is used and
lake O2 levels drop below that which can sustain some
animal species (decomposing organisms use up O2).
10.
Phosphorus is needed by all living things.
11.
Phosphorus comes from rocks/sediments,
decomposing organisms, fertilizers, and septic/animal wastes.
12.
If there is a lot of decomposing matter,
too much phosphorus is released, which causes too much algae.
13.
When these "algae blooms" die, even more
biomass is introduced to the system to be decomposed.
14.
Once O2 levels in the lower
levels of the lake start to decline, the phosphorus present in the
sediments becomes available, and phosphorus levels increase even
further. Initial research shows that volcanic soils such as those of HL
contain especially high levels of phosphorus.
15.
The remains of 1000’s of dead, rainbow trout
are known to be sitting in the bottom of the lake. Most of the trout's
added biomass has not been removed or flushed from the system. It
has contributed to the decaying mass of biotics
and sediments present on the floor of the lake.
Hidden Lake Chronology
1970-2010
Prepared by
Marilyn Borich, 9/2010
The purpose for gathering the following
facts about the lake at Hidden Lake subdivision is to assist the HLPOA
Board and Lake Committee to make informed decisions to improve the
health and quality of the lake, including its ability to support a
healthy fish habitat.
Sources for information include the HLPOA
Annual meeting Minutes, HLPOA special reports, HLPOA Lake committee
reports and e-mails, research notes, lake observations, discussions with
HLPOA like and alpine owners and persons participating in the
development of the Hidden Lake subdivision. Any additions or corrections
are welcome.
1970 to 1995
1.
The flume was dismantled during the 1970’s.
Between 16 and 25 years elapsed between the dismantlement of the flume
and the development of the subdivision.
2.
Owners learned that the lake was
eutrophic and had no continual
input/output of fresh water. It was formed in a volcanic depression and
precipitation is the primary source of fresh water. All streams which
could have fed the lake have dried up except for one small stream
located on Lot 42.
3.
The developer was advised by hydrology
consultants to aerate the lake. However, the developer chose to do
nothing other than stock rainbow trout annually.
2001-2005
4.
The developer purchased the trout and
Cutterine algaecide from the
Crowthers Hatchery located in Colorado.
When the HLPOA was formed in 2001, it continued this practice. The
Cutterine was applied in 3
applications—1/3 of the lake at a time. In 2005. Luis Baca, the
caretaker, applied Cutterine to 2/3 of
the lake.
5.
Several owners can verify Baca’s concern
about the decreasing water level in the lake between 2000 and 2005.
Baca’s concern is supported by the location of a boathouse and dock
built on lot 46 in 2000. The dock is about 150 feet or more from the
lake’s current shore. Luis Baca resigned from his position as caretaker
in April 2005.
6.
Kris Perreault
was hired as the caretaker in November 2005.
2006
7.
Kris applied the remaining
Cutterine to the lake. Fish were stocked
but no additional algaecide was applied in 2006. The lake reportedly had
a significant amount of rooted and surface plants and salamanders
thrived.
8.
A Lake Committee was formed at the 2006
Annual Meeting. Committee members elected to apply a “semi-scientific”
approach to lake management. Six owners donated $500 each to support the
Committee’s research efforts and to purchase scientific equipment. The
Committee researched data and interviewed experts on water quality
issues, fishery habitats, appropriate fish species, and plant
identification and control.
9.
The Committee soon learned that aeration and
plant management were essential to making the lake healthy. Research on
aeration products was straightforward while research on plant management
was more difficult.
2007
10.
A dissolved oxygen (DO) measuring system was
purchased with donated funds. Jim Coy performed the first DO test in
February under 19 inches of ice. The measurement date proved that there
was virtually no oxygen in the lake.
11.
In April, stakes were placed at the water’s
edge in 5 locations to monitor the water level. During the summer of
2007, the level of water in the lake increased a few inches at each
location. Annual precipitation was 24.68 inches.
12.
In May, Mike Smith and Tom
Rahage measured the lake. The surface
area, the volume, the depth, the width, and the length were measured. 72
depth measurements were taken to establish 7 depth profiles. The output
of the spring on Lot 42 was also measured. The length of time that the
spring contributes water to the lake is dependent on the height of
ground water and precipitation. It was also recognized that due to the
mesa’s topography, the lake probably received additional runoff from the
area above the north shore and from higher ground to the south of the
lake. These investigations and calculations require a significant effort
and were not implemented in this measurement.
13.
The 2007 lake measurements provide valuable
information and baseline data from which to compare 1995 data as well as
to monitor future measurements:
a.
The lake receded from 42 acres to 36 acres
since 1995. This is a reduction of 6 acres in 12 years.
b.
The depth of the lake decreased from 35 feet
to 24.7 feet since 1995—a reduction of nearly 10 feet in 12 years.
c.
Distribution of the 72 depth measurement
points showed that 16 points measured depths between 20 and 24.7 feet
deep, 18 points showed the lake to be 15-19.9 feet deep, and 8 points
showed that the lake depth was 10-14.9 feet. 30 measurement points
revealed that the lake was 10 feet or less in depth.
In other
words, 53% of lake measurements were 15 feet or less deep and 47% of the
measurements were between 15 and 24.7 feet in depth.
14.
The depth data above supports the average
lake depth of 12.8 feet in John Adamick’s
lake report.
15.
The stream of water feeding the lake at Lot
42 was measured in May at 12 gallons per minute. It is estimated that it
would provide 12x60x24x30x5 = 2,592,000 gallons annually if
precipitation was “normal”.
16.
In June 2007, the first water quality
analysis was performed by Aquatic Control and showed an extremely high
Ortho Phosphate (P) level of 0.43 ppm. A
result greater than 0.03 ppm is
considered too high. Total Phosphorus levels were 0.77
ppm, and measure all phosphorus both
organic and inorganic. Only the amount of Ortho P is available for
uptake by plants and the rest indicates a large sink of nutrients that
can become available over time. The water quality analysis showed that
all other measurements were within normal ranges.
17.
In September 2007, the first windmill was
erected and installed at the east access between lots 51 and 52. The
windmill aerates 3-5 acres of water.
18.
A DO test in October 2007 showed that
dissolved oxygen was very good at 7.68 ppm
at a depth of 21 feet. Per several fishery and lake consultants, fish
need at least 4.0 ppm and preferably 5.0
ppm to survive winter stress under ice.
19.
No fish were stocked or algaecide applied in
2007. A significant amount of surface and rooted plants were visible in
the lake.
20.
The Lake Committee was concerned about
copper-based algaecides because the copper settles into the sediments
and could be released as a nutrient at a later time.
2008
21.
In April and June, 2930 fish were stocked.
800 fish were 2-4 inches, 1,440 fish were 4-6 inches, 640 fish were 6-8
inches and 50 fish were 10 inches in length.
22.
Since the subdivision was formalized in
2001, about 1,000 rainbow trout were stocked annually for fishing.
Algaecides were also applied. Although the size of the fish stocked is
unknown, and the stocking of 2,930 fish contained very small fish, the
number of fish stocked in 2008 was triple that of the prior 1,000 fish
stocked. Relative to the algaecides applied, we do not know if the
applications were annual. There is no evidence that a sprayer was used.
23.
Only one record on lake levels was recorded
in 2008. On October 24, a distance of 6.7 feet between the stake and the
water’s edge was recorded at lot 53. Lot 57 showed a distance of 5.1
feet. Although this measurement was crude, it did indicate that lake
levels could be dropping. 2008 precipitation was recorded by Joe
Stehling as 25.27 inches.
24.
No DO tests were conducted or algaecides
applied in 2008. Owners reported a significant amount of surface and
rooted algae in the lake. Also, odor on the north shore was reported.
2009
25.
One DO test occurred in 2009. A January 25
DO test showed marginal DO in the lake. The windmill was damaged and
inoperable for over a month. The DO was 5.26 ppm
at location one and 4.63 ppm at location
two in a water depth of only 3 feet. In 6 feet of water, the DO was 3.42
ppm at location one and 3.7
ppm at the second location.
26.
In May 2009, 1,000 rainbow trout were
stocked. Their sizes ranged between 9 inches and 11 inches.
27.
Distances between the stakes and water’s
edge continued to increase indicating lower water levels. By the end of
July 2007, four lots showed significant increases of 27.7 feet, 20.5
feet, 24.5 feet, and 10.2 feet. Precipitation for 2009 was recorded at
23.15 inches.
28.
In August, an accurate lake level
measurement system was installed and monitored weekly. On August 1, a
depth of 23 feet was recorded. This is a decrease of 19 inches since the
2007 lake depth measurements.
29.
Concern over continuing decreases in the
lake levels prompted the HLPOA Board to hire a consultant recommended by
Eric Frei, NM Game and Fish. Wildcat
Environmental offered several diagnostic options but major costs without
reasonable expectations were an issue. The consultants recommended carp
to help control algae and offered to prepare an Aquatic Vegetation
Management Plan for $475. Additional services were not purchased by the
Lake Committee or the HLPOA Board.
30.
Several consultants, including Wildcat
Environmental, told us that water is lost each year due to evaporation.
Two consultants said to expect between 24 and 36 inches of water loss
annually minus precipitation. Recorded precipitation for 2007, 2008, and
2009 was 24.68 in, 25.27 in, and 23.15 in
respectively. Using an evaporation average of 30 inches, the
precipitation modified our evaporation loss to 5, 3, and 7 inches.
31.
Fishing during the summer of 2009 was
reportedly the best ever. Per John Adamick’s
report, the catch rate was 3-4 fish per hour per person. The rainbows
were very fat—close to 3 pounds each and the average size was 16 inches.
This information proved that the 2008 stocking survived the winter in
spite of minimal oxygen available to fish.
32.
In October 2009, a second windmill was
installed on the south side of the lake on the easement for lot 42. The
water aerated by both windmills is 6-10 acres.
33.
The second water quality analysis from
Aquatic Control in October 2009 showed tremendous improvement in the
quality of water. Total Phosphorus went from 0.77
ppm to 0.05 ppm
and the critical Ortho P went from 0.43 to 0.04
ppm.
34.
No algaecides were applied in 2009. Rooted
and surface algae were abundant.
2010
35.
DO tests taken in January (with ice
measuring 17 inches), and in May showed good DO levels (6.04
ppm and 6.5 ppm)
in water at 13 feet and 18 feet deep respectively.
36.
Between January and April, the second
windmill’s compressor malfunctioned and did not push oxygen down to the
diffusers. The compressor was replaced in July.
37.
The absence of fish was noted after the ice
melted. At first, it was thought that some fish survived. Continual
monitoring and fishing proved differently. Nearly 4000 fish died. Fish
in both the 2008 and 2009 stockings were lost.
38.
1,000 fish were delivered for stocking on
June 28.
39.
DO tests in July 2010 showed good DO down to
12 feet of water. The third water quality sample was taken on July 6th
and reported a higher Ortho P than reported in 2009. Without aeration,
the Ortho P was 0.43 ppm in 2007. In
October 2009, 28 months later, the Ortho P was 0.04
ppm while the July 2010 analysis resulted
in 0.13 ppm. Normal results should not be
higher than 0.03 ppm.
40.
The depth of aerated water decreased since
2007. In the October 2007 DO test, good
oxygen was available at a depth of 21 feet. The DO test in May 2010
showed a depth of 18 feet while the July 2010 test showed good oxygen at
a depth of 12 feet of water.
41.
Rich Palmer, our caretaker, reported a dead
fish on July 19 and several dead fish on July 26. Mike Vorst stated that
several times 100 dead fish washed up on his bank between the middle and
end of July. Janet Matthews reported seeing dead fish on the shoreline
also.
42.
Based on the above-reported facts, it is
assumed that the June 28 stocked fish are also dead. About 5000 fish
have died in 2010 or between the last fishing event and July 2010.
43.
There have been no algaecide applications
made to date in 2010.
44.
At a HLPOA Board meeting in August, Bill
Frazelle questioned whether Whirling
Disease (WD) could be the cause of the summer fish kill. Marilyn
Borich said she’d talk to
Lonnel Crowthers
and Mike Vorst. She also talked to Eric Frei
(NMG&F) and sent an email with a summary of all conversations to the
HLPOA Board. Eric felt our problem was a water quality problem and not
WD.
45.
After the Annual meeting, Marilyn
Borich asked Susan
Fakhrai of Lot 5 about
lake carrying capacity formulas. Susan has
an Environmental Science degree and has an excellent background for
researching lake issues. She emailed me a sample of many available
charts showing stocking rates. I’ve included a copy of one in the Plan
section, below.
Questions
(Resulting from the
Chronology)
Some questions have been answered or
implemented, others may not be reasonable while others may merit further
investigation. Many people have contributed to these questions and the
range and depth of questions do reflect the understanding that owners
have about lake management.
A.
Does the
HLPOA have goals for the lake?
Should the
goal be a healthy lake? Should it be a healthy lake and fishery? Should
it include a community dock? Should we plan a path around the lake for
strolling and bird watching? Should the debris in the easement be
collected, and the debris in the lake hauled out, chipped or burned and
disposed of? Should the lake be a trophy fishing lake? Should the
maintenance of the windmill access be part of the lake program? Should
we do minimum improvements and keep the lake and surrounding area as
natural as possible?
B.
Why does
the lake continue to decrease in size and depth?
Is it
evaporation only? Is it low precipitation? Is it a combination of both?
Is it because the flume is gone? Do we have an output flow that we are
not aware of? Is the bottom filling in with decomposed material? Is it
from the construction of roads or from wells? Is it because we have a
eutrophic lake and little can be done to
slow down the aging process?
C.
Why aren’t
the lower depths of water getting as much dissolved oxygen as the lake
received in 2007?
Are the
windmills too weak to push enough air through the lines to generate
oxygen? Is the decomposition of algae so excessive that it is using the
lower levels of oxygen? Is the decomposition of many fish using the
oxygen? Is it a combination of fish and algae? Are the diffusers
plugged? Are their limits to the lake’s ability to support specific fish
populations? Are there years of stored nutrients in the sediment which
are being released? Is there another condition we are not thinking of?
D.
What
options in addition to aeration do we have to improve the lake’s health?
What about
a dye that discourages plant growth? What about an algaecide that does
not hurt fish or humans? Would one time dredging remove plant materials,
increase the depth of the water, and remove phosphorus-producing
decaying plant and animal materials? What about carp or some other fish
that feeds on algae to help us control plants? Is there a product that
reduces Ortho P and releases nutrients in the water column more
aggressively if there is no fish in the lake?
E.
Should we be looking at methods to harness more precipitation to
increase the water level in the lake?
Should snow
fences be installed to collect snow on and around the lake? Should high
drift areas be identified and snow fences used to collect precipitation?
Should the stream on lot 42 be researched to determine if the flow can
be increased? Should a ditch system be engineered to direct the flow
from higher elevations to the lake?
F.
What is the
impact of algaecides on a eutrophic lake?
Do we know
what the rate of algae growth is annually over a five year period? What
is the tipping point when algae consumption of oxygen starts to kill
fish? Are there any cost effective alternatives to the use of algaecides
(other than dye or carp)? How dangerous to fish is copper in the
sediment? Do we need an aquatic plant management plan or a similar plan
as suggested by the consultant?
G.
Why did
fish survive the 2009 winter when the DO was minimal and only extended
down to 6 feet in depth?
Were
smaller fish a consideration? Was the Ortho P of 0.04
ppm a factor? Were the algae not using as
much oxygen to kill fish? Were 3000 small fish a more sustainable
quantity? Did the smaller fish adapt to our lake environment more
readily than larger fish? Are there other reasons we haven’t thought
of?
H.
Why did the
fish die in the 2010 winter when the DO was very good and extended to 13
feet in January?
Was the
water quality poor due to algae or some other factor? Did
an unknown condition increase oxygen
consumption? Were the fish in poor health before winter and unable to
sustain themselves under winter stress? Were there too many fish
competing with algae over the oxygen? Is there another issue we haven’t
addressed?
I.
Have the
Koender windmills performed as expected?
Are the two
malfunctions, in two windmills, in two years acceptable? What about
another type of unit where spare parts and repair can be done
expeditiously on site? Do we need to appoint a person to research other
types of windmills used by local ranchers? Does the HLPOA Board need to
support the Lake Committee more effectively?
J.
Should we
be spending money on fish and aeration when the lake level continues to
decrease and the cause has not
been identified?
If the lake
level has been receding between 1996 and 2000 until present, do we need
a consultant to help us? If the water level continues to decrease and
the issue cannot be resolved should we go back to the developer’s
practice of annual stocking and algaecides without concern for the
quality of water in the lake? Should we accept the lake as dying and
invest as little as possible in it knowing that a marsh will replace the
lake in the future? Is the lake an asset to the community? If so, should
we set aside budget, experiment ourselves, purchase professional help,
and improve the health of the lake to the best of our ability in a cost
effective manner?
A Plan (That Just
Might Work)
We need to
establish goals for the lake’s water quality and fishery. Step
One should be Water Quality goals and the
steps to achieve those goals. The fishery is improved as a by-product of
a healthy lake. Therefore, fishery goals and improvement steps are Step
2. When water quality and fishery goals are being successfully
implemented, goals to improve the community’s opportunities to enjoy the
lake can be Step Three. Steps One and Two are addressed below.
Step One: Water
Quality
A.
Water
Quality Goals
1.
Recommended
goals include:
a.
Establish the desired Ortho P levels
b.
Control aquatic plants
c. Increase
the distribution of oxygen to the lower depths of water
d.
Stabilize the lake’s size (depth, volume,
etc.)
B.
Water
Quality Improvement Steps
1.
Establish
desired Ortho P ppm, control aquatic
plants, and increase oxygen at lower depths.
a.
The first step is to give the lake a rest
and a chance to heal—a chance to decompose the fish and algae lying in
the sediment.
b.
Establish the desired Ortho P
ppm. We recommend 0.03
ppm. Continue water quality analyses.
Monitor, compare and record current Ortho P ppm
with the established Ortho P ppm goal.
c.
We recommend that the first water quality
analysis be initiated in October 2010 and again in July 2011 after
aquatic plant control is initiated.
d.
Research products that may be available to
reduce Ortho P ppm, by accelerating
decomposition.
e.
Obtain aerial photos of the lake taken prior
to the installation of the flume to compare the previous size of the
lake to its current size.
f.
During the winter of 2010/2011 options and
products proven to control algae should be researched. The focus should
be on surface plants but rooted plants may also require “thinning”. We
recommend that aquatic plant control commence in June 2011.
g.
Since owners at the 2010 Annual Meeting
voted not to stock fish in 2011, an aggressive plant control option can
be pursued.
h.
Aquatic plant control selection can be
simplified and research reduced by purchasing an aquatic plant
management plan similar to that offered for $475 by Wildcat
Environmental. If recommendations and instructions are followed, we
should be fairly successful. However, we may find that the
recommendations are expensive or difficult to implement.
i.
The alternative option is to research and
screen the many available products to find the most cost effective plant
control. Dyes and carp, as well as algaecides are used in this part of
the state.
j.
Whether to buy an application sprayer or
rent one must be determined before algaecide application begins. Hand
broadcasting may also be an option.
k.
Continued water analyses and DO testing will
show us if we are going in the right direction or whether we must modify
our improvement programs. Per the NMG&F expert, experimenting is often
necessary.
l.
Prepare a budget which addresses water
analyses, interviews, reference and instructional materials,
consultants, and algaecide applicator and a reserve for additional
aeration if needed.
2.
Lake
Stabilization
a.
Stabilization is probably our biggest
financial and technical challenge.
b.
One owner recommended putting a dye in the
center of the lake and tracking its flow. If a source of leakage is
located, a clay product (used in the oil business) could be applied to
seal the outflow.
c.
Another owner has suggested drilling a well,
installing a windmill, and pumping water from the well to the lake (this
may require permission from the State Engineer).
d.
Streams have been seen on several lots. Once
identified, with owners’ permission, they can possibly be routed to the
lake.
e.
Several owners have discussed the design of
a ditch system from the southern and higher part of the subdivision to
bring more precipitation to the lake. This system should also look at
the feasibility of incorporating some of the mapped streams.
f.
The use of snow fences was also a suggestion
to collect snow. The identification of high drift areas and the
installation of snow fences is a good first step while the design and
implementation of a more permanent system could be developed.
g.
We should not rule out the use of
consultants. They are expensive but so are losing water and fish.
Consultants could shorten the time it takes to get results if the
recommendations are reasonable. Consulting with owners of large ranches
with lakes/ponds may also be helpful.
Step Two: The Fishery
A.
Fishery
Goals
1.
Recommended
goals include:
a.
Establish the appropriate DO
ppm to support a healthy fishery
b.
Monitor and record the actual DO
ppm measured and compare to the
established DO pm goal.
c.
Ensure that the aeration system supports the
established DO ppm.
d.
Establish a stocking program based on the
lake’s capacity to support fish.
e.
Prepare instructional procedures.
B.
Fishery
Improvement Steps
1.
Establish
an appropriate DO ppm.
a.
Establish the DO ppm
(we hear most often from 4.0 ppm to 6.0
ppm) requirements to ensure fish
survivability during winter. Also establish the desired depth that DO
should be available to fish.
b.
We recommend that several water quality
experts be consulted while DO requirements addressed in a. (above) are
established. The NMG&F personnel in Raton have a wealth of experience
and should be an excellent source of guidance on this topic and others.
2.
Monitoring,
Testing, and Recording DO ppm
a.
Monthly monitoring of DO levels should be at
3-foot depth intervals. This information will inform us when the desired
DO ppm is achieved or when the desired DO
ppm is not achieved. Monthly data may
also be a useful indicator to recognize an oxygen reduction trend.
b.
If the amount of oxygen necessary to
maintain a healthy fishery was available at 21 feet depth in
2007, and if monthly DO monitoring showed
a trend of less oxygen at lower water depths for a few months, we may
have known much earlier that something in the fishery was not right.
However, with the few DO samples taken, this warning was not available.
Monthly DO testing will determine if this
trend indicator is reasonable.
c.
The frequency of DO testing, water quality
analyses, and the water level monitoring
is critical as a basis for making fishery habitat decisions. Obviously,
during water quality restoration, the frequencies should be often; once
quality levels are achieved, monitoring would require less effort.
3.
Ensuring
the Aeration System Supports the Baseline DO ppm
a.
A question asked at the Annual Meeting was
whether a third windmill should be purchased. A decision to do so or not
should be part of this plan.
b.
There are many unanswered questions at this
point that impact fish survivability including Plant Management, High
Ortho P, Reduced Oxygen at lower lake
levels and perhaps, even stocking levels. Aeration is the number one
contributor to water quality and a fishery habitat but it is not the
only contributor.
c.
Since there will be no stocking in 2011,
there is no immediate concern about fish survivability. This gives us
time to thoroughly address aeration.
d.
Our approach is to implement plant control
and Ortho P reduction, establish a DO baseline, and monitor until the
desired level of DO is achieved. Stock fish at an appropriate stocking
rate and continue monitoring DO monthly. If the DO levels are maintained
with a little surplus DO, we may not need additional aeration.
e.
However, if plants are controlled, Ortho P
is reduced appropriately, and fish thrive, and the DO is lower than the
DO requirement, then serious consideration should be given to additional
aeration or addressing the DO requirement.
f.
Based on information from NMG&F personnel,
aeration—be it windmills or electrical
systems—may not be able to quickly supply enough DO to sustain fish when
a huge draw on oxygen occurs. It’s our job to ensure that such a huge
draw on oxygen does not occur.
4.
Fish
Stocking
a.
Determining the appropriate number and size
of fish to stock depends on available lake volume and adequate water
quality.
b.
We recommend that—prior to the next stocking
activity—the NMG&F be consulted regarding their recommended stocking
rates. Other sources, such as the table below should also be consulted
(From: Managing Michigan Ponds for Sport Fishing, 1994. JD
Schrouder
et.al. MSU.)
|
Stocking Rates—Unfed Pond
(numbers in
parentheses are if you assume
HL = 15 acres) |
|
Type of Trout |
Size |
Number/acre |
When stocked |
Comments |
|
Spring fingerlings |
2-3” |
200-300
(3000-4500) |
April-May |
Low
cost; only for ponds with no other fish |
|
Fall fingerlings |
5-6” |
50-150
(750-2250)
|
Sep-Oct
|
For
initial stocking or restocking |
|
Spring yearlings |
6-7” |
50-150
(750-2250)
|
April-June |
For
initial stocking or restocking |
|
Adults |
Over 7” |
25-50
(375-750)
|
Spring or Fall |
For
initial stocking or restocking |
c.
Relative to available water acres used in
the above chart, we would not use the entire lake acreage (36 acres) in
the stocking calculation. Since about one-half of the lake is 15 feet or
less, and ice thickness can be 19 inches thick, we suggest using 15
acres as the starting point.
d.
If continued fishing, monitoring and water
analyses reflect healthy fish, increase stocking—one acre at a time—up
to 18 acres.
5.
Prepare
Instructional Procedures
a.
The recommended instructional documents
include windmill maintenance and DO test procedures. These procedures
should be written by persons knowledgeable about each topic. At the very
least, knowledgeable persons should review the work and approve it.
b.
The steps in each procedure should be given
to a person not familiar with the procedure. If the procedure is
followed easily, the procedure is well written. If an unfamiliar person
has a few problems understanding the process, some changes may be
necessary.
|