United States
Environmental Protection
Agency
Environmental Monitoring
and Support Laboratory
P.O. Box 15027
Las Vegas NV 89114
Research and Development
&EPA
of
Phytoplankton in
Iowa Lakes
Working
Paper695
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DISTRIBUTION OF PHYTOPLANKTON IN IOWA LAKES
by
L. R. Williams, S. C. Hern, V. W. Lambou
F. A. Morris*, M. K. Morris*, and W. D. Taylor
Water and Land Quality Branch
Monitoring Operations Division
Environmental Monitoring and Support Laboratory
Las Vegas, Nevada 89114
*Departroent of Biological Sciences
University of Nevada, Las Vegas
Las Vegas, Nevada 89154
WORKING PAPER NO. 695
NATIONAL EUTROPHICATION SURVEY
OFFICE OF RESEARCH AND DEVELOPMENT
U.S. ENVIRONMENTAL PROTECTION AGENCY
November 1978
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DISCLAIMER
This report has been reviewed by the Environmental Monitoring and
Support Laboratory-Las Vegas, U.S. Environmental Protection Agency, and
approved for publication. Mention of trade names or commercial products does
not constitute endorsement or recommendation for use.
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FOREWORD
The National Eutrophication Survey was initiated in 1972 in response to
an Administration commitment to investigate the nationwide threat of
accelerated eutrophication to freshwater lakes and reservoirs. The Survey
was designed to develop, in conjunction with State environmental agencies,
information on nutrient sources, concentrations, and impact on selected
freshwater lakes as a basis for formulating comprehensive and coordinated
national, regional, and State management practices relating to point source
discharge reduction and nonpoint source pollution abatement in lake
watershed.
The Survey collected physical, chemical, and biological data from 815
lakes and reservoirs throughout the contiguous United States. To date, the
Survey has yielded more than two million data points. In-depth analyses are
being made to advance the rationale and data base for refinement of nutrient
water quality criteria for the Nation's freshwater lakes.
Ill
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CONTENTS
Foreword iii
Introduction 1
Materials and Methods 3
Lake and Site Selection 3
Sample Preparation 3
Examination 4
Quality Control 5
Results 6
Nygaard's Trophic State Indices 6
PaTmer's Organic Pollution Indices 6
Species Diversity and Abundance Indices 8
Species Occurrence and Abundance 10
Literature Cited 11
Appendix A. Phytoplankton Species list for the State
of Iowa 12
Appendix B. Summary of Phytoplankton Data 16
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INTRODUCTION
The collection and analysis of phytoplankton data were included in the
National Eutrophication Survey in an effort to determine relationships between
algal characteristics and trophic status of individual lakes.
During spring, summer, and fall of 1974, the Survey sampled 179 lakes in
10 States. Over 700 algal species and varieties were identified and
enumerated from the 573 water samples examined.
This report presents the species and abundance of phytoplankton in the
15 lakes sampled in the State of Iowa (Table 1). The Nygaard's Trophic State
(Nygaard 1949), Palmer's Organic Pollution (Palmer 1969), and species
diversity and abundance indices are also included.
TABLE 1. LAKES SAMPLED IN THE STATE OF IOWA
STORET No.
Lake Name
County
1901
1902
1903
1904
1905
1906
1907
1908
1909
1910
1911
1912
Lake Ahquabi--
Big Creek Reservoir
Black Hawk Lake
Clear Lake
Lake Darling
Lost Island Lake
Lake McBride
Prairie Rose Lake
Rathbun Reservoir
Red Rock Reservoir
•
Rock Creek Lake
Silver Lake
Warren
Polk
Sac
Cerro Gordo .
Washington
Palo Alto
Johnson
Shelby
Appanoose, Wayne, Lucas
*•
Marion
Jasper
Worth
(Continued)
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TABLE 1. LAKES SAMPLED IN THE STATE OF IOWA (Continued)
STORET No. Lake Name County
1913 Spirit Lake Dickinson
1914 Viking Lake Montgomery
1915 West Lake Okoboji Dickinson
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MATERIALS AND METHODS
LAKE AND SITE SELECTION
Lakes and reservoirs included in the Survey were selected through
discussions with State water pollution agency personnel and U.S. Environmental
Protection Agency Regional Offices (U.S. Environmental Protection Agency
1975). Screening and selection strongly emphasized lakes with actual or
potential accelerated eutrophication problems. As a result, the selection was
1imited to lakes:
(1) impacted by one or more municipal sewage treatment plant outfalls
either directly into the lake or by discharge to an inlet tributary
within approximately 40 kilometers of the lake;
(2). 40 hectares or larger in size; and
(3) with a mean hydraulic retention time of at least 30 days.
Specific selection criteria were waived for some lakes of particular State
interest.
Sampling sites for a lake were selected based on available information on
lake morphometry, potential major sources of nutrient input, and on-site
judgment of the field limnologist (U.S. Environmental Protection Agency 1975).
Primary sampling sites were chosen to reflect the deepest portion of each
major basin in a test lake. Where many basins were present, selection was
guided by nutrient source information on hand. At each sampling site, a
depth-integrated phytoplankton sample was taken. Depth-integrated samples
were uniform mixtures of water from the surface to a depth of 15 feet
(4.6 meters) or from the surface to the lower limit of the photic zone
representing 1 percent of the incident light, whichever was greater. If the
depth at the sampling site was less than 15 feet (4.6 meters), the sample was
taken from just off the bottom to the surface'. Normally, a lake was sampled
three times in 1 year, providing information on spring, summer, and fall
conditions.
SAMPLE PREPARATION
To preserve the sample 4 milliliters (ml) of Acid-Lugol's solution
(Prescott 1970) were added to each 130-ml sample from each site at the time of
collection. The samples were shipped to the Environmental Monitoring and
Support Laboratory, Las Vegas, Nevada, where equal volumes from each site
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were mixed to form two 130-ml composite samples for a given lake
composite sample was put into storage and the other was used for
examination.
One
for the
Prior to examination, the composite samples were concentrated by the
settling method. Solids were allowed to settle for at least 24 hours prior to
siphoning off the supernate. The volume of the removed supernate and the
volume of the remaining concentrate were measured and concentrations
determined. A small (8-ml) library subsample of the concentrate was then
taken. The remaining concentrate was gently agitated to resuspend the
plankton and poured into a capped, graduated test tube. If a preliminary
examination of a sample indicated the need for a more concentrated sample, the
contents of the test tube were further concentrated by repeating the settling
method. Final concentrations varied from 15 to 40 times the original.
Permanent slides were prepared from concentrated samples after analysis
was complete. A ring of clear Karo® corn syrup with phenol (a few crystals of
phenol were added to each 100 ml of syrup) was placed on a glass slide. A
drop of superconcentrate from the bottom of the test tube was placed in the
ring. This solution was thoroughly mixed and topped with a coverglass. After
the syrup at the edges of the coverglass had hardened, the excess was scraped
away and the mount was sealed with clear fingernail polish. Permanent diatom
slides were prepared by drying sample material on a coverglass, heating in a
muffle furnace at 400° C for 45 minutes, and mounting in Hyrax®. Finally, the
mounts were sealed with clear fingernail polish.
Backup samples, library samples, permanent sample slides, and
Hyrax-mounted diatom slides are being stored and maintained at the
Environmental Monitoring and Support Laboratory-Las Vegas.
EXAMINATION
The phytoplankton samples were examined with the aid of binocular
compound microscopes. A preliminary examination was performed to precisely
identify and list all forms encountered. The length of this examination
varied depending on the complexity of the sample. An attempt was made to find
and identify all of the forms present in each sample. Often forms were
observed which could not be identified to species or to genus. Abbreviated
descriptions were used to keep a record of these forms (e.g., lunate cell,
blue-green filament, Navicula #1). Diatom slides were examined using a
standard light microscope. If greater resolution was essential to accurately
identify the diatoms, a phase-contrast microscope was used.
After the species list was compiled, phytoplankton were enumerated using
a Neubauer Counting Chamber with a 40X objective lens and a 10X ocular lens.
All forms within each field were counted. The count was continued until a
minimum of 100 fields had been viewed, or until the dominant form had been
observed a minimum of 100 times.
®Registered trademark
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QUALITY CONTROL
Project phycologists performed internal quality control intercomparisons
regularly on 7 percent of the species identification and counts. Although an
individual had primary responsibility for analyzing a sample, taxonomic
problems were discussed among the phycologists.
Additional quality control checks were performed on the Survey samples by
Dr. G. W. Prescott of the University of Montana at the rate of 5 percent.
Quality control checks were made on 75 percent of these samples to verify
species identifications while checks were made on the remaining 25 percent of
the samples to verify genus counts. Presently, the agreement between quality
control checks for species identification and genus enumerations is
satisfactory.
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RESULTS
A phytoplankton species list for the State is presented in Appendix A.
Appendix B summarizes all of the phytoplankton data collected from the State
by the Survey. The latter is organized by lake, and includes an alphabetical
phytoplankton species list with concentrations for individual species given by
sampling date. Results from the application of several indices are presented
(Nygaard's Trophic State, Palmer's Organic Pollution, and species diversity
and abundance). Each lake has been assigned a four-digit STORET number.
(STORET (STOrage and RETrieval) is the U.S. Environmental Protection Agency's
computer system which processes and maintains water quality data.) The first
two digits of the STORET number identify the State; the last two digits
identify the lake.
NYGAARD'S TROPHIC STATE INDICES
Five indices devised by Nygaard (1949) were proposed under the assumption
that certain algal groups are indicative of levels of nutrient enrichment.
These indices were calculated in order to aid in determining the surveyed
lakes' trophic status. As a general rule, Cyanophyta, Euglenophyta, centric
diatoms, and members of the Chlorococcales are found in waters that are
eutrophic (rich in nutrients), while desmids and many pennate diatoms
generally cannot tolerate high nutrient levels and so are found in
oligotrophic waters (poor in nutrients).
In applying the indices to the Survey data, the number of taxa in each
major group was determined from the species list for each sample. The ratios
of these groups give numerical values which can be used as a biological index
of water richness. The five indices and the ranges of values established for
Danish lakes by Nygaard for each trophic state are presented in Table 2. The
appropriate symbol, (E) eutrophic and (0) oligotrophic, follows each
calculated value in the tables in Appendix B. A question mark (?) following a
calculated value in these tables was entered when that value was within the
range of both classifications.
PALMER'S ORGANIC POLLUTION INDICES
Palmer (1969) analyzed reports from 165 authors and developed algal
pollution indices for use in rating water samples with high organic pollution.
Two lists of organic-pollution-tolerant forms were prepared, one containing
20 genera, the other, 20 species (Tables 3 and 4). Each form was assigned a
pollution index number ranging from 1 for moderately tolerant forms to 6 for
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TABLE 2. NYGAARD'S TROPHIC STATE INDICES ADAPTED FROM HUTCHINSON (1967)
Index
Calculation
Oligotrophic Eutrophic
Myxophycean
Chlorophycean
Diatom
Euglenophyte
Compound
Myxophyceae
Desmideae
Chlorococcales
Desmideae
Centric Diatoms
Pennate Diatoms
Euglenophyta
Myxophyceae + Chlorococcales
Myxophyceae + Chlorococcales +
0.0-0.4
0.0-0.7
0.0-0.3
0.0-0.2
0.0-1.0
0.1-3.0
0.2-9.0
0.0-1.75
0.0-1.0
1.2-25
Centric Diatoms + Euglenophyta
Desmideae
TABLE 3. ALGAL GENUS POLLUTION INDEX
(Palmer 1969)
TABLE 4* ALGAL SPECIES POLLUTION
INDEX (Palmer 1969)
Genus
Anacystis
Ankistrodesmus
Chlamydomonas
Chi orel la
Closterium
Cyclotella
Euglena
Gomphonema
Lepocinclis
Me 1 osi ra
Micractinium
Navicula
Nitzschia
Oscillator! a
Pandorina
Phacus
Phormidium
Scenedesmus
Stigeoc Ionium
Synedra
Pollution
Index
1
2
4
3
1
1
5
1
1
1
1
3
3
5
1
2
1
4
2
2
Species
Ankistrodesmus falcatus
Arthrospira jenneri
Chlorella vulgaris
Cyclotella meneghiniana
Euglena gracilis
Euglena viridis
Gomphonema parvulum
Melosira varians
Navicula cryptocephala
Nitzschia acicularis
Nitzschia palea
Oscillatoria chlorina
Oscillatori a limosa
Oscillatoria jsrinceps
Oscillatoria putrida
Oscillatoria tenuis
Pandorina morum
Scenedesmus quadricauda
Stigeoclonium tenue
Synedra ulna
Pollution
Index
3
' 2
2
2
1
6
1
2
1
1
5
2
4
1
1
4
3
4
3
3
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extremely tolerant forms. Palmer based the index numbers on occurrence
records and/or where emphasized by the authors as being especially tolerant of
organic pollution.
In analyzing a water sample, any of the 20 genera or species of algae
present in concentrations of 50 per milliliter or more are recorded. The
pollution index numbers of the algae present are totaled, providing a genus
score and a species score. Palmer determined that a score of 20 or more for
either index can be taken as evidence of high organic pollution, while a score
of 15 to 19 is taken as probable evidence of high organic pollution. Lower
figures suggest that the organic pollution of the sample is not high, that the
sample is not representative, or that some substance or factor interfering
with algal persistence is present and active.
SPECIES DIVERSITY AND ABUNDANCE INDICES
"Information content" of biological samples is being used commonly by
biologists as a measure of diversity. Diversity in this connection means the
degree of uncertainty attached to the specific identity of any randomly
selected individual. The greater the number of taxa and the more equal their
proportions, the greater the uncertainty, and hence, the diversity (Pielou
1966). There are several methods of measuring diversity, e.g., the formulas
given by Brillouin (1962) and Shannon and Weaver (1963). The method which is
appropriate depends on the type of biological sample on hand.
Pielou (1966) classifies the types of biological samples and gives the
measure of diversity appropriate for each type. The Survey phytoplankton
samples are what she classifies as larger samples (collections in Pielou's
terminology) from which random subsamples can be drawn. According to Pielou,
the average diversity per individual (H) for these types of samples can be
estimated from the Shannon-Wiener formula (Shannon and Weaver 1963):
S
H = -E pi 1Q9X pi
where P is the proportion of the ith taxon in the sample, which is calculated
from n-j/N; n-j is the number of individuals per milliliter of the ith
taxon; N is the total number of individuals per ml; and S is the total number
of taxa. However, Basharin (1959) and Pielou (1966) have pointed out that H
calculated from the subsample is a biased estimator of the sample H, and if
this bias is to be accounted for, we must know the total number of taxa
present in the sample since the magnitude of this bias depends on it.
Pielou (1966) suggests that if the number of taxa in the subsample falls
only slightly short of the number in the larger sample, no appreciable error
will result in considering S, estimated from the subsample, as being equal to
the sample value. Even though considerable effort was made to find and
identify all taxa, the Survey samples undoubtedly contain a fair number of
rare phytoplankton taxa which were not encountered.
8
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In the Shannon-Wiener formula, an increase in the number of taxa and/or
an increase in the evenness of the distribution of individuals among taxa will
increase the average diversity per individual from its minimal value of zero.
Sager and Hasler (1969) found that the richness of taxa was of minor
importance in determination of average diversity per individual for
phytoplankton and they concluded that phytoplankton taxa in excess of the 10
to 15 most abundant ones have little effect on H. This was verified by our
own calculations. Our counts are in number per milliliter and since
logarithms to the base 2 were used in our calculations, H is expressed in
units of bits per individual. When individuals of a taxon were so rare that
they were not counted, a value of 1/130 per milliliter or 0.008 per milliliter
was used in the calculations since at least one individual of the taxon must
have been present in the collection.
A Survey sample for a given lake represents a composite of all
phytoplankton collected at different sampling sites on the lake during a given
sampling period. Since the number of samples (M) making up a composite is a
function of both the complexity of the lake sampled and its size, it should
affect the richness-of-taxa component of the diversity of our phytoplankton
collections. The maximum diversity (MaxH) (i.e., when the individuals are
distributed among the taxa as evenly as possible) was estimated from Iog2 S
(Pielou 1966), while the minimum diversity (MinH), was estimated from the
formula:
MinH = -
S-l
"IT
N - (S-l)
N
og2
N - (S-l)
N
given by Zand (1976). The total diversity (D) was calculated from HN (Pielou
1966). Also given in Appendix B are L (the mean number of individuals per
taxa per milliliter) and K (the number of individuals per milliliter of the
most abundant taxon in the sample).
The evenness component of diversity (J) was estimated from H/MaxH
(Pielou 1966). Relative evenness (RJ) was calculated from the formula:
RJ =
H-MinH
MaxH-Mi nH
given by Zand (1976). Zand suggests that RJ be used as a substitute for both
J and the redundancy expression given by Wilhm and Dorris (1968). As pointed
out by Zand, the redundancy expression given by Wilhm and Dorris does not
properly express what it is intended to show, i.e., the position of H in the
range between MaxH and MinH. RJ may range from 0 to 1; being 1 for the most
even samples and 0 for the least even samples.
Zand (1976) suggests that diversity indices be expressed in units of
"sits", i.e., in logarithms to base S (where S is the total number of taxa in
the sample) instead of in "bits", i.e., in logarithms to base 2. Zand points
out that the diversity index in sits per individual is a normalized number
ranging from 1 for the most evenly distributed samples to 0 for the least
evenly distributed samples. Also, it can be used to compare different
samples, independent of the number of taxa in each. The diversity in bits per
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individual should not be used in direct comparisons involving various samples
which have different numbers of taxa. Since MaxH equals log S, the expression
in sits is equal to logs S, or 1. Therefore diversity in sits per
individual is numerically equivalent to J, the evenness component for the
Shannon-Wiener formula.
SPECIES OCCURRENCE AND ABUNDANCE
The alphabetic phytoplankton species list for each lake, presented in
Appendix B, gives the concentrations of individual species by sampling date.
Concentrations are in cells, colonies, or filaments (CEL, COL, FIL) per
milliliter. An "X" after a species name indicates that the species identified
in the preliminary examination was in such a low concentration that it did not
appear in the count. A blank space indicates that the organism was not found
in the sample collected on that date. Column S is used to designate the
examiner's subjective opinion of the five dominant taxa in a sample, based
upon relative size and concentration of the organism. The percent column (%C)
presents, by abundance, the percentage composition of each taxon.
10
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LITERATURE CITED
Basharin, G. P. 1959. On a statistical estimate for the entropy of a
sequence of independent random variables, pp. 333-336. In: Theory of
Probability and Its Applications (translation of "Teoriya Veroyatnosei i
ee Premeneniya"). N. Artin (ed). 4. Society for Industrial and
Applied Mathematics, Philadelphia.
Brillouin, L. 1962. Science and Information Theory (2nd ed.). Academic
Press, New York. 351 pp.
Hutchinson, G. E. 1967. A Treatise on Limnology. II. Introduction to Lake
Biology and the Limnoplankton. John Wiley and Sons, Inc., New York.
1,115 pp.
Nygaard, G. 1949. Hydrobiological studies of some Danish ponds and lakes.
II. (K danske Vidensk. Selsk.) Biol. Sci. 7:293.
Palmer, C. M. 1969. A composite rating of algae tolerating, organic
pollution. J. Phycol. 5:78-82.
Pielou, E. C. 1966. The measurement of diversity in different types of
biological collections. J. Theor. Biol. 13:131-144.
Prescott, G. W. 1970. How to Know the Freshwater Algae. William C. Brown
Company, Dubuque. 348 pp.
Sager, P. E., and A. D. Hasler. 1969. Species diversity in lacustrine
phytoplankton. I. The components of the index of diversity
from Shannon's formula. Amer. Natur. 103(929):51-59.
Shannon, C. E., and W. Weaver. 1963. The Mathematical Theory of Commu-
nication. University of Illinois Press, Urbana. 117 pp.
U.S. Environmental Protection Agency. 1975. 'National Eutrophication Survey
Methods 1973-1976. Working Paper No. 175. Environmental Monitoring and
Support Laboratory, Las Vegas, Nevada, and Corvallis Environmental
Research Laboratory, Corvallis, Oregon. 91 pp.
Wilhm, V. L., and T. C. Dorris. 1968. Biological parameters for water
quality criteria. Bio-Science. 18:477.
Zand, S. M. 1976. Indexes associated with information theory in water
quality. J. Water Pollut. Contr. Fed. 48(8):2026-2031.
11
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APPENDIX A
PHYTOPLANKTON SPECIES FOR THE STATE OF IOWA
12
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Achnanthes sp.
Aotinastrum hantzschii
Amphora sp.
Anabaena planotonica
Andbaena spiroides
Anabaenopsis circularis
Anabaenopsis raciborskii
Ankistrodesmus falcatus
Aphanisomenon flos-aquae
Aphanizomenon flos-aquae
v. gracile
Aphanocapsa delioatissima
Aphanocapsa elachista
Aphanooapsa elachista
v. planotonioa
Aphanothece castagnei
Aphanothece clathrata
Arthrodesmus sp.
Asterionella fovmosa
Botryocoocus bvaunii
Caloneis amphisbaena
Caloneis lewisii
v. inflata
Carteria sp.
Ceratium hirundinella
Ceratiwn hirundinella
v. furooides
Ceratium hirundinella
v. robustum
Ch-ilomonas ? paramaeoium
Chlamydomonas pseudopertyi
Chlorogonium sp.
Chrooooccus dispersus
Chroococcus dispersus
v. minor
Chroooocous lirmeticus
Chroomonas nordstedtii
Closteriopsis longissima
Closteriim gracile ?
Cooooneis placentula
Cooooneis placentula
v. euglypta
Coelastrum cambricum
Coelas trim cambricum
v. intermedium
Coelastrwn retioulatwn
Coelastrum sphaerioum
Coelosphaerium minutissimum
Coelosphaerium naegelianum
Cosmarium clepsydra
v. nanwn
Crucigenia apioulata
Crucigenia quadrata
Crucigenia rectangularis
Crucigenia tetrapedia
Cryptomonas erosa
Cryptomonas marssonii
Cryptomonas ovata
Cryptomonas reflexa
Cyclotella meneghiniana
Cylindrospermum stagnale ?
Cymatopleura elliptica
Cymatopleura solea
Cymbella affinis
Cymbella triangulum
Dactylococoopsis irregularis
Diatoma vulgare
Dictyosphaerium pulchellum
Dinobyron cylindricum
Dinobyron divergens
Dinobyron sertularia
Dinobyron sociale
Elakatothrix gelatinosa
Epithemia turgida
Errerella ? bornhemiensis
Euastrum dentioulatum
Eudorina elegans
Euglena acus
Euglena deses
Euglena graoilis
Euglena oxyuris
Euglena sciotensis ?
Euglena spiroides
Euglena tripteris
Eunotia gracilis
Fragilaria construens
Fragilaria crotonensis
Fragilaria intermedia
Franceia sp.
Glenodinium aoiouliferum
Glenodinium gymnodinium
Glenodinium gymnodinium
v. biscutelliforme
Glenodinium oculatum
Gloeocystis vesiculosa
Golenkinia sp.
Gomphonema acuminatum
v. coronata
13
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Gomphonema constvictum
Gomphonema parvulum
Gomphosphaeria
Gyrmodinium albulwn
Gymnodinium ordination
Gyrosigma sp.
Kirchneriella elongate.
Kirchneriella lunaris
v. irregularis
Lagerheimia citriformis
Lepocinclis aouta ?
Lepocinclis butschlii
Lyngbya circumcreta
Lyngbya limnetica
Mallomonas acaraides
Mastogloia sp.
Melosira distorts
Melosira granulata
Melosira granulata
v. angustissimct,
Melosira granulata
v. angustissima f. spiralis
Melosi.ro. i,slandica
Melosira var-ians
Merismopedia minima
Merismopedia punotata
Merismopedia tenuissima
Mesostigma viridis.
Miorooystis aeruginosa
Microoystis inaerta
Mieroeystis stagnalis
Navieula aryptocephala
Navicula ouspidata
Naviaula ouspidata
v. ambigua
Naviaula exigua
Navieula zanoni
Nitzsohia aeicularis
Nitzsohia filiformis
Nitzsohia holsatioa
Nitzsohia palea
Nostoo sp.
Oooystis submarina
Oseillatoria agardhii
OsaHlatoria lirnnetioa
Osaillatoria subbvevis
Pandorina monm
Pediastnan bioaudata
v. longecomutum
Pediastrum boryanum
Pediastrum duplex
Pediastvum duplex
v. clathratum
Pediastnan duplex
v. reticulation
Pediastnan kawraiskyi
Pediastrum simplex
Pediastrwn tetras
Pediastnan tetras
v. tetraodon
Peridinium oinotum
Peridiniwn inconspieuum
Peridinium quadridens
Peridinium umbonatum
Phacus aotminatus
Phaaus caudatus
Phacus longicauda
Phacus megalopsis
Phacus nordstedtii
Phacus orbicularis ?
Phacus pleuronectes
Phacus pseudonordstedtii
Phacus pyrum
Phacus tortus
Phormidium mucicola
Pinnularia sp.
Polyedriopsis sp.
Pteromonas angulosa
Quadrigula sp.
Raphidiopsis curvata
Rhoicosphenia sp.
Rhopalodia gibba
Scenedesmus abundans
Scenedesmus acuminatus
Scenedesmus arcuatus
Scenedesmus bicaudatus
Scenedesmus bijuga
Scenedesmus bijuga
v. flexuosus
Scenedesmus denticulatus
Scenedesmus dimovphus
Scenedesmus granulatus
v. longispina f. granulata
Scenedesmus intermedius
Scenedesmus intermedius
v. bicaudatus
Scenedesmus protuberans
Scenedesmus quadricauda
Scenedesmus quadricauda
v. biornatus f. giganticus
14
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Scenedesmus quadricauda
v. quadrispina
Soenedesmus reniforme
Schizochlamys ? oompaota
Schroederia setigera
Spermatozoopsis sp.
Sphaerocystis schroeteri
Spirogyra sp.
Staurastrum chaetocerus
Stauraatrwn tetracerum
Stauroneis
Stephanodiscus astraea
Stephanodiscus hantzschii ?
Stephanodisaus niagarae
Surirella angustata
Synedra acus
Synedra ulna
Tetraedron oaudatum
Tetraedron aaudatum
v. longecomutum
Tetraedron eons trie turn
Tetraedron hastatum
Tetraedron minimum
v. scrobiculatum
Tetraedron muticum
Tetraedron regulare
Tetraedron regulare
v. incus
Tetrastrum elegans
Tetrastrum heteraaanthum
Tetrastrum staurogeniaeforme
Trachelomonas atomaria
Traahelomonas ensifera
v. Javanioa
Traehelomonas fluviatilis
Traahelomonas gibberosa
Trachelomonas intermedia
Trachelomonas oblonga
Trachelomonas planctonica
Trachelomonas pulchella
Traahelomonas scabra
Trachelomonas urceolata
Trachelomonas volvoaina
Treubaria sp.
Westella -botryoides ?
15
-------
APPENDIX B. SUMMARY OF PHYTOPLANKTON DATA
This appendix was generated by computer. Because it was only possible to
use upper case letters in the printout, all scientific names are printed in
upper case and are not italicized.
The alphabetic phytoplankton lists include taxa without species names
(e.g., EUNOTIA, EUNOTIA #1, FLAGELLATE, FLAGELLATES, MICROCYSTIS INCERTA ?,
CHLOROPHYTAN COCCOID CELLED COLONY). When species determinations were not '
possible, symbols or descriptive phrases were used to separate taxa for
enumeration purposes. Each name on a list, however, represents a unique
species different from any other name on the same list, unless otherwise
noted, for counting purposes.
Numbers were used to separate unidentified species of the same genus. A
generic name listed alone is also a unique species. A question mark (?) is
placed immediately after the portion of a name which was assigned with
uncertainty. Numbered, questioned, or otherwise designated taxa were
established on a lake-by-lake basis; therefore NAVICULA #2 from lake A cannot
be compared to NAVICULA #2 from lake B. Pluralized categories (e.g.,
FLAGELLATES, CENTRIC DIATOMS, SPP.) were used for counting purposes when taxa
could not be properly differentiated on the counting chamber.
16
-------
LAKE NAME: ACOUABI
NUMBER: 1901
NYGAARO TROPHIC STATE INDIrFS
DAT? 04 17 74 07 02 76. 09 25 74
MYXOPHYCEAN
CHLQRQPHYCEAN
E'JGLENOPHYTc
01 ATOM
COMPOUND
2.03 E
3/01 0
O.SO E
0.50 E
5.01 E
6.00 E
1.30 E
0.4.3 e.
0.75 E
13.0 ?
3.50 ?
3.00 P
0.15 ?
?.00 F
q.50 c
PALMER'S ORGANIC PQLLUTON INfMCES
OAT? 04 17 74 07 02 74 QO 25 T^
GENUS
SPECIE'
05
03
09
00
06
00
SP=CIFS DIVERSITY AND APUNOANC?
OAT?
04 1T 74 07 02 74.
SVER.AGE DIVERSITY
NUMBER OF TAX*
NUMBER OF SAMPLES COMPOS ITEO
•«AXI««UM DIVERSITY
MINUMUM DIVERSITY
TOTAL DIVERSITY
OF INDIVIOUALS/ML
rVENESS COMPONENT
RFLATIve FVEN^SS
OF INOIVTOUALS/TAXA
MOST ABUNDANT T SXON
TOTAL NUMBER
MEAN NUMBER
NUMBER/ML r*
25 74
H
s
M
MAXM
MINH
n
N
J
RJ
L
<
2.47
14. 00
1. 00
3.31
0.11
3324.62
1346. 01
0.65
0.64
O6. 14
475.00
2.62
21.00
1.00
4.3°
0.13
5067.0?
1934.03
0.60
0 .59
9?. 10
575.00
2.36
22.00
1.00
4.46
0.1 5
3894.00
1650.30
0.53
0.52
75.00
769.00
17
-------
LAKE NAME: ACOUABl
STORET NUMBER 1 190)
T»X»
ANABAENA
ANABA?NA l\
ANABAFNA PLANCTONIC*
APHANIIOMENON FLOS-AQUAE
ASTERIONEILA FORMOSA
CALONEIS LEWISII
V. INFLATA
CENTRIC DIATOM
CERATIUH HIRUNDINELLA
CLOSTFRIUM ft
cocroin CHRYSOPHYTAN
COELASTRUM CAMRRICUN
COELOSPHAFRIUM MINUTISS1MUM
COELOSPHAER1UM NAEGELIANUM
CRUCIGENIA APICULATA
CRYPTOMDNAS EROS*
CRYPTOMONAS REFIEXA
EUOORINA ELECANS
FLAGELIATE II
FRACILARU
IFPOCINCIIS
LYNGBVA
MAllOMONAS ACAROIOES
MFIOSIRA GRANUIATA
MFIPSIRA GRANULATA
V. ANGUSTISSIMA
MF.LOStRA VARIANS
HICROCYSTIS AERUGINOSA
NlT7SCHIA II
NITZSCHIA 12
N1TZSCHIA 13
NlTZ5CHIA 14
NOSTOC
nnCYSTIS
OSrilliTORIA AGAROHII
OSCIllAIORIA LIMNETIC*
PEDIASTRUM DUPLEX
V. RETICUIATIIM
PTEROMQNAS ANGULOSA
SCENEOESMUS ARCUATIIS
SCHSOFOERtA SETIGEPA
SPHAEROCYSTIS SCHROETERI
STAURASTRIIM CNAETOCERUS
SYNEDPA ULNA
TRACHFLOMONAS ATOMARIA
TRACHFLOMONAS INTERMEDIA
TOACHFIOHONAS 081ONGA
TRACHELOMONAS PLANC TONICA
TOTAL
CONTINUFO
0* IT T*
OT
FORM
FIL
Fll
FIL
FIL
CEL
CEL
CEL
CEL
CEL
CFl
COL
COL
COL
COL
CEL
CEL
COL
CEl
CEL
CFL
FIL
CEL
CEL
CEL
CEL
cm.
CEL
C6L
CEL
CEl
CEL
CEl
Fll
Fll
COL
CEL
COL
CEL
COl
CEL
CEl
CEL
CEl
CEL
CEl
ALGAL
UNITS
S XC "FR Ml
*
1
Z
?
t
U.T
I*.T
20.6
5.9
3.0
s.a
35.3
lie
198
277
X
• x
79
X
40
X
X
119
X
*7»
X
ALGAL
UNITS
S XC PFR ML
1129.71 575
*
3
S
2.7
16.2
2.7
'
5.4
'
?.7
2.7
S.4
2.7
X
52
X
314
X
X
X
52
X
X
X
X
115
X
52
X
52
105
52
12129. T| 575
Air.M
IM!»<
s tr p« MI
1 1
4| 4.7| TT
1 1 x
31 9.31 154
5
2
1
?.J
2.1
.
2.3
23.3
46.5
2.3
X
X
X
3»
J«
»
'•
X
'»'
X
x
76*
X
3D
X
X
t
4.7| 7T
2.31 •*«
1
1)46 1934 1*50
18
-------
LAKE NAME: BIG CREEK
STOPFT NUMBER: 190?
NYGAARD TROPHIC STATE INDIC"
D4T = 04 \H 74 07 09 T4 09 ?5 74
MYXQPHYC54N
CHLOROPHYCEAN
EUGLENQPHYTc
OIATO"
COMPOUND
0/0 0
02/0 P
1.00 E
0.4) E
06/0 E
01/0 «•
0/0 ri
1.00 E
0.50 F
03/0 c
2.00 E
0/05 ?
1.00 e
7.00 c
SPECIES
S ORGANIC POLLUTION
OAT= 0* 13 74 07 09 74 09 25 74
06
03
00
00
SPECIES DIVERSITY AND 4BUND4NCE INTIC5?
OATE 04 IB 74 07 09 74 09 25 74
4VEPAGF DIVERSITY
NUMBER OP TAXA
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY
DIVERSITY
01VER SITY
TOTAL NUMPEO OF INDIVIDUALS/ML
EVENF.SS COMPONENT
RFLATTV? PVEMESS
MEAN NUMBER o^ INOIVIDUALS/TAXA
NUMBER/ML C* ««nST ABUNDANT TAXCN
H
<;
M
"AX"
MINH
n
V
J
R J
L
K
0. 80
19.00
?.oo
4. 25
0.0?
13274.40
16593. 00
0.19
0.19
973.3?
14887.00
1.20
7.00
2.00
2.a!
0.06
1317.60
1099.00
0.43
0.42
156.96
595 .00
1.58
20.00
2.00
4.?2
0.14
2629.12
1664.00
0.37
0.35
33. ?0
1167.00
19
-------
LAKE NAME! BIG CREFK
NUMBER: 1902
TAXA
ANK I STRODE SHUS FAlf.ATUS
APHANIl'JMENON FIOS-AOUAE
APHANOTHECE CASTAGNEI
ASTERIONELLA FORMOSA
CERATIUM HIRUNOINELLA
f. RPBUSTUM
CHILOMONAS 7 PARAMAECIUH
CHLAMYDOMONAS
CHIOROPHYTAN FLAGELLATE
COCCGNEIS PIACENTU.A
V. EHGIYPTA
COELASTRUM CAMBRICUM
COSMARIUN II
CRYPTDMONAS ft
CRYPTOMONAS 12
CRYPTHMONAS EROS A
CRVPTHMONAS REFLEXA
CYHATOPLEURA SOLEA
OINORRYON SER TUI ARIA
EUOORINA ElEGANS
EU CIENA
FLAGELLATE II
FLAGFllATE IT
FRAGILARIA CROTONENSIS
GLENOnlNlUM AC1CUIIFEBUM
GlENOnlNlUM OCULATUM
GLnEOCYSTIS VES1CULOSA
CONTINUE"
GYHNOOINIUM OROINATUN
HFLOSIRA GRANULATA
NAVICULA
NITtSCHIA II
OSCILLATORIA LINNET ICA
PANOORINA HORUH
PEOIAfTRUN DUPLEX
PHACUS CRBICULA^IS ?
RHOICnSPHENIA
SCENEOESHUS OUADRICAUOA
V. OUAORISPINA
STFPMANOOISCUS ASTRAEA
STEPHANOniSCUS MANTIS CHI I 7
TRACMELOMONAS
TOTAL
0* 18 74
07 09 74
FORM
CEL
FIL
COL
CEL
CEl
CEL
CEL
CEL
CEL
COL
CEL
CEl
CEL
CEL
ca
CEL
CEl
COL
CEl
CEL
CEL
CEL
CH.
CEl
COL
CEl
CFL
CEl
CFL
CEL
CEL
FIL
ecu
COL
CH
CEl
COl
CEL
ALGAL
UNITS
? tC PER Ml
SI 1.31 2SO
*
3
?
1.3
0.5
0.8
2.3
1.8
0.5
0.3
0.3
1.0
0.3
20B
X
83
X '
129
X
37*
291
83
42
42
166
42
X
X
X
CFl 11189.71 14887
CH. 1 1 1 X
ALGAI
UNITS
S tC PER ML
I
3
2
54.2
4.2
41.6
X
595
X
46
X
X
457
Air.n
UNI TS
S rr PF» MI
4
5
2
t
3
1
2.41 41
2.4| 40
2.4
1.2
2.4
15.4
70.1
1.2
2.4
X
X
X
X
X
40
X
X
?0
'0
fit
X
1167
X
20
X
X
'0
16593
1098
20
-------
LAKE NAME: RLACK HAWK
STCPFT NUMBER: 190'
NYGAARO TPQPHIC STATE IMOrrcS
OATP }A \r) 7<, 37 33 74 )9 7? 74
"YXOPHYCEAN
DIATOM
COMPOUND
04/0 F
0.10 ?
0.83 E
26/1 E
?.00 F
4.67 c
0.10 ?
0.2? ?
3.00 P
7.00
6.3}
0.23
1 .A?
19.5
PALME"*? ORGANIC POLLUTION tNor~=s
OATS 14 1<) 74 07 03 74 09 25 74
GENUS
16
11
06
04
27
SPECIES OIVERSITY ANO ABUNDANCE
OAT=
SVERAG? OIVEOSITY
NU^BP« HP TAXA
NUMBER OF SAMPLES COMPOSITED
MAXIMUM TIVE'SITY
MINUMU« DIVERSITY MINM
TOTAL OTVC3SITY
TOTAL NUMBER OF INOt VI OUALS/ML
EVFNeSS COMPONENT
MEAN NUMBER OF INOI VIO'JAL S/TA XA
NU««B6R/ML CF MCST ABUNCANT TAXON
04 19 74 07 03 74 09 25 74
H
S
«
XH
NM
n
*j
J
»J
L
<
2.77
3<». 33
2.00
5.29
0.01
163690.38
59094.30
0.52
0.53
1515.23
20231.00
2.39
39.00
2.00
5.29
0.02
60052.16
25232.33
0.45
0.45
646.97
9323.00
3.05
47.00
2.00
5.55
0.01
165667.80
54316.33
0.5 =
0.55
1! 55. (S 6
29097.00
-------
LAKF NArE : BLACK HAWK
S10BET NUMBER I 1903
CONI1NUEH
74
07 01 7*
TAXA
ACTINASTRUM
ANABAFNA
ANABAFNOPSIS CIRCULAR IS
ANABAF.NOPSIS RACIBORSKII
ANKISTRQOESMUS FALCATUS
APHANI70MENON FLOS-AQUAE
APHANIfOMENON FLOS-AQUAE
V. GRACILE
APHANOCAPSA ELACHISTA
APHANOTHECE
ASTER IONELLA FORMOSA
CERATIUM HIRUNDINEUA
F. FUBCOIOES
CHLAMYDOMONAS
CHROOCOCCUS OISPERSUS
CH»OOCOCCUS OISPERSUS
V. MINOR
CinSTERIOPSIS
CLOSTERIOPSIS 7 LONC1SSIMA
ClOSTfRIUH
CtOSTERIUM fl
ClOSTFRIUM 12
CIOSTERIUN SPP.
COCCONEIS
COELASTRUH CAMBRICUM
COSMARIUM
CRIICIGENIA TETRAPEOIA
CRYPTOMONAS
CRYPTHMONAS EROSA
CRYPTOMONAS REFLFXA
CfttPTHMONAS SPP.
CTCIOTELLA MENFGHINIANA
CVPATOPIEURA SOLE A
CYM8EUA TRIANGULUM
DACTYLOCOCCOPSIS
BICTYOSPHAERIUN
ElAKATOTHftlX
ELAKATQTHRIX GELATINOS'
EPITHEHIA TURGIOA
FBREPHLA 7 BORNHEMIENSIS
EIKIENA
FLAGELLATE II
FLAGELLATES
KIRCHNERIEILA T
IF.POCINCLIS
(ttlOSIRA 14
KF.LOSIRA GPANULATA
NfLOSIRA GRANULATA
«. ANGUSTISSIMA
HEPISMOPEOIA MINIMA
fffRISMOPEDIA TENUISSINA
KESOSTIGMA VI HI 01 S
HTCROCYSTIS AERUGINOSA
KICROCYSTIS INCERTA
MAVICULA
1AVICULA II
HI175CHIA ACICULARIS
KITZSCHIA PALEA
•OSTOC
OdCYSTIS
OSCILLATORIA
OSCILIATORIA II
OSCILLATORIA 12
PEOIASTP.UN BORYANUM
rfOIASTRUM DUPLEX
PFOIASTRUM DUPLEX
V. RETICULATUM
PEDIASTRUM KAWDAISKVt
PEOIASTRUM TETRAS
PHACUS
fHACUS CAUOATUS
PMACUS HEGALOPSIS
PHACUS PYRUM 1
PINNUHRIA
OUADRIGULA
SCENEOESMUS
SCENEOESMUS ABUNOANS
SCfNEDESMUS ACUMINATUS
SCENEOESMIIS OIMORPHUS
SCENEDESHUS INTERMFOIUS
SCFNFOESMUS PROTUBFRANS
FORM
CEl
FIL
ML
FIL
CEl
CEL
Fit
COL
COL
CEL
CEL
CH
COL
COL
CFl
CEL
CEL
CEL
CEL
CH
CU
COL
CFL
COL
CEL
CEL
CF.L
CH
CEL
CEL
CEL
CEL
COL
CEL
COL
CEL
CEL
m
CEL
CEL
CEl
CFL
CEl
CEl
CEl
COL
COL
CEL
COL
COL
CEl
CEl
CEl
CEL
CEL
CEl
HI
ML
FIL
COl
COl
COL
cm
cm
CEl
CEl
CH
CEl
CEL
CEL
COl
COL
COl
COl
coi
COL
ALGAL
UNITS
1C °ER ML
0.21 106
1 X
1
1
*.9| 2875
1
1
1
1
1
1
1
1
1 X
1
1
1
0.4) 213
1
1
1
1
1
1 X
1 X
1
1
1
1 X
1 X
5.»l 319*
l.*l 812
O.*l 21)
1
1.6| 958
1 X
1
1
1
1
1 X
13.51 7986
3.11 1810
1
1
1.11 639
1 X
1
1
l.*l 8V
1
0.21 106
1
1
0.51 319
1
34.21 20231
0.7) 426
1
1
1 X
1
1
1
0.21 106
1
1
1
1
0.4) 213
1
1
1
1
1 X
1
1
0.21 106
0.4) 213
0.7| 426
1 X
ALGAL
UNITS
TC PF.R ML
1
I. 7| 417
36.9
0.4
0.2
4.6
1.3
1.9
O.A
0.4
0.6
22.
9323
X
X
X
X
X
93
46
X
1160
325
X
X
371
139
X
X
93
139
X
X
X
X
5612
X
X
X
•-
X
X
X
X
AIC.AI
UNITS
TC P« Ml
3.11 169T
1.31 479
1 X
1.9) 10H
1
0.61 ?^9
1
4.7| ??46
0.6| >39
o..6| '39
1
1
22
-------
I. IKE N4MEI BL»CK HtMK
S100ET NUNFIER: \903 -
TAX*
CONTINUED
7*
07 01 7*
0" ?•> 74
SCENEOESNUS OU«0«1CAUO«
SCEWEOESMUS SPP.
SCMBneOERIA SETIGERA
SPHAEROCYSTIS SCHRnETERI
SIEPW4MOOI SCUS II
STEPHtNOniSCUS 12
STEPHAN001SCUS »STB»E*
STFPM1NOOI SCUS NIAr,»B»E
SUR1BHI* II
SUflOEll* 12
IET04STBUM ELEONS
TETRASTRUM HETF«»C*NTHUM
IE1R4STRUH SPP.
TFTRkSTRUN ST4U90CFNI46FOOHE
TROCHEIOMONAS «l
t«»CHElOMON»S *t
T»»CMELOMON4S FLUVI»TIIIS
TDT»l
FORM
coT"
COL
CEt
COL
CEL
CEL
CEL
CFL
CEL
CF.L
COL
COL
COL
COL
CEL
CH.
CEL
»LGU
UNITS
S *C PER ML
2
28.1
I.I
X
X
16611
X
X
639
X
ALCiL
UNITS
S tC PER ML
*
2
0.61 139
1
O.*l 93
24.61 6**T
3.3
835
X
X
X
Al f.Al
l«l TS
S tC Pf» «l 1
5
1
0.5) 755
3.31 1782
0.31 170
4.51 7*61
0.2
K*
X
o.X m
1
5909* 25232 5*316
23
-------
LAKE NA*E: CLEW
STCPET NUMBER: 1904
NYGAA90 TROPHIC STATE
DATE 04 1? 74 07 03 76
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTc
OI4TOM
COMPOUND
3.50 E
5.51 F
0.0*. ?
0.51 E
10.5 E
3.00 E
5.50 E
0/17 ?
0.43 E
10.0 F
)9 •>•>, 74
12.0 B
12.) F
0/24 ?
1.00 E
PALMER'S ORGANIC POLLUTION
(J6. iq 74 07 03 7fc 09 23 76.
GENUS
SPECIES
14
16
06
04
0'
00
SPECIES DIVERSITY AMP AeuNOAMCE INDICES
OAT<= 04 18 74 07 03 76 Q9 ?3 74
AVERAGE DIVERSITY
NU^BEfi OP T4XA
NUMBER OF SAMPLES COMPOSITED
"INUMIJ" DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ ML
EVENPSS CCMPONENT
RELATIVE SVENESS
MEAN NUMBER OF INDI V IDUAL S/TAXA
NUMBER /ML OF MOST A8UNCANT TAXON
H
s
<<
MAX"
MIN"
0
"4
J
. RJ
L
<
2.94
33.00
3.00
5.04
0.03
44667.42
15193.00
0.59
0.59
460.39
5340.00
2.73
39.00
3.00
5.29
0.04
39915.16
.14322.00
0.5?
0.53
367.23
5919.00
2.2?
32.00
3.00
5.00
0.0?
35453.40
15970.00
0.46
0.45
49.06
3132.00
24
-------
LAKE HHHt I CLEAR
STORET NUMBER! 190*
TAX*
ACTINASTRUM
ANABAENA PLANCTONICA
ANAMFNA SPIR010ES
AN*tSTRODESNUS FAICATUS
APHANOCAPSA OE11CATISSIMA
APMANOCAPSA ElACHISTA
APHANOTHECE 7
ASTERICmEllA FORMOSA
CERATIUM HIRUN01NELLA
r.m.AMYOr>MONAS
CHBnncoCCUS LIMNETICUS
CHUOONONAS NOROSTFDTII
COELOSPHAERIUM
COEIOSPHAERIUM NAEGELUNUN
COSNAR1UM
COSMARIOM 12
CRUCICENI* OUAORATA
CRUCIGENIA RECTANGUIARIS
CRYPTDMQNAS
CVANOPHYTAN FILAMENT
CYMBElLA II
CYMBKIA 12
CVMBELLA SPP.
DICTVOSPHAERIUM PULCHEILUM
DINCBRYON CYLINORICUM
01 NOBBVON OIVERGENS
DINOBRYON SPP.
ELAKATOTHRIX
FLAGELLATE II
FRAGUARI* It
F«AGIIAAIA CONSTRUFH5
FRAGIlARIA CROTQNENSIS
GIF.NnniNIUM GYMNaDINIUV
V. 8ISCUTELL I'ORNF
COIIPHONEMA CONSTRKTUM
GOTPMOSPHAERIA
GlfNODINIUM
XIHCHNERIEUA
IYNGBYA
IVNG8VA II
IYNG8YA LIMNETICA
MELOSIRA
MELOSIRA CRANIA AT A
HEIOSIRA ISIANDICA
MEIOSIRA SPP.
HfRISKOPEOIA MINIMA
MICPOCYSTIS 7 STAGNALIS
MICDOCYSTIS II
HICaOCYSllS AERUCINOSA
HICROCYSTIS INCERTA
MIOOCYSTIS STAGNAl IS
OflCYSTIS
OSCILIATORIA
PEOIASTRUM II
PEOIASTRUM BORVANUM
PEOIASTRUM tXIPlEX
PEOIASTRUM DUPLEX
V. CLATHRATUM
PEOUSTRUM KAMPAISKYI
PE*IDINIUH CINCTUM
• APHIOinPSIS CURVATA
SCENEOESMUS ft
SCENEOESNUS BIJUGA
V. FIEXUOSUS
SCtNFOESMUS OIMORPHUS
SCENEOESMUS OUAORICAUOA
SCENEDESMUS OUAORICAUDA
V. HIORNATUS F. GIGANTICUS
SCENEDESMUS SPP.
SCHROEDERIA SETIGEPA
SPHAEROCYSTIS
STATOSPOP.E IDIN06RVON CIVERGENSI
STAURASTRUN
STAURASTRUM II
SIAURASTRUM I)
STAU»ON?IS
STFPHANHOISCUS ASTRAEA
SVNEORA ULNA
TFTRAFORON CAUOATUM
TRACHELOMONAS VOLVOCINA
TOTAL
CONTINUEO
0* 18 7*
07 OJ 7*
09
FORM •
ca
Ftl
Fll
CEL
cot
COL
COL
CEL
CEL
CEL
COL
ca
COL
COL
CEL
CEL
COL
COL
CEL
FIL
CEL
CEL
CEL
COL
CEL
CEL
CEL
CFL
CEL
CEL
CEL
CF.l
CEL
ca
COL
CEL
CEL
ML
FIL
Fll
CEL
CEL
CEL
CEL
COl
COL
COL
COL
COL
COL
CEL
FIL
COL
COL
COL
COL
COL
CEL
FIL
COL
COL
COL
COL
COL
COL
CEL
COL
CEL
CEL
CEL
CEL
CEL
ca
CfL
CFL
CEL
ALGAL
UNITS
1C PER ML
1 X
1
1
0.9| 1*0
1
1
1 X
s.el 86*
1
1
1
1
1
1 X
1
1
0.31 47
1
3.*l 911
1
1
1
1
1 X
1
3S.lt 53*0
1
2.81 M9
5.21 793
1
1
13. SI 2091
1
1
0.31 *7
0.61 93
1.21 187
1
2.*l 370
0.9| 1*0
22.61 3*32
1
t
1
0.31 *7
1
1
1
1
1
1
0.91 1*0
0.31 *6
1
1
1
1
1 X
1 X
1
1
1
1
1 X
1
1
1
0.91 1*0
0.61 93
1
1 X
1 X
1
1 X
1 X
0.61 93
0.6) 93
I
0.31 *7
ALGAL
UNITS
XC PER Ml
1 1
1 3.31 *77
1
1
1
1
1
1 «
0.81 111
1 X
1
o.ai 119
1.21 1609
1
1 x
1
1
1
1
1
1 x
1 x
1.21 1T9
O.*| 60
1 X
1 X
1.21 179
1 X
0.81 119
1 X
1 X
3.7| 536
|
1 X
1 X
1
1
1 x
1.7| 23»
1
1
1
1 X
1 X
*1.3I 5919
1.7| 238
[ 22.91 3277
1
|
1
1
5 3.7| 536
1
1
O.*l AO
1
1
1 X
1 x
1
1.21 179
O.*l 60
1
1 x
1
O.*l 60
1
1
1
1.21 179
1
1
1
1 X
1
1
1.21 179
1
1
1
Ainu
UNI T *
! 1C P?R •*
?2.9
l.«
•).*
0.7
0.7
1.5
».«
2.9
11.8
X
365'
?°5
59
X
X
I
X
11"
Ml
?36
73*
X
X
*71
X
X
1RP.6
X
X
2.6) *I2
0.7| U»
50. 9| 813?
O.*l 59
0.*
a. 7
X
50
X
X
X
ll«
X
X
15193
1*322
15971)
25
-------
LAKE SAKE: UARLING
STORET NUMBER: 1905
NYGAARO TROPHIC STATE INDICES
DATE 0* 18 74 09 24 74
MYXQPHYCE.AN C2/0 E 1.00 fc
CHLOROPHYCEAN 02/0 £ 1.50 E
EUGLENOPHVTE 0.75 £ 0.40 E
DUTUfl 0.50 E 01/0 E
COMPOUND 08/0 E 4.00 E
PALMER'S ORGANIC POLLUTION INDICES
DATE 04 18 74 09 24 74
GENUS
SPECIES
09
03
02
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER of SAMPLES COMPOSITED
MAXIMUM DIVERSITY
P1NUMUH DIVERSITY
TOTAL DIVERSITY
TOTAL NtMBER OF INDIVIDUALS/MI
IVENESS CUHPCNtM
RELATIVE EVENESS
MEAN NUH&Efc of INDIVIDUALS/TAXA
NUM8t.fi/fU Uf MOST ABUNDANT IAXON
DATE
H
S
N
HAXH
HINH
0
N
J
RJ
L
K
04 18 74 09 24 74
2.45
19.00
2.00
4.25
0.09
6220.55
2539.00
0.58
0.57
133.63
1367.00
1.45
15.00
2.00
3.91
0.03
10682.15
7367.00
0.37
0.37
491.13
5665.00
26
-------
I AM «AJI£I UA811NC
SIO«EI MMBtRl 190)
1414
ANABAiMA PIAHCTONICA
AN* is MODE SMS FAICAIUS
APHAMUUIUNOM FlOS-AOUAf
CONTINUtO
18 74
coccaib cfii
COELAST*IM CAM* 11 UN
CKTPrCXUMkS HOSA
C8TPICHOMAS SfP.
CTAKOPMTIAII MlAIUHl
DINCBBTOfc DIVIB6ENS
tUGUHA »1
tUt KM «2
FLACilLAIE fl
CTRHOUINIUH
(IKCHHtlilELL*
IEPOCIMC1IS >1
KPOCIHCtlS 12
MEIUSI** 6«»»Ol»I»
MAV1CU1A fZ
NAVICUIA SPP.
NAVlCtiA ZAMONI
PAIPXLLOIO CHIORUPHTIAN CGIGHI
QUAO«1CULA
1APNIOIUP5IS CIMVAI*
SCHIQiOiltIA SCTUIkA
STtPHAHUDlSCUS
ItACHIiUHUHAS
TOTAL
>0*N
Ml
CEl
Ml
Cll
CEl
COl
CEl
CEl
CEl
Ml
CEl
CEl
Cfl
CEl
CEl
CEl
CEl
CEl
CEl
CEl
Cfl
CEL
CEl
CEl
CEl
COl
CEl
COl
f II
CEL
CEl
CEL
S 1C
1 1
21 7.71
4
1
3
5
1
1
1.41
1
|
1
33.81
0.71
3.91
1
1
1
2.11
3.JI
11.21
1
1
2.11
1
2.11
1
1
1.41
1
1
2.11
1
• .41
1
1
1
AL6AI
UNI IS
Hi Ml
19*
36
1
1367
18
89
X
I
X
>3
89
284
S3
43
X
36
X
43
213
S XC
1
4
2
1
1
76.91
0.41
I
0.81
0.31
7.81
1
I
1
1
1
1
1
4.31
1
1
1
1
O.SI
1
0.61
|
1
1
C.6I
I
3.31
1
3.21
1*4 2.11
131 1.31
AlCAl
UN IIS
Pl« Nl
1
4664
40
39
20
474
317
I
»9
»9
59
20
238
1*8
99
2»3*
7367
27
-------
LAKi NAME: LCST INLAND
STORE! NUMBER: 1906
NYGAAKO TROPHIC STATE INDICES
OAlt C9 Z3 7*. 0
-------
IAKE NANft IOST ISIAHO
STOkEI MUaeERt 1906
TAl*
AC I IMAS1KOK
ANAbAlfcA
AkAtAtNA *1
ABA I At MA 1Z
MWISTIUUE SHUS
A*HMn/OHENOM FIDS-AQUAE
ATMMOCArSA 7
A*HANOIHtC( ClAIHKATA
AStEllOHtllA FOfcHCliA
CAAUVIA
CEftlBIt 01 A IOKS
cmoococcus OISPESSUS
COCCQHCIS PUCENTUIA
cotLAsrRuN cAiteaiciM
cot IOSPHAER mn
COMMBIUH
CRTPTOHONAS
c*TrTnnanAS ERUSA
CftTMl-MUNAJ REflEXA
CKTPIMIQNAS SPP.
CTMKiPMTIAN FIlAflENJ
CTCLUIEllA
CrCLOIEUA HENE6HIHUNA
CTMEUA AFMN1S
CTHSELIA SPP.
OlMOBPTOM DIVEkGENS
(IAKA>O1H« II
COMIIMUEO
23 7*
7b
tUhCIU •!
CUNOflA CDACIIIS
(•AC.I1A71A
inutmtulA
ACUH1HAIUH
. CMUNAtA
^HOHEIU CLNSIRICTUN
PARVUIUH
$P4>.
• IkCMMRlf HA
• ItCHMBIiLLA II
•ICCHMIIItllA ElOMCAIA
ITHtBTA CI*CUHCDCIA
ITIW«TA, tlnnfTlCA
6RAHUIA1A
•CLOS1IA C8AMU1AIA
1SIAH01CA
MIUSIIA SP».
MINIMA
IKKlSHOrfOIA IfNUISSMA
nUIOCTSIIS
nlCUKTSIIS 1NCERIA
MA«ICUiA CUSPIOATA.
•AVICIH.A CUiPIOAlA -
V. MI»IW«
HAVICM* Jf>.
•IT/SCM1A ACICUIAHIS
HIIZStHU HMSAIICA
HlflSCMI* PAlEA
OOCVSIIV
ate ILIA IMIA
PIDIASINU* tOITAMUH
ftblASTlUK OUPIEX
PfOIASIktm KAkRAISKTI
PC 01 AS I «UH IITBA5
PHACUS ACUKINAIUS
PMACUl ME6AiOPSlS
PHACUt SPP.
PNOKnlOIUH 12
pHOkHioiun nuciCQiA
PIHMUIA*|A
BAPHICIOPS1S
DHOPAIOOIA &IB«A
SCtHEOtSHUS ASUNtlAMS
Kj«n
ciT
Fll
Fit
fit
CEl
FH
cut
COl
CEl
CEl
CEL
COl
Cfl
CCl
COL
CEl
CEL
CEL
CEl
CfL
Fll
CEl
Cil
CEl
Cll
CEl
Cll
CCl
CEl
CEl
CEl
CEl
CU
CEl
CEl
Ctl
CEl
CEl
CEl
CEL
CEL
CEl
CEl
CEL
CEL
CEl
f 11
Fll
CEL
CEL
Ctl
CEL
CEl
CEl
CEl 3
COl
COl
CM
COl
COl
COl
CEl
CEl
CEl
CEl
CEl 1
CEl
CEl
fll
CCl
COL
COl
COl
CEl
CEl
CEl
ru
COl
CEl
Fll
CEL
COl
S SC
0.7
2.4
5 S.»
* 19.9
2.C
1.3
3.4
0.4
1.)
0.9
3.9
15.0
14.9
10.1
3.3
2.0
11.2
4.4
2.4
ALCAL AlCAl
UMITS
PER HI
2»A
939
2134
7769
761
»12
>
171
171
X
I
>9«
341
1
1
1
1)37
6147
X
X
X
X
5805
3927
I
Ittl
X
76*
43}4
171
939
X
X
X
I
UNITS
S SC PER HI
1.31 11»
1 X
r
i
> 7. HI 692
1
1
1
0.71 J«
1.31 119
1
1
3.61 317
1 X
1
0.31 29
1
1 X
1 X
1 9.71 »6i
1.31 114
1.61 144
|
1 X
1.21 2aa
4.91 432
i
l.JI So
1.91 173
1 I
1 X
C.JI 29
18.21 1614
2.61 231
2.61 231
k 6. SI »76
2.3
0.3
4.«
1..
1.0
1.3
1.6
2.3
I
X
X
X
202
29
403
86
X
X
86
Hi
X
I
X
317
1
X
202
X
I
0.31 29
0.31 29
0.31 29
1
0.71 »•
4.91 432
1 X
0.71 »•
29
-------
lA«t
STORIT
IUSI 1S1AMU
I9C'b
com INUCD
09 23
7e
!»*•
SCENiOtSMIS AC UN IN A [US
SCINEOESMIS ilJUGA
SCEN£OtSHUS OUAOKICMIO*
STAURASIMUN
STAURISIKUM li
STHEURA
STNtOPA ACUS
TE1RAIORUM CAUOAIl'M
IETKAEOROM HASTATUH
(Old
C01
cot
CO*.
C£l
C£l
Cfl
Cfl
Ctl
CI1
Cfl
CFl
Cfl
Cfl
C01
s
tc
0.7
J.»
AlfaAl
UNITS
PEk m
i
X
Z56
I
1
171
S
3
2
AlUt
JKITS
XC PEI Nl
i
2.»l 231
1.31 11»
3.71 »•
U.JI 24
1 X
1 X
I
2.31 202
1
0.71 58
1
1
1
TUIAl
393 IS
8B77
30
-------
LAKE NAME: RCbKlbfc
STUHET NUHBtR: 1907
NY&AARO TRCPH1C STATE INOICtS
UATt Zi> 18 74 07 03 7-, 09 2* V4
MYXCPHYCEAN Cl/0 £ 3.00 fc 4.CO I
CHLOROPHYCEAN C2/0 E 4.00 E 13.0 E
tUGLtNOPHYTE 0.33 E 0.43 E 0.24 I
01AIOH 3.00 E 3.00 E 0.87 t
COMPCUNO C7/0 E 13.0 E Zb .0 E
PALMER'S ORGANIC POLLUTION INDICES
CiAlE 04 18 74 07 03 74 09 24 7
-------
LAKE MHis MCBRIDE
siuitii tiunniiii isc7
CONIIMUEO
04
7*
37 03 74
09 24 7*
TAX*
AMA6AEM*
ANKISIRUUtSiMlS ftlCATUS
APHAMI20HENCM flUS-ACUAE
ASTEklONILLA FGRNOSA
CENtRIC OIAICB
CHIORGCUCCAICAN C£1L
CGCCantlS
COElUSPMAtRlUft N*t6tLlANUH
CRUClOtNIA AP1CUIA1A
CRTPTOHOMAS
CHTPtGBUMAS fRUiA
CaTPrt«OI«AS HARSSOJlll
CRYPTOHOIUS REflEIA
CTCIOUUA MNEGHINIAMA
OAcmococcorsis
OACTTIOCOCCOPSIS IRREGULAR IS
DICTYOSPHAERltm
OIN08RTON SOC 1 Alt
EUA STRUM OENTicutATuit
EUOORINA ILECAMS
EUCIEMA SCIOTENSIS I
FtACElLAlES
IRAHCt 1A
UTHMOClNlUN AltUlUN
LEPUCIHCtl!
LUNATE Cti.1
NElOSIilA «1
HELOSIKA OISTAHS
NELOillA (.CAMUIAIA
HtlOSlDA bAAMULAIA
V. AhtU^TISSlKA
HtlOSIftA 6RAMUt«f*
V. AH6UMJSSIWA t. 1PH«A11S
Hf« ISXUPiOtA TENUISSIHA
HESOSII6N*
NAV1CUIA
N1TZSCHIA
OOCTSI1S
OSCllLAIORIA I
PfOlASIUUlt KICAUOAIA
V. IClflftECOfMUIUII
PEOiAsrttim DUPtEi
V. ClArMAIUft
PtOlASTMim SIHPIEX
PENMAft OlAlOHS
PMACU5
PHACUS LUMGICAUOA
PHACUS PTRUH
PTERORUNAS AM«ULOSA
SCtHECtSHUS
SCENEOESflUS CUAOR1CAUOA
V. ?
SCENtUSmi! SPP.
SCHROEbERIA JETUIRA
SIAURASTRUN
STEPHAMODISCU3
SICPHAMOOISCUS HIA6A**f
SU«I*IILA
STHEOkA
STNEOtA AC US 1
V. SCR081CU1ATUH
TETRAEOKIM HUIICUH
TiTRASTRIM Mf KRACANIHUII
TETRAStilUH S?AtWU6fi>lAEFORHE
tRACHCLUMlllAS
TOTAL
FOKH
CEl
Fit
CEl
Fit
CEl
Cti
CEl
CEl
COl
COl
COl
CEl
CEL
CEl
CEl
CEL
CEl
CEl
CEL
COL
CEl
CEl
cat
CEl
CEL
CEL
CEL
CEl
CEl
CEl
CEl
CEl
CEl
CEl
CEl
CEl
C1L
COl
CEL
CEL
CCL
CEl
Fll
COl
COl
COl
COL
CEL
CEl
CEl
CEL
CEL
COl
COl
COl
COl
CEL
CEL
.CE-L
CEl
CEl
CEl
CEl
CEl
CEL
COl
COl
CEL
AlCAl
UNI IS
S 1C PEA ML
0.9
4.3
6*.*
4.7
21.3
3.4
>
114
»«3
8889
X
X
X
6i2
X
X
3oei
i
X
X
X
X
»7»
ALbAl
UN IIS
S U PER Ml
J.7
3.3
1.3
1.3
».3
Z.J
t.7.7
3.3
13.2
0.7
X
''
•0
X
X
X
198
79
79
X
317
119
*07T
198
792
X
X
X
o
X
1.31 79
416*1
UMIS
S 1C PER HI
1 X
|
1 I
1
1
1
0.41 37
1 X
|
1 I
1 I
6.91 63»
1
1
0.41 37
I
1 X
1.91 187
1 X
|
I
1 X
1
1 X
1 X
1
12.61 1232
O.*l 37
0.41 37
1
1
1 X
6.11 »97
38.71 3770
2.31 224
1
3.81 373
1.11 112
0.41 37
1 X
0.41 37
o.8i n
i
i i
'
1 X
1
1
1 X
8. 81 6*9
1 X
|
1 X
o.8i n
1 X
1
1
1 I
1.91 187
1
1
3.81 373
|
1 X
6. SI 63»
I t
1
0.81 7S
1 X
1 X
1.11 112
1
13RO* bCll 47*3
32
-------
LAKf HA At: PkAIRIt RUSt
STORET NUHBEK: 1903
NYGAAfcO TROPHIC SUIE INDICES
DATE 0* 17 74 07 C2 T, 0V 2'j 74
flYXOPHYCEAN 2.GO E 1.67 £ 1.67 £
CHLOKOPHYCEAN 3.00 E 2.00 E 1.67 E
EUGLENOPHYTE 0.40 E 0.18 ? 0.30 I
DIATOM 0.71 E 2.00 E 2.00 E
COMPOUND Y.50 E 5.00 E 5.00 E
PALMER'S ORGANIC POLLUTION INDICES
DATE 0*. 17 T, 07 C2 T, 09 25 74
GENUS
SPECIES
06
00
11
CO
05
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE 04 17 74 07 02 74 09 25 74
AVERAGE DIVERSITY
NUMBER OF 1AXA
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY HAXH
MINUHUH DIVERSITY HINH
TOTAL DIVERSITY
TOTAL NUH&CR OF INO I V I DUALS/ML..
EVENESS COMPONENT
RELATIVE EVENESS
MEAN NUMBER UF INOIV10UALS/TAXA
NUMBER/ML OF HOST ABUNDANT TAXON
H
S
N
XH
NH
0
N
J
RJ
L
K
2.33
36.00
2.00
5.17
0.04
30956.38
13286.00
0.45
C.45
369.06
7006.00
3.10
22.00
2.00
4.46
0.11
7483.40
2414. CO
0.70
0.69
109.73
522.00
2.41
22.00
2.00
4.46
0.12
5333.33
2213.00
0.54
0.53
100.59
68 1.00
33
-------
LAKf N»K£: PKAIRIE ROSE
STORE I NUflBtR: 1906
UXA
iNASAENA
ANA8AENA
AHB1STR00E SWIS ?
APMANUOHEN&N HOS-MMU
IPHANUAPSA
ASTERIONELLA I- DRUGS 4
BOlRTtCOCCUS BftAUNII
CEHIR1C OlAIOIf
CEIAIIUH HIRUNDINEllA
CHlAflTOOMJMAS 1
ciosrtRiuPSis LONCISSIM
CIOSURIM fi
ClbSUBIUII »2
cicsuRiuM n
coccoio CHRTSGPHTIAI.
COElASTkUH CAMBRIC UK
COELOiPHAERlUft NAE6ELIAMUH
CCSHAPIU*
CRTP10HCNAS
CkTPTCflbNAS ESOSA
CftTPTbHOHAS (ROSA I
CRTPfUIOMAS HARSSUNII
CRYPTCflCNAS HARSSOHII ?
CRTPfMOMAS REFUXA
CTBAtbPttURA U1IP11CA
DICTTQSPHACRIUfl PUlCHtllUf
DINOBRTOM OlVtRGtNS
CQN11NUEO
C* 17 7*
J7 32 7*
09 2» 7*
CU«1EMA II
(U61ENA UXTVtlJ
*1
CRUTOMtNSIS
CTIOS1CHA t
••LtOPONAS
HkiOSUA D1SIAHS
NtluSllA 6RAW11ATA
KftOSUA VA«IAH$
MICROCTSTIS AERUfclMuSA
HITZ5CHIA
•irZSCHIA •!
OOCTSIIS
OSCH.IATM1A
OSCUlAtWlA A6AKOHI1
CSC1LIATOR1A SU«BREV1$
flOIAJIRUX OUPltX
MOIASTRIM OUPiES
V. ClAfmAIUH
pcousmufi OUPIEX
*. RIIICULATUH
nOUSTRUPl SIHPltl
PEMNAU OIAIOK
FHACU3 TORTUS
PHACUJ ro«ius ?
SCEKEOESnuS OUAOtlCAUOA
SCHIZDCHIAIITS t COUP ACT A
ST AURAS TRlin
STAURAStRUH CHAEIOCERUS
SItPHAHOOIJCUf tSTRAE*
TilkAtORON CONSIRUIUH
IRACHCIUHQNAS
TRACHllOBONAS T
tRACM(t3nOMAJ V01VCCINA
TOlAt
(OBH
?IT
HI
CEl
Ml
CO!
CEL
COl
Ctl
CEL
CEL
CEt
CEL
CEL
CEL
CEL
COL
COL
CEt
CEL
Cfl
CEl
CEL
CEL
CEL
CEL
COl
CEL
CEl
CEL
CEl
CEL
CEl
CEl
m
CEL
CEl
CEL
COL
CEL
CEL
CEl
f 11
fit
fit
COl
COL
COL
COL
CEl
CEL
CEl
CCL
COL
CEL
Cll
CEl
CEl
CEl
CEL
CEL
ALGAL
UNI IS
S 1C PER HI
| I
1
3.11 *3»
1
1
5Z.7I 7006
|
16.21 219*
I
1 1
1
1
1
1 I
1 1
0.21 23
1 I
1
1
2.»l 237
1
1.51 193
I
3.41 <••
1 I
0.21 23
6.31 83$
1 X
1 X
1
11.21 14»7
}.»! 08
1 1
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1 X
O.*l *•
0.31 46
|
0.21 23
O.»l 71
1.01 13S
1 X
1 X
1
1
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1
1
1
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1
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1 X
1
1
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2.41 124
|
1
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•
AlCAl
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S 1C Ptfc HI
-- -
H20.il 494
1 1
2I1S.9I 38)
1.1
1.1
1.1
9.1
3.4
1.1
11.4
21.6
8.0
1.1
1.4
1.1
X
X
27
27
X
27
X
220
X
82
27
27S
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192
X
X
27
82
X
27
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UNI IS
S 1C PER ftL
*»_—
1.9
30.8
26.9
7.7
17.3
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43
681
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170
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I
383
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2 S3
X
X
X
X
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X
13Z86 2414 ZZ13
34
-------
LAKt NAME: RATHBUN
STORET HUMBE&: 1909
NYGAAfiD TROPHIC STATE INDICES
PATE 0* 19 74 07 03 74 J<» ?«, 7*.
MYXOPHYCEAN 1.00 E 01/0 E 0.00 E
CHLQRUPHYCEAN 6.CO E 04/0 E 9.00 I
EUGIENOPHTU 0.06 C 0.60 E 0.53 E
DIATOM C.6C fc 1.67 E 1.CO E
COMPOUND 16.0 E 13/0 E 2«.0 E
PALMER'S ORGANIC POLLUTION INDICES
DATE 0* 19 74 07 03 7* 09 24 74
GENUS
SPECIES
03
03
01
00
09
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE
AVERACE DIVERSITY
NUflfitR OF TAkA
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY MAXH
*INUMUM DIVERSITY NINH
TOTAL DIVERSITY
TOTAL NUMBER iif 1NO 1 V IOUA Li/ML
EVENESS COMPONENT
RELATIVE EVENESS
MEAN NUHbER OF INDIVIDUAlS/TAXA
NUMBER/ML UF MOST ABUNDANT TAXON
04 19 74 07 03 74 09 24 74
H
s
M
XH
NH
D
N
J
RJ
L
K
0.63
27.00
6.30
4.75
0.01
213C6.60
33820. 00
0.13
0.14
125J.59
30 8 98. UC
3.47
21. CO
6.00
4.39
0.22
3612.27
1041.00
C.79
0.78
49.57
190.00
3.39
45.00
6.00
5.49
C.21
9061.81
2679.00
O.b2
0.61
59.53
816.02
35
-------
IARE NAHE: BAIHDUh
SlbRtl NUHBIR: 1VU9
07 03 7*
0V Z* 7*
ACHNAN1MES T
ACT1NASIRUH
FALCAIUS
ASIERIiJNCLlA FORMOSA
CARIEtlA
CHROOMONAS ? NORDSIEDlll
ClUSTERIUH
COEIAS1RUH CAHBRICUn
V. INfERHEOlUN
CRTPICHONAS
CRTPICHUNAS SPP.
CTAMOPMirAN FIIAHENI
CTANQPHTIAN FILAMENT (1
CYANOFHTIAN FUANtNl 12
CTClOliLLA niNEGHlNlANA
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IUCIENA IR1PUR1S
FIACEUAIE il
FlA6tLLAlE 12
FLA6EILATE «3
FRAtllARIA T
tTBXOOIHIUn 1 ONOINAIUH
KIKCHNIRUILA
LIPCC1HC1IS
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(IEIOS1RA 01SIANS
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MELOSIRA VAMANS
nERlSROPtOI* TENUISS1HA
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V. IE1RAOOOH
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PENKAIE DIATOn (I
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PENNAIE 01*101 (3
PIR101N1UH
PER10IMIUH QUADS I DIMS
PHACUS
PHACUS CAUOATOS
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RAPHIDIOCSIS
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SCENIC! SliUS
SCtNlOESHUS blCAUDAlUS
SCENEOISHUS B1JUGA
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SCHRUEDIRIA SCTIa
33«9*
X
192
287
nr.AL
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2
*
5
1
3
•
13.6
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4.S
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1*2
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1 X
6.81 71
13.61 1«2
9.1
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6.6
2.3
95
71
190
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I
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X
X
>
71
2*
41641
UN11S
S XC PER HI
2
3
1
»
1
1
1 X
1
|
1 X
1 X
1 X
1.91 SO
|
9.31 2*S
1
0.91 2S
3.91 25
|
1
1
2.81 7*
1
1 X
I
1
5.61 149
1 I
15.71 421
1 X
1
1.91 50
0.91 25
0.91 25
1
1
1 X
1 X
30.51 818
1
1.91 SO
1.91 50
|
1 X
1
1
1
1
|
1 X
1
1
1
0.91 25
1 X
1 X
1 X
1
1
4.61 124
1 X
1
1 X
1
1 X
1 X
1
7.41 198
1 X
1 X
1
1 X
1 X
1 X
1.91 50
2.81 74
1
|
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1 X
1 X
131 7.41 198
33820
1041
2679
36
-------
LAKl SANE : RED RL.CK
STGREI NUMBER: 1910
NYGAARC TROPHIC STATE iNOlCtS
L'ATt C4 16 74 07 08 74 09 24 74
MYXOPMYCEAN 2.0C E 07/0 fc 3.00 €
CHLOROPHYCEAN 5.00 E 14/0 E 7.00 E
EUf.lEHQPHYTE 0.57 E 0.24 E 0. 10 ?
DIAIOn 0.50 E 0.83 E 1.50 E
COMPOUND l4
0.03
20884.70
13474.00
0.33
C.33
538. 96
9795.00
4. 10
42.00
5.00
5.39
0.14
16014.60
3906.00
0.7o
0.76
93.00
454.00
2.59
25.00
3.00
4. 04
0.05
16143. S7
6233.00
0.5b
0.56
249.32
321 3.00
37
-------
I AM runt: BCD RUCK
SIO»E» HUH81RI 1910
TAIA
AC11NASUUH
ACIlftASrhUR HANIZSCHII
ANA8AEMA
AN* IS'RUOtSnuS T
APHAHUJHtkON FLOS-AQUAE
APHANGCAPSA
MIMOOtSHUS
ASIEBIONtllA FORHOSA
CALONflS AHPXlSBAtNA
CtMltIC 01 A IOH
CHLORGPHTIAN COCC010 CELLED COiONT
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». IMItMEDtim
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u? Ob 7*
7*
COUClOtlUA TCTRAPEblA
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*. JAVAHICA
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TPtAl
FORK
CE1
CEL
FH
CEl
f U
COi
CEl
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cot
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COL
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9.il 363
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1
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1
1
1
1
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7.01 273
1.21 »S
3.51 136
1
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1
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3. SI 136
4.71 U2
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4.71 182
1 I
I
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4.31 227
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|
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2.31 91
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AlGAl
UNI IS
S tC PER HI
1.0
SI. 3
3.1
1.0
1.0
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7.2
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193
13474
3906
6233
38
-------
LAKE NAME: RUCK CREEK
STORET NUMBER: 1911
KYGAAkD TROPHIC STATE i
('ATE C'4 IP 74 07 03 7<, 09
7«.
MYXCFHYCEAN 0.50 E 0/03 0 2.50 E
CHLOROPHYCEAN 1.1.0 E 0/03 0 2. 50 E
EUGLENOPHYfE 0.67 E 12/0 E 0.30 E
DIATOM 0.43 E 0.75 E 0.67 E
COMPOUND 4.00 E 5. GO t 7.50 E
PALMER'S ORGANIC POLLUTION INDICES
CATS C4 19 7
-------
LAKE .iA«t: RUCK CkfE*
SlUki I MunaCK: 1411
UXA
ANAbAlNA (1
ANAbAENA 12
APHANizoiiENbH FICIS-AOUAE
ASTERIUNEllA ftlKNOSA
CENTRIC DIAlbft
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CLUSTER1UM M
CLSJSTERIUN 12
CIOSIERI1W 13
CLOSTER1UH §4
COElASIRIM CANtKICbft
COHTlNCtO
19 7»
C,7 03 7*
0"
7*
CRUCIGiHiA QUADRA I A
CRIPItiflOHAS EROS A
CRTPTONUNAS OVATA
CRTPTOIIbNAS REFLEIA
CTCIOTELLA
CTHATOPIEURA SOIL*
CTH8ELIA
OlNOBRTON SdCKit
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».
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28.
3*.J
2...
2.;.
4.0
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22.9
413
X
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62.0
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9.9
1.4
X
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2759
313
X
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1.41 63
18C90 1»»7 »*»*
40
-------
LAKt NArtf: SIIVIR
STCftcT NUM61R: 1912
NYGAARO TROPHIC STATE INC'ICtS
UAU 07 C3 7* 09 33 7
-------
LAKE. NAMES SILVER
191?
CONTINUEU
(.7 j3 7*
•'-•9 23 7*
TAXA
AC II MAS 1 RUfl
AMA8AINOPS1S CIRCULAR IS
ANK1SIROOESFIUS FALCAlUS
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tPIIHEftlA
EUClENA
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CIENOOINIUH bTNNODlNIJN
bOLENKINU
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V. IKRECULARIS
lAtiKMEllllA
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3.91 773
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1.61 1332
1.41 11J9
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1.81 1149
1
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3.11 97
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2.01 li>4;
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2.11 1738
0.91 773
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1 X
|
1 X
1 X
1 X
0. 1 1 97
2.61 2125
1 X
O.tl 676
1
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0.71 579
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1.21 966
S.4I 4441
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1
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1
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4.81 13192
0.01 1274
1
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1
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1
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826 7«
2UU9
42
-------
LAKE NAME: SPIRIT
STORE! NUM3ER: 1913
MYGAARD TROPHIC STATE INDICES
0*TE 'J4 23 74 J7 09 74 09 23 74
nYAUPHYCEAN Cl/0 E 06/0 E 9.00 E
CHlORUPHYCtAN 01/0 E 04/C E 3.00 E
EUGIENOPHYTE 0/02 ? 0/10 ? O.C8 ?
DIATOM 0.12 ? 0.33 E 0.50 E
COMPOUND 03/0 E 12/0 E 14.0 E
PAIHER'S ORGANIC POLLUTION INDICES
DATE 0* 23 7* 07 09 7<, 09 23 74
GENUS
SPECIES
01
00
01
GC
07
30
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE
AVERAGE DIVERSITY
NUMBEk CF TAXA
NUMBER (if SAMPLES COMPOSITED
MAXIMUM DIVERSITY MAXH
MINUMUM DIVERSITY MINN
TOTAL DIVfkilTT
TOTAL NUMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
RELATIVE EVENESS
MEAN NUMBER OF 1NDIVIDUALS/TAXA
UUMbER/ML OF MUST ABUNDANT TAXON
23 74 07 09 7«. 09 23 T,
H
s
H
XH
NH
D
N
J
RJ
L
K
2.40
17.00
3.00
4.09
0.13
3666.40
1536.00
C.59
0.58
90.35
672.00
2.36
20.00
3.00
4.32
0.06
6855.80
2905.00
J.55
0.54
145.25
1569.5»
2.98
19.00
3.00
4.25
0. 06
11055.80
3710.00
0. 70
0.70
195.26
1182.00
43
-------
I AH **HE< SPIR1I
siontr NunaEi" 1913
FAIA
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LAKE Ht.nl : VIKING
STORET NUMBER:
NYGAAKD TROPHIC STATE INDICES
OftTE 0«i 17 74 07 C2 7*. C«» 25 74
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLCNOPHYTE
OUTOtl
COMPOUND
01/0 E
01/0 E
0/02 ?
0/01 ?
02/0 t
5.00 E
3.00 E
0.12 ?
1.03 E
10.0 E
1.25 E
0.50 ?
0.1* ?
1.00 t
2.25 E
PALMER'S ORGANIC POLLUTION INDICES
DATE 0* 17 7* 07 02 74 09 25 7*
GENUS
SPECIES
00
00
05
CO
02
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY
H1NUNUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER UF INDIVIDUALS/ML
EVENESS COMPONENT
RELATIVE -6VEHESS
HE AN NUMBER OF INDIV1DUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXQN
17 7* 07 02 74 09 25
H
s
M
MAXH
H1NH
D
N
J
RJ
L
K
0.56
7.00
1.00
2.81
0.00
30812.68
55023.00
O.iG
C.2C
7860.43
49981.00
2.47
16. wO
1.00
4.00
0.05
9862.71
3993.00
0.62
0.62
249.56
1719.00
2.22
17. JO
1.00
4. 09
0.05
9446.10
4255.00
0.54
C.54
2SC.29
1684.00
45
-------
lAKt H*nt: VIKlNt
SI'J*ET nurHJK : 1914
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46
-------
LAKE NAIL: MIST LAKE QKOBOJ1
STURET
NYGAARi; TftUPHIC STATE iNOICtS
IUTE 0*. ii' 74 07 09 7s 00 23 74
MYXOPHYCIAN
CHLLJPOPHYCE AN
tUGLENGPHYTE
OIAIGrt
COMPOUND
01/0 I
0/0 0
i.oo e
0.37 E
05/0 E
06/o e
06/0 E
0/13 ?
1.00 fc
IS/0 E
IC.O E
7.00 E
0/17 ?
0.57 E
21 .0 E
PALMER'S ORGANIC POLLUTION INDICES
DATE 0
-------
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30 3b 1897 8t>!>
48
------- |