United States
Environmental Protection
Agency
Environmental Monitoring
and Support Laboratory
P.O Box 15027
Las Vegas NV89114
EPA-600/3-78-101
December 1978
Research and Development
Ecological
Research Series
Distribution of
Phytoplankton in
Arkansas Lakes
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RESEARCH REPORTING SERIES
Research reports of the Office of Research and Development, U.S. Environmental
Protection Agency, have been grouped into nine series. These nine broad categories
were established to facilitate further development and application of environmental
technology. Elimination of traditional grouping was consciously planned to foster
technology transfer and a maximim interface in related fields. Th nine sereies are:
1. Environmental Health Effects Research
2. Environmental Protection Technology
3. Ecological Research
4. Environmental Monitoring
5. Socioeconomic Environmental Studies
6 Scientific and Technical Assessment Reports (STAR)
7. Interagency Energy—Environment Research and Development
8. "Special" Reports
9 Miscellaneous Reports
This report has been assigned to the ECOLOGICAL RESEARCH series This series
describes research on the effects of pollution on humans,plant and animal species, and
materials. Problems are assessed for their long-and short-term influences Investiga-
tions include formations, transport, and pathway studies to determine the fate of
pollutants and their effects This work provided the technical basis for setting standards
to minimize undesirable changes in living organisms in the aquatic, terrestrial, and
atmospheric environments.
This document is available to the public through the National Technical Information
Service, Springfield, Virginia 22161
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EPA-600/3-78-101
December 1978
DISTRIBUTION OF PHYTOPLANKTON IN ARKANSAS LAKES
by
J. W. Hilgert*, F. A. Morris*, M. K. Morris*, W. D. Taylor
L. R. Williams, S. C. Hern, and V. W. Lambou
Monitoring Operations Division
Environmental Monitoring and Support Laboratory
Las Vegas, Nevada 89114
*Department of Biological Sciences
The University of Nevada, Las Vegas
Las Vegas, Nevada 89154
ENVIRONMENTAL MONITORING AND SUPPORT LABORATORY
OFFICE OF RESEARCH AND DEVELOPMENT
U.S. ENVIRONMENTAL PROTECTION AGENCY
LAS VEGAS, NEVADA 89114
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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.
n
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FOREWORD
Protection of the environment requires effective regulatory actions
which are based on sound technical and scientific information. This
information must include the quantitative description and linking of
pollutant sources, transport mechanisms, interactions, and resulting effects
on man and his environment. Because of the complexities involved, assessment
of specific pollutants in the environment requires a total systems approach
which transcends the media of air, water, and land. The Environmental
Monitoring and Support Laboratory-Las Vegas contributes to the formation and
enhancement of a sound monitoring data base for exposure assessment through
programs designed to:
• develop and optimize systems and strategies for monitoring
pollutants and their impact on the environment
• demonstrate new monitoring systems and technologies by
applying them to fulfill special monitoring needs of the
Agency's operating programs
This report presents the species and abundance of phytoplankton in the
16 lakes sampled by the National Eutrophication Survey in the State of
Arkansas, along with results from the calculation of several commonly used
biological indices of water quality and community structure. These data can
be used to biologically characterize the study lakes, and as baseline data
for future investigations. This report was written for use by Federal,
State, and local governmental agencies concerned with water quality analysis,
monitoring, and/or regulation. Private industry and individuals similarly
involved with the biological aspects of water quality will find the document
useful. For further information contact the Water and Land Quality Branch,
Monitoring Operations Division.
e ^. Morgan^
Director
Environmental Monitoring and Support Laboratory
Las Vegas
111
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CONTENTS
Page
Foreword "Mi
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
Palmer'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 Arkansas 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
16 lakes sampled in the State of Arkansas (Table 1). The Nygaard's Trophic
State (Nygaard ".949), Palmer's Organic Pollution (Palmer 1969), and species
diversity and abundance indices are also included.
TABLE 1. LAKES SAMPLED IN THE STATE OF ARKANSAS
STORET
LAKE NAME
COUNTY
0501
0502
0503
0504
0505
0506
0507
0508
0509
0510
0511
Beaver Lake
Blackfish Lake
Blue Mountain Lake
Bull Shoals Lake
Lake Catherine
Lake Chicot
DeGray Lake
Lake Erling
Grand Lake
Lake Hamilton
Millwood Lake
Benton, Carroll, Washington
Crittenden, St. Francis
Logan, Yell
Baxter, Boone, Marion
(Taney, Ozark in MO)
Garland, Hot Spring
Chicot
Clark, Hot Spring
Lafayette
Chicot
Garland
Hempstead, Howard, Little River,
Sevier
(Continued)
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TABLE 1. LAKES SAMPLED IN THE STATE OF ARKANSAS (Continued)
STORET
LAKE NAME
COUNTY
0512
0513
0514
0515
0516
Nimrod Lake
Norfolk Lake
Lake Ouachita
Table Rock Lake
Greer's Ferry Lake
Perry, Yell
Baxter, Fulton (Ozark in MO)
Garland, Montgomery
Boone, Carroll (Barry, Taney in MO)
Van Buren, Cleburne
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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 limited 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 1imnologist (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. One
composite sample was put into storage and the other was used for the
examination.
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 superconcentate 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, Naviculattl). 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 intercompsrisons
regularly on 7 percent of the species identifications and counts. Although
an individual had primary responsibility ^or analyzing a sample, tnxonomic
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 ?.5 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
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TABLE 2. NYGAARD'S TROPHIC STATE INDICES ADAPTED FROM HUTCHINSON (1967)
Index
Calculation
01 igotrophic 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
Melosira
Micractinium
Navicula
Nitzschia
Oscillatoria
Pandorina
Phacus
Phormidium
Scenedesmus
Stigeoclonium
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 vuljjaris
Cyclotella meneghiniana
Euglena gracilis
Euglena viridis
Gomphonema parvul urn
Melosira varians
Navicula cryptocephala
Nitzschia acicularis
Nitzschia palea
Oscillatoria chlorina
Oscillatoria limosa
Oscillatoria princeps
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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forms to 6 for 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 = -Y?. log
x
1=1
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-1)
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:
D1 _ H-MinH
KJ -
MaxH-MinH
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
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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 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 entrophy of a
sequence of independent random variables, pp. 333-336. In: Theory of
Probability and Its Applications (translation of "Teoriya Veroyatnosel 1
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. Uilliam 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 Eutroph1cat1on 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 ARKANSAS.
12
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Aohnanth.es lanaeolata
Acln.nantln.es lanoeolata
v. dubia
Aohnanthes miorooephala
Aotinastrum gracilimum
Aotinastrum hantzschii
v. fluviatile
Anabaena planctonioa
Andbaenopsis sp.
Andbaenopsis oiroularis
Andbaenopsis e lenkinii
Anabaenopsis raaiborskii ?
Ankistrodesmus falaatus
Ankistrodesmus falaatus
V. asioularis
Ankistrodesmus falcatus
v. mirabi Us
Aphanizomenon flos-aquae
Aphanooapsa sp.
Aphanotheoe sp.
Arthrodesmus minor ?
Asterionella formosa
At theya sp.
Binuolearia sp.
Caloneis lewisii
Capaptogramma cruaieula
Carter-ia klebsii
Centritractus sp.
Ceratium hirundinella
Ceratium hirundinella
f. braehyceras
Cevatium hirundinella
f. fureoides
Ceratium hirundinella
f. Tobustum
Chlamydomonas globusa
Chlorogoniwn sp.
Chvooaoccus dispersus
Chrooeoeous 1i.rmeti.ous
Chroomonas aouta
Closteriopsis sp.
Closterium sp.
Cooconeis sp.
Coelastrum sambriaim
V. intermedium
Coelastrum micvoporum
Coelastrum proboseideum
Coelastrum retiaulatum
Coelastrum retiaulatum
V. polyahordon
Coelastrum sphaerioum
Coelosphaerium naegelianum
Cosmarium clepsydra
V. nanwn
Cruoigenia apioulata
Cruaigenia cruaifera
Cvugigenia fenestrata
Crugigenia quadrata
Crucigenia tetrapedia
Crucigenia trunaata
Cryptomonas erosa
Cryptomonas marssonii
Cryptomonas reflexa
Cyolotella aomta
Cualotella meneghiniana
CMolotella miahiganiana
Cyalotella stelligera
Cymatopleura elliptiaa
Cymatopleura solea
Cymbella minuta
Cymbella tumidula
Cymbella ventriaosa
Dactylocoaaopsis irregularis
Diatoma tenue
v. elongatum
Diatoma vulgare
v. breve
Dictyosphaerium pulahellum
Dinobryon bavaricion
Dinobryon aylindriaum
Dinobryon divergens
Dinobryon sooiale
Elakatothrix gelatinosa
Entomoneis ornata
Euastrum dentiaulatum
Eudorina elegans
Euglena aaus
Euglena graailis
Euglena limnophila
V. lermermannii ?
Euglena oxyuris
v. minor
Euglena tripteris
Eunotia peotinalis
v. minor f. impressa
Eunotia peotinalis
v. ventriaosa
Fragilaria orotonensis
Franaeia ovalis ?
Glenodinium gymnodinium
Glenodinium gymnodinium
v. bisautelliforme
Glenodinium kulczynskii
Glenodinium ooulatum
13
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Glenodinium penardiforme
Glenodinium quadridens
Gloeooystis sp.
Golenkinia radiata
V. brevispina
Gomphonema graoile
Gomphonema parvulum
Gomphonema truncation
v. aapitatum
Gonatozygon montaenium
Gonium peatorale
Gymnodinium albulwn
Gymnodinium ordinatum
Gyrosigma sp.
Hantzschia sp.
Kirahneriella aontorta
Lagerheimia ailiata
Lagevheimia quadi-iseta
Lagerheimia subsalsa
Lepoainclis sp.
Lyngbya birgei
Lyngbya contorta
Lyngbya hieronymusii
Lyngbya limnetiea
Mallomonas acaroides
Matlomonas pseudocoronata
Melosira di-stans
Melosira granulata
Melosira granulata
v. angustissima
Melosira granulata
v. angustissima f. spiralis
Melosira italiaa
Melosira varians
Merismopedia glauoa
Merismopedia minima
Merismopedia punatata
Merismopedia tenuissima
Mesostigma viridis
Miaractinium pusillum
Miorooystis aeruginosa
Miaroaystis incerta
Mougeotia sp.
Navicula oapitata
Navioula ouspidata
Navioula salinarum
v. intermedia
Navicula viridula
v. linearis
Nephroaytium sp.
Nitzschia aaicularis
Nitzschia holsatiea
Nitzsehia vermioularis
Ooaystis sp.
Ophiooytium oapitatum
Oseillatoria laaustris
Osaillatoria limnetiea
Pandorina morum
Pediastrum biradiatum
Pediastrum biradiatum
V. longecornutum
Pediastrum boryanum
Pediastrum duplex
Pediastrum duplex
v. reticulatum
Pediastrum simplex
Pediastrum simplex
v. duodenarium
Pediastrum tetras
v. tetraodon
Peridinium inconspieum
Peridinium munusculum
Peridinium quadridens
Peridinium umbonatum
Peridinium willei
Phaaus aouminatus
Phaaus oaudatus
Phaaus ahloroplastes
Phacus longiaauda
Phaaus megalopsis
Phaaus pleuroneates ?
Phaaus pseudonordstedtii
Phacus tortus
Phaaus triqueter
Phormidium muaioola
Pinnularia mesolepta
Ptevomonas aauleata
Pteromonas angulosa
Pteromonas aordiformis
Quadrigula sp.
Raphidiopsis aurvata
Rhizosolenia sp.
Rhoiaosphenia curvata
Scenedesmus abundans
Saenedesmus aouminatus
Saenedesmus arauatus
v. platydisca
Saenedesmus armatus
v. ?
Scenedesmus biaaudatus
Scenedesmus bijuga
Saenedesmus brevispina
14
-------
Soenedesmus denticulatus
Soenedesmus dimorphus
Scenedesmus intermedius
Saenedesmus intermedius
v. biaaudatus
Soenedesmus ovalternus
V. graevenitsii
Soenedesmus protuberans
Saenedesmus quadricauda
Soenedesmus quadricauda
v. quadrispina f. spinosus
Sahroederia setigeva
Saytonema sp.
Setenastnm minutum
Skeletonema potamos
Spermatozoopsis sp.
Staurastrum cuspidatum
Staurastnun tetvaaenm
Stephanodisous astraea
V. minutula
Stephanodisaus niagavae
Stipitoaooous sp.
Suri,vel1a angusta
Sux*ipella tenera
Synedva aous
Synedra capitata
Synedi>a delieatissima
Synedpa delicatissima
v. angustissima
Synedra rumpens
Synedra ulna
SyrniTa uvella
Tabellaria fenestrata
Tetvaedron aaudatim
Te traedron cauda turn
v. longispinwn
Tetraedron oons trie turn
Tetraedvon graoile
Tetvaedron li,rmeticwn
Tetraedron minimum
Tetraedron minimum
V. sorobioutatum
Tetraedron muticum
Tetraedr-on regulare
Tetraedron trigonum
Tetraedron trigonwn
v. gvaoile
Tetpastrum elegans
Tetrastvum hetevacanthum
Tetrastrum staurogeniaeforme
Traehelomonas bulla
Trachelomonas fluviatilis
Trachelomonas gibberosa
Tvaahelomonas hispida
Trachelomonas intermedia
Traahelomonas lacustris
Trachelomonas longicauda
Trachelomonas saabra
Traahelomonas soabra
v. oordata
Trachelomonas scabra
V. longioollis
Trachelomonas schauinslandii
Trachelomonas volvoaina
Treubaria setigenm
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! BEAVER IAKE
0501
NYGAA30 TROPHIC STATE
DATE 04 0^ 74 08 30 74 10 09
MVX1PHYCEAN
CHLQRQPHYCEAN
EUGLENOPHYTc
DIATOM
COMPOUND
02/1 F
0?/0 f
0.55 f
O.fn F
un E
1.50 F
6.50 c
0.30 F
0.50 F
14.5 P
5.H <=
7.00 c
0.67 F
1.40 c
27.0 c
01
02
10
00
04 OS 74 OR 30 74 10 0 74
01
00
SPc;iES TTVE'SITY AND ARUNOANC? !N"ICC(:
OF
AVERAGE DIVERSITY
NUMBE" OF TAXA
SAMPLFS CnMPOS!TEf>
DIVERSITY
OAT?
M
S
M
04
7<> 08 30 ^4 10 09 74
TOTAL ntVFR ST TV
TOTAL NUMPER PF 1 NOIV 1 OU Al
MEAN NUMBER HF INOI V IOU ALS/T AX A
NUMBER /ML OF MOST ABUNDANT TAXON
2.91
27.00
6. 01
51 .00
3.'0
39.00
XH
NM
n
M
I
RJ
L
K
4.5'
0.16
48P8. * )
1680.00
0.64
0. 64
73.04
475. 10
5.67
0 .22
9886.50
?9?S.OO
0.60
0.58
57.3*
549.00
5.?9
O.e7
??35. ' "»
771.00
0.50
0.54
1H.4P
1 "".00
17
-------
LAKE NAME : BEAVFS IAKF.
CONTINUcr>
ACHNANTHFS
ANA8ACN*
»NK 1 STRODE SMUS
V. /CMCULAOIS
ASTER I ONE LLA
CFNTPfc DIATOM
CFPATtUM HI»UNOINELIA
F. RPACHYCFRAS
CHL AMYIIMONAS
CHI 0«rI
V. lONr.ECOP-NHT'JH
PFQIASTPUM SIMPLEX
V. OOHDENAPIUM
PEOIASTP.UM TETOAS
V. TFTQJOOON
PfNNATE DIATOM
PFP.ID1NIUM INCCN5PICUUW
OOAn°,IOFNS
SCENEOE?«US DENT 1C1IL ATUS
SCFNEnESMUS INTFBMtDIUS
5CFNEnES»US OUAOP |f»LIOA
1f.Hl»OfOERU SETIGE«»
STAUPASTKUH
STFPMANnOlSCUS
STFPH/INOOISCOS fl
STEPHANODISCUS ASTDAEA
V. MINIJTULA
SY«(6P»A fl
SYNEOPA •?
SYNPDPA »J
SYNF.ORA ULNA
SYNU"A
TFTBAF[\PO«< CONSTRKTUM
TETPAFORON MINIMUM
V. Sril"BICULATUN
TBACHFIOHONAS
TRACHELQMONAS BJLLA
TPACHFLOMONAS BULLA ?
HISPIBA
TPACH"=lOMONAS SCHAIIINSI AUDI I
TBEUBA»IA SFTIG^RUM
TCTAL
00 M
CEL
FIL
ML
CFL
CEL
CEL
CFl
CEL
CEL
CFL
CFL
COL
COL
COL
CEL
CFL
CFl
CEl
CEL
CEL
C FI
CEL
CEL
CEL
CFL
CFL
CFl
CFl
CFl
C CL
ML
CFl
CEL
CEL
CEL
CFl
CFL
ML
rEL
CFL
CEl
p II
F II
cm
cm
cm
COL
CEL
C CL
CEL
CFL
CFL
COL
COL
COL
COL
CH.
CFL
CEl
CFl
CFl
CEL
CEL
CFL
CEl
CCL
c FL
CFl
CFL
c FL
CFL
CEL
cei
CEL
C?L
•-LGAL
IN!'1;
•>.
t
•>
<.
1
CEL |
1.9
22.6
28.1
5.7
1.9
1 .0
7.6
9 .*
7.6
l.o
11 .3
X
310
475
x
9?
V
X
12
127
15S
12T
X
X
12
X
X
*
190
X
X
X
X
AlCU
UNIT-;
S * C o cq M{
2
4
1
1
3
4.?l 12?
'.'. 1 61
1.0
11.5
1.0
4. ?
6 . 1
!«.»
».i
11.5
1.0
1.0
6.1
18. (<
4.?
10
X
X
X
115
X
X
X
X
X
1?'
X
X
U'
X
X
X
X
X
X
54Q
X
244
X
X
X
315
X
X
X
X
X
X
X
X
10
X
X
10
X
X
113
549
X
12?
X
X
X
if T<
l
4
•>
e
1
'3.3
4.7
9.6
4. T
!4.1
9.6
4.7
» 4. 1
4 . •>
Q.6
X
!7?
X
14
69
'
X
X
' 01
to
X
X
14
X
X
X
X
X
X
X
X
X
V
\0i
X
X
14
X
X
60
X
X
X
x 1
1
18
1640
-------
L AK E NfcMEt 81ACKFISH
STORFT NUMBER: 0502
MYX1PHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTc
NYGAAPO TROPHIC STATE
03 26 74 06 04 74 10 16
01/0 E
0/0 0
5.03 F
O.U f
07/o F
02/0 F
02/0 F
2.00 P
^.S") «=
13/0 P
r»3/o F
05/0 f
1.25 F
•».T«; c
?\/Q F
PALMER'S ORGANIC POLLUTION
04TC 03 2S 7* 06 04 74 10 16
38
00
19
00
02
SPPCIFS OIVF'StTY AND A61IN04NCE
TOTAL NUMBER
&VFRAGE DtVFR$ITY H
TAXA S
COMPOSITPD M
DIVERSITY MAXH
DIVERSITY MINH
n
N
J
"J
TOTAL
INOIV I DUALS/ML
'OMPONFNT
MEAN NUMREP OF !N01 V Inij ALS/ T 4X A
NUMBER /ML OP MOST ARUNOiNT TAX ON
03 2S 74 06 04 ft. \n 16 74
7.76
f.OO
3.00
4. 19
0.^4
1344.12
4fl7. 00
0.67
116.30
f.OO
3 .00
0.16
2650.flO
112".00
0.57
T.56
66.3S
475.00
3A.OO
0.
47351,
115?'..
0.
1,
0*
31.
00
70
ft 1
1767.00
19
-------
BLACKFISH
MJ«I6F1>: 050'
CONT 1NUF1
F^H
CHlA«YOOMnNAS TEL
C ML AM YO^mtjAS GinROSA CFl
CHP1OWO*iAS 4CUTA rFL
1 'JFLCUPHAFBlim NiECELMNUM Cat
CBVPTTMONA5 rFL
COYPTPMONAS EROS* CFL
rpyprpMONAS PfcLFXA CF^
CYCLOTFLL* «FNf GHI'I I4NA rFl
OAC TVL rXOCCHPSIS CFL
FJGLFNB 11 rpL
"IJ^iLFNt *2 C^t.
EUGLCNA (3 (;F(_
El) GLEN A ** r"EL
FUGLENA #5 C*L
FUGIENA ACUS rfL
FiJGLENA SPP. CFl
FUGLENOPHf TAN CFLL CFL
pL*nFn.4TF *? rFL
FUG£LL«TF ««. jFl
FL»r,FLiATE »5 rri_
GO^PH^fJ rei
Cror-SIG"* CEL
K|OCHN=BJ£LLA CFL
L FPOC I NCL IS CEL
LYMGBYA COMTORT* c R
MFLOStPAOISTANS CEL
••FKISJP* GOANUI ATA CFL
Hfirs[°A GRANUL1T*
V. *NG US T [ SST f*A CCL
MEff (SLOPED It HINIH* COL
^FSOSTlG*** VIRtllS Cft
NAVTfULA TEL
I'.VICUV* 11 CFL
MIViriJL* «> CEL
M'VICUt» CltSPIOAT* CEL
NTTZSrHTA r*L
.,|Tj;'M[A »? CCL
NiiyscHii nii.SA7ici rr\_
S4IT7CrMlA SPB CFL
PHACUS CFGALQPSIS CFL
'H4CUS T«IOUFTFP CFL
OhriPKID'JH F II
PTrarjMONAS ANGULOS* r Ft-
OTco0MONAS CO'DIFOPMIS CFL
^rp^enfKMu5 ABUNDANS COL
SCFNFieS»US BIJIJG* COL
sr CMEnES"US OUAO«IC*UO* COL
5«FLFTONE«I* POTAMOS CCL
SPE R»A TOZ OOP SI 5 CEL
TfTpacTOU* FLFC.ANS CCL
rcTOASTOU" HETFRACANTHKH Ct>L
rpeCH'Ln'ONAS riSBFROSl CEL
T 0 4rHFLO"ONAS MISP'tl* CFL
T=«CMFLO"ON4S HISPID*
V. ? CFL
TOACHELPtONAS INTfPMEDT* CFL
T»eCMELCH5NAS LONGK»ur* CFL
T"4CHcl 1XONAS VILVnCIHA CFL
IN f<
•: »c OFO *L
i
4
1
7
5
I'M
14.4
?5. H
4.7
1°. 1
9.4
4.7
4.7
11
X
70
X
116
X
? 3
X
X
X
X
X
93
4ft
21
21
X
• J N f T e I r I r T c
S *C OFB "L t< tC P" "•.
1
S
3
1
42. 1
5.?
?1 .1
^,2
^.?
47S
X
5 =
t
X
?!8
f3
X
V
X
*
sq
X
X
4110.11 119
1 X
1 ?l ' ^. *! I to
! 1
11 ' 1 .Tt 1 -<4».
?
I.
1
s
1 .4( 4 '
|
1
]?.»l 14"
0.71 "4
1 « 1 7 l n
•ijs I *"> 1
•i'sl n,
T ,1 | 1 T^>
1 '
t
n.7| «4
1
1
6.M "i7
ojsil 45
1 *
1 x
J.M '04
«.M ^^^
1
1.1) 1 ? f
"l
1
1
0.4| 47
1 . M ' ? *-
l.l| '711.
1
1
1
1
l-i.'l >•">-'
1
t
1. 4 | 13
1 *
1
1 . f 1 'in
'.M "4
1
1 . s 1 i * «
•).4| 4'
f>. ? 1 Tl *
1 X
1.71 »t
0. 4| 4">
1
1
|
1
2.11 "ft
1
l.\! '?*.
497
20
-------
tAKF. NAME: BLUF MOUNTAIN LAKE
STC3FT NUMBER: D5D1
-JT,
MYXOPHYCFAN
CrlLOROPHYCFA^
Dl ATOM
COMPOUND
STATF
0?/0
1 .50
1 .00
\2/0
0.26 c
POLLUT11N
DATP 33 2* 74 36 36 74 13 Ifl 74
00 \ 4
SPEC IP<;
SPECIES OIi/FPSHY AND ABUNOANCC
TATF 33 23 74 06 ~>6 74 13 IS 74
AVERAGE DIVERSITY
NUMBER IF TAXA
NUMBER OF SAMPLED COMPOSITED
HAX1MUM niVERSITY
MINUMUM OIVEPSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
CVFNESS COMPONENT
MFAN NUMBFB OF t NO ! VI DUAL S/ TA XA
H
S
MAXH
Mt MH
n
N
J
"J
L
NOMBFR/ML
MOST ABUNDANT TAXON
IS. 33
2. 00
4.17
3. IS
1168*.50
4853.00
-». 58
0.5R
269.44
. 00
0
17
2
4
1
2217
4031
.55
.00
.35
.05
.00
237.1?
3742.00
45.33
?. 00
3.16
3661.00
0.50
1'. .36
90S. 00
21
-------
LAKF NAME: RID* MOUNTAIN LAKF CONTTNi]
STO»ET KUMRFP: 050'
TAXA FORM
ANA8ACMA F IL
ANM STPOOESMUS CH
ANK I S TOHDE SMUS FALCATUS CFL
ASTER1 iNELLA FORMOSA CFL
CALONf IS LFHl SI I CFL
CARTFPIA CFL
CE°»TIUM HlauNniNELLA CFL
CFPATIIJM HIPUN1INFLLA
f. B»ACHYCERAS CFL
CFOATJUM. HIOUNOI NFL LA
F. FIJRCOIDES CFL
C ML AMYOHMONAS CFt
CHROOMPNAS ACUTA CFL
C L^STFP TUM C FL
COFLASTCUM M1C»OPOPUM CCL
CRUCK.ENIA APICULATA COL
C«tlClr,FNt A 'ETCAPEDIA COL
C R YP TOMPNA S CFL
C°YPTO«ONAS ERCSA CEL
CO YPTPMCINAS MAOSSONII CFL
DACTYlprncc/lPSI S CFL
r)ACTYLOCOCCOPS IS I" RERUL AR IS CFL
cue TYCISPHAFBI UM PULCHFLLUM COL
DTNOBRVON PAVABICUM CEL
ril'.LENA •! CEL
FUGLFNA •? CFL
FUC,LrNft 9* CFL
FL4GFLLATE ^FL
GYMNOniNIUM ALBIXU" CFL
I FPOCINCL IS CFL
MAILOMONAS ACAPdlOFS rcl
MFLOSIO* OISTINS CFL
"FI.OSIPA G'ANULATA CFL
V. ANCUSTISSIMA CEl
MICPdCYSTJS AEPOG1HOSA COL
NAVICIJLA C*L
NAVICULA CAP! TATA CFL
NITZSCHIA II CEL
TPH10CYTHJM CAP1TATUM r FL
TSCILIATOHIA FIL
PANDORINA MQRIJM COL
V. LONGECORNUT'JN COL
PECIASTBUM DUPLEX
V. RFTICULATLIM COL
PFDIASTRUM TETRAS
V. TETBAOOON COL
PCNNATF DIATOM »1 CEL
P^NNATf DIATOM «2 CEl
DMACU^ CFL
PHACUS MEGALOPSIS CFL
PHiCUS TCIOTI;S CEL
PIN^ULARIA MFSOLEPTA CFL
PTFPTCnNAS ANGULOSA CFL
sctNEnESMus ABUSOA^S COL
SCf NEOES-US BICAUnATUS COL
SCFN^DFSMiJS DENT1CULATUS COL
SCFNEOESMUS DI»ORPH(IS COL
SCENE^ESMuS INTFpMFOIUS COL
SCFNFOESMus PROTUBERANT COL
SCENE^ESMUS OUADRICAJQA COt
ST'PHANOOI SCUS ASTPAFA
V. "IN'ITOLA C^l
SYNEB°» CFl
SY«(FO"A «1 CEl
SYNFO»» ULNA CFL
TABELL»»IA FENEST»AT» CEL
TFTPAFO»Cm TRIEONU" CFL
^FTRASTRUM HFTER ACANTHUS r HL
TRACHELOMONAS C FL
TRACHELOMONAS l\ CFL
TP4CHFLOMONAS FLUVIA^UIS CFL
TPACHFLOMONAS VOLVOCIN* CEL
1
c
4
->
T,
*>
'
TC
1. 4
2?.0
•i.l
'. f-.l
b.8
40.7
?.5
0.1
2.*
) < ? R 74
M GUI
•INI TS
-> co ^L
X
1(>4
I3f><*
?47
7fll
X
X
X
X
129
l°7J
1?3
X
41
1?1
X
X
s
?
5
}
4
1
rc
T. 7
0.7
0.7
1.4
2.1
•»?.*
1 .4
T> 16 7(.
M r,-M
1 1 M T C
n C q Ml
?o
X
X
70
7 Q
X
SP
X
lifc
374?
18
X
X
X
«
X
X
S
4
S
7
1
1
Tr
°. 1
! .1
? . »
? .1
4 .«-
2? .7
?7.>
1 .1
4.5
1.1
1.1
'1 .*
1.1
15 >q 14
f 1 ^. • |
U*i ! T r
prr "i
y
y
X
x
X
-» 11
i.?
X
V
9 1
X
« "»
' fc^
V
X
X
r
oqft
X
X
X
t*7
X
' hf.
X
X
X
X
X
X
X
X
u->
y
u ~>
X
X
-•on
X
X
y
X
t?
TOT'.L
22
-------
LAKE NAMES BULL SHOALS LAKH
STORET NUMBER:
NYGAA^D TROPHIC STATP INDICES
DAT? 04 05 74 06 20 74 09 05 74 10 15
MYXOPHYCEAN
CHLQOOPHYCEAN
EUGLENOPHYTE
DIATOM
COMPOUND
04/9 E
04/3 E
1.12 ?
0.67 E
17/0 E
4.00 F
5.00 E
0/18 ?
0/03 ?
9.00 E
2.33 E
0.67 ?
0/09 ?
0.50 E
3.31 P
06/0 <"
05/0 r
0/1! ?
1.50 <=
1'*/0 c
PALMER'S ORGANIC POLLUTION INDICES
OAT? 34 36 74 06 20 74 D9 35 74 13 15 74
GENUS
SPECIES
08
00
01
00
00
SPCCIES DIVERSITY AND ABUNDANCE
OATE 34 36 74 06 20 T<» r>q }5 74 1 ~) 1.5
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES COMPOS ITEO
MAXIMUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF I NO! VI DUALS/ML
CVENESS COMPONENT
RELATIVE FVENESS
MEAN NUMBER Of INOIVIOUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TUXON
H
S
M
MAXH
MI NH
n
N
J
RJ
L
3.03
36. 33
"i.OO
5.17
3.23
6641.76
219?. 00
3.59
0.57
60. *)9
2.26
31 .00
8.00
4.9*
T.22
3812.62
16B7 .00
1.46
n.44
54.4?
2.2°
22.33
R.OP
4.46
3.4fr
1076.30
470.00
T.51
0.46
21 .36
?."M
? \ .">"»
R.OO
4. 1Q
3.25
2471 . 5?
91 2. OO
0.6?
0.60
41.41
620.00
927.00
1 81.00
23
-------
LAKF NAME: BULL SHOALS LAKE
STOfFT NUMPFI>: 050*
06 ?0 7*
IVCHN&STHES LANCeOLATA
V. OUBH
AN4B»CNA
4NKISTRODESMUS FALCATUS
4<>HAN!ZOMENON FLOS-AQUHE
APHINICAPSA
APHANOTHECE
ASTFRIPNELLA FORMOSA
CFNTPIC OIJTQH
CERAT!U» HIRUNOINELIA
CE°ATlu« MIRUNOINELLA
f. B°»CHYCE.RAS
CFRATTUN HIRUNOINELLA
F. FUPCOIOES
CH°oncoccus LIMNETICUS
CHRnrjMQNAS ACUTA
CinSTCR IUM «1
CLOST^PIUM tl
COELA5TPUM RFTICULATUM
V. PHLYCHOROON
CnSLASTRU* SPHAFR1CUM
CCnOSPHAERIUM NAEGELIANUM
cnSMiRIUM
COS»AP[U« CLEPSYDRA
V. NAMUM
CPYPTOMONAS ER1SA
roYPTOMriNAS MAPSSOM!
COYPTOMONAS SPP.
r YI-LOTFLLA
r YMATTPLEUBA SOLEA
01 ATOM* TENUE
V. FLONGATUX
OIATOMA VULOARf
V. BREVf
OICTYnSPHAFRIUH PUICHELLUH
OINORBYON niVE'CENS
OINOBRYON SOCIALE
FRAGHARIA
tUAGILARIA CROTONENSIS
GLENOOINIU" KUlCZYNSKII
GYMNOIINtUM
LAGEPHFIMIA C 1 1 I A TA
L «GEOHF!«I» SUBSAL^A
LYNG8YA HIERONYMUSII
L YNG^Y* LIHNETICA
HALLCMONAS
"6LOSIRA G»ANUtATA
"FLOSIOA GRANUtATA
V. ANGUSTISS1MA
HAL ICA
VARIANS
MICOOCYSTIS AERUGINOSA
HOUGFOTIA
NAVICULA SALINARUM
V. INTERMfOIA
NITZSCHIA VERMICULARIS
OOf YSTIS
1SCILLATORIA II
"SC ILLATORIA »2
flSCItLATOOIA IIUHEMC*
OANOCRINA HORUM
"FOIASTRUI4 HORYANUH
PEOIASTOUM SIMPLEX
V. DUOOENARIUM
V.
PENMATE DIATOM
Pf RIOI NIUM
PFR IPINIUM 12
PfRIOIMUK QUADKIOENS
"TR ID! NIUM MI LL5I
PMSCUS PSEUDONOROSTeOTII
3UAORIGULA
SCfNE"E SMUS
SCENEOESMUS 6IJUGA
SCCNEOESMUS OUA5HICAUDA
SrAUOASTRUM
FORH
TEL
•ML
CFL
FIL
COL
COL
rEL
CFL
CFL
CFL
CEL
COL
CEL
CEL
CEL
COL
COL
COL
CEL
CEL
CEL
CEL
CFL
CFL
CEL
CFl
CFL
CDL
ca
CEL
CEL
CFL
CFL
CEL
CFL
CEL
<=!l
FIL
CEL
CEL
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CEL
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COL
CFL
CFL
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<=Il
FIL
FIL
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COL
COL
COL
CEL
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cm.
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cot
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INI 'S
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u
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17.1
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7.5
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175
285
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X
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165
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60
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620
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212
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24
-------
LAKE NAME! BULL SHOALS LAKE
NUMBER I
TJX*
STEPHSNOOISCUS ASTRAEA
V. MINUTULA
STEPHV(r)D!SCUS NIAGARAF
SYNEO°» I!
SYSED°» r>FlICATtSSI*«
Tf TiMEnaON
TPT04EOKON
V.
TOT4L
CQNTINUFO
Of, T,
Ofc JO 14
1 5LC»l
1 'INITS
FOR* IS ttC OFR "L
1 1 1
cn \ I fc.il 13*
CEl UllO.ZI ZZS
CEL 1 1 O.TI 15
CFL IS) 8.9) 195
CEt 1 1 1
1 1 1
CFL 1 1 1
1
1
IS
«c
4LG»L
UNfS
PFR •(.
X
X
1
1
IS
«r
ALr.Ai
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y
X
1
1
(«
Tr
' 1.1
/vLr.Ai
IJiilT?
ore MI
X
X
Oi
2192
25
-------
LAKE NAME: LAKE CATHERINE
NUMBERS
NYGAARD TROPHIC STATE INDITES
DAT<= 73 2f> 74 06 05 74 11 15 74
MYXOPHYCEAN
CHLQRQPHYCF.AN
EUGLENOPHYTc
DIATOM
COMPOUND
01/0 E
06/"> F
0/Cf ?
0.8? E
12/J E
03/0 F
)8/0 «=
0.1P ?
0.57 F
17/0 E
2.00 F
9.51 P
0.14 ?
0.33 F
13.5 F
PALMER'S ORGANIC POLLUTIDN
OATF 03 ?S 74 16 05 74 U 15 74
GENUS
SPECIES
11
03
03
08
04
SPECIES DIVERSITY AND SBUNOANCF INtMCE*
OATF
AVERAGE DIVERSITY
NUMBER IF TAXA
NUMBER OF S«MPLES COMPOSITED
MAXIMUM DIVFRSITY
MINUMUM DIVERSITY
TOTAL OIVERSITY
TOTAL MUMRE« OF INOIVIPUALS/Ml
FVF.NESS COMPONENT
RELATIVF 6VENFSS
MEAN NUMBER OF INDIVIDUALS/TAXA
NUMBEK/ML 0* HOST ABUNDANT TAXON
13 26 T4 36 75 74 10 15 74
H
<;
M
MAXH
MINH
n
N
1
RJ
L
\
3.01
?5. 11
4.00
4.64
0. 05
19131.56
«>356. 10
0. 65
0.65
254.24
211ft. 00
1 .69
33.01
4.00
5.04
0.09
8745.75
517S .TO
0.?4
0.33
156.82
3685.00
3.57
46.00
4.00
5.52
0.2?
9121.35
25 55. 01
0.65
0.64
55.54
487.00
26
-------
LAKE NAME: LAKE CATHERINE
STQRfT NUMBER : 0505
TAXA
ANKISTROOESMUS
ANKISTPHOESMUS FALCATUS
ANK ISTRODFSMUS FALCATUS
V. MIPABUIS
ASTER IONELLA FORMOSA
CENTR 1C OIATOH
CENTRITRACTUS
CHLAXYDOM9NAS
CHLORHPHYTAN F1LAHENT
CHROOWONAS ACOTA
CO?l»STRU* RETICULATUM
C»UCtGEN!A
CPUCICESIA TETPAPE01A
CONTINUFI
13 26 T4
16 15
EROSA
PEFLEXA
CYCLOTELLA
CACTYLOCOCCOPSIS
OICTYnSPHAERIUM PULCHELLUH
OIUCBRYON SOCIALE
EUGLENA
EUGIF.NA *1
FLAGELLATE
FLAGELLATE »z
FLAGELLATES
FRAGUAP.IA CPOTQNENSIS
GPLENKINIA
GCMPHONEMA
GONIUM PECTORALF
K IRCmERIELLA
MALLPMCNAS
MELOSIRA OIST4NS
••FLOSIRA GPANULATA
OELOS1RA GRANULATA
V. ANGUSTISSI^A
KESOSTIGMA VIRIOIS
NAVICULA
NITZSCHIA II
NITZSCH1A 12
OOCYSTIS
OSCILl
DSC ILLATORIA It
PASCCPINA MQRU"
PEDIAST9UH BIRAOIATUM
OCD I45TPU" TETRAS
V. TETRAOOON
PENNATE OI4TOH *1
PfSNATE OI4TOMS
PCPIOINIUM INCONSPICUU*1
PHACUS
RHQtCnSPHENtA CURV4TA
SCENEOESMU5
SCfNEOF SHUS ABUNOANS
SCENEOES*US BICAUOATUS
SCeNfOES«US OENTICULATUS
SCFNFOFSCUS OIMORPMUS
SCENEDESHUS OUAORICAUOA
SKELETONEKA POTAMOS
S">ER»»ATOIOOPSIS
JTAUR'STRUH
SUPIREILA
SYNEO»A ACOS
SYMEOPA RUHPfNS
TABFL14PIA FFNESTBAT*
TFTRAFO»ON CAUDATO"
V. LONGISPINUH
TETPAEORON MINIMUM
TfTRA?0»ON MINIMUM
V. SCROBICULATIJH
TF.TRASTRUX HE TEP ACANTHUM
TFTPASTP1JM STAUROGENIA'-FORME
TPACMCLOMONAS
SETIGERUM
TOTAL
FORM
CEL
CEL
CEL
CEL
CFL
CEL
CEL
Fit
CEL
COL
COL
COL
CFL
CEt
CEL
CEL
CEL
COL
CEL
CEl
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
COL
CFL
Cfl
CR
CEL
ca
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CEL
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CEL
CEL
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FIL
FIL
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COL
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COL
CEL
CEl
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UNI TS
5 TC "1 ML
1
&
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?
5
|
1.21 77
1
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6.7
1.2
7.9
,
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0.6
33.3
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2.4
5.5
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0.6
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1.2
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42*
X
77
X
-
501
X
.
462
X
39 •
2118
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X
154
X
347
X
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X
77
39'
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2
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3
1
2.21 113
3.5
4.4
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1.7
7.2
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0.4
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0.9
7S.1
X
191
X
X
226
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116
73
X
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90
X
X
113
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158
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4
1
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'..2
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2.4
4.4
4. R
2.4
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3.6
19.1
1.2
1.2
5.9
14. '
I .2
X
X
X
6!
15?
X
'I?
31
X
X
X
X
6!
y
»
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X
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9!
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407
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33
V
15
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X
X
X
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r
X
6356
5175
27
-------
LAKF NAME: LAKE CHICOT
STCRET NUMBER: 0506
NYGA43D TROPHIC STATE INOIfFS
DATE 33 26 74 06 35 74 It If, ^4
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTc
01 ATOM
COMPOUNO
04/3 E
09 /) E
0.46 F
1 .03 F
23/0 E
5 .00 F
3.33 F
1.00 f
1.50 F
19.0 F
05/0
3«/3
0.46
1.40
?6/0
PALMER'S ORGANIC POLLUTION
OAT? 03 26 74 06 05 74 10 16 74
GENUS
SPECIES
01
33
IB
03
Of
00
AVERAGE DIVERSITY
NUMBED n»= TAXA
NUMBER OF SAMPLES COMPOS ITFO
MAXIMUM DIVERSITY MAXH
MINUMUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INOIVIOUALS/ML
FVFNFSS COMPONENT
RELATIV^ EVENESS
MEAN NUMBER OF INDIVIDUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
DIVERSITY AND ABUNDANCE INDICES
03 ?6 74 06 05 74 10 16
3.OP
31.00
5.25
H
s
M
XH
NM
0
N
J
RJ
L
•<
1 .6fi
29.00
3.00
4. 86
o. n
4799.76
2B57. 3)
0.35
0.33
98. 52
1904.00
3.56
30.00
3.00
4.91
0.13
10502 .00
2953.33
0.""
O.T2
98.33
566.00
6743.33
0. 50
0.59
22B1.00
28
-------
LAKE NlKft LA.M CHICOT
STOBET NUMSEPJ
COMT INUFO
S MICRQCEPHAIA
ACTINAST9UM GP-ACILIMUM
ANA6AFNOPSIS CIRCULAH1S
ANA8AFNOPSIS EI^HKINII
ANKISTBODESMUS FALTATUS
ANKISTPODESMUS FALCATUS
V. AC ICULAR1S
8INUCLFARIA
CnonOMONAS
CHRCOMONAS ACUTA
CLOSTERIUM
COFLASTRUM MICPOPOPUM
CRUCtGFNIA APICUIAT*
C«IK IGFNIA TETBAPEPIA
CHYPTOONAS EROS*
CRYPIOHONAS HARSSONII
CYASOPHYTAN FtMKEMT
CYCLOTELLA
D1CTYLOCOCC3PSI5
fUGtFNS (1
FUGLFNA 12
EUGLE'iA f3
fUGLENA 14
»cus
EUGIEN* IINNOPHRA
V. LFMHESH1NHII T
EUGLENt OXYJRIS
V. «1NO«
FUGIFNA SPP.
tUCEll ATE »2
GLFNOOIN1UH OCULATIX
LFPOCtNCLIS
LUNATE CELL
"tFLOS IRA OISTANS
ME LOS!" A GRANUUTA
XELnSIR* GPANULATA
V. ANGU5TISSIMA F. SPIR
«?LCMRA VAUI *NS
H5RISHOPED1A TFNUISSIMA
"FSnSTIGMA V1RIPIS
"ICROCYSTl S 1NCEBTA
NITZSCHIA «
NIT7SCHIA f?
NITZSCHIA ACICUt.AP.IS
OSCILIATORIA
OSCILLATOR1A »1
PEOIASTPUN DUPLEX
V. RE'KULATUW
PEHNATE DIATOM
"EH 1DINIUM
PERIDTNIUM JM8TINATUM
PHACUS
PM1CUS ACUMINATUS
PH4CUS "fCALDPSIS
PTFPOMONAS ACUIEATJ
"APHIOIOPSIS T
PAPHlniOPSIS CUR VAT A
sreNeiFsnus
SCENEOESHUS OIHOUPMUS
SCENEOFSMUS P«OTUBF»ANS
SCHROEOFftlA SfTIGFPA
SKELPTONFH* POTAX05
S'FPM»NODISl.US
STEPHAN001 SCUS 4STPAEA
». HIN'JTULA
II
SYNEORA
SYNEOPA
SYHTBPA
TSTR«rt>»ON CAUOATU"
V. L(1NG!5P!NU«
TETRAFORON MINIMUM
RON MUTICUM
FORM
C€L
CEL
Fit
FIL
f TL
CEL
CEL
ML
COL
CEL
CFL
CEl
COL
Cdt
r.rn.
CEL
CEL
FIL
CEL
CFA
CFL
CEL
CFl
CEL
CEL
CEL
CEL
CFL
CFL
CFl
CFL
CEL
CEl
CEl
CFL
Cfl
CFL
ca
CEL
CEl
COL
CEl
COl
CEl
CFl
CEL
FIL
FIL
COL
CEL
CFl
CEL
CFL
CEL
CFL
CEl
FIL
ML
cni
COL
COL
CFl
CFl
CFl
CEL
CFl
CEL
CEL
ca
CEl
CEL
CEL
MG»L
UNI TS
s tc =FR ML
&
i
s
?
I
1
5.*l 15*
1.1
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3.2
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12. <»
l.l
6 (-.6
X
X
n
X
X
X
2*6
9?
X
X
31
568
X
X
M
X
X
X
X
X
X
!<)>
X
X
X
»l GAl
IIXI TS
S 1C "ER ML
1
1
*
2
5
».o
?.->
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1.0
l*.l
1.0
6.1
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«-.3
z.o
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6.1
T.l
Ill
61
X
1<>
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*n
30
1 '9
89
I
X
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11"
I |0
60
K
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X
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60
1T9
X
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X
X
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«
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4.6
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X
' 04
? -Jftl
IS
X
^s
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f
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X
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•"•
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X
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X
1<
29
-------
LAKE NAME I LAKE CHI COT
STQPET NUMBER: 0506
TAX*
TfTRAEOION TP.IGONU"
rET»»ST«>U» STAU*OGEN|AEFOP.i«
TPACHELONONAS
TBACMEIOKONAS SCABBA
TRACHFIOHONAS SCABS*
V. C1HDATB
CONTINUE"
01 26 T4
06 OS 74
10 '.
PORN
CEL
COL
CEL
ca
CEL
1
«
ALGAL
PE« ML
X
X
X
s
tC ff'O "I
1
3.31 89
1 X
1
1 X
•!
V.
prD ui
X
X
X
285T
C-741
30
-------
LAKE NAME: DE GRAY LAKE
STORFT NUMBER: 0507
MYXQPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTC
DIATOM
COMPOUND
NYGAARD TROPHIC STATE INDICES
03 25 74 06 05 74 10 16 74
03/0 F
05/0 E
0.1? ?
0.31 ?
12/0 E
3.75 E
1.00 F
0.14 ?
0.80 E
3.00 E
2 .5") P
4.50 P
0.07 ?
").43 F
8.50 r
PALMER'S ORGANIC POLLUTION INDICES
OATF 03 ?5 74 06 05 74 10 16 74
GENUS
SPECIES
06
03
06
00
11
04
SPCCIES DIVERSITY AND ABUNDANCE INDICES
03 21 74 06 05 74 10 16 ^4
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMRER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY MAXH
^INUMUM DIVERSITY MINH
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
FVENESS COMPONENT
RELATIVE FVENESS
MEAN NUMBER OF INDIVIOUALS/TAX A
NUMBER/ML OF MOST ABUNDANT TAXON
H
S
*
XH
NH
0
kl
,J
RJ
I
K
3.57
26.00
6.00
4.71
0.19
5808. 39
1677.00
n. 76
0.75
62.59
2R7.00
1 .87
28.00
5 .00
4.R1
0.04
17196 .52
9196.00
0.?9
0.39
328.43
6083 .00
4.14
33.00
6.00
5.04.
0. 20
8176.50
19'5.00
O.P?
0 ,«2
59. «5
?l4.oo
31
-------
LAKE NAMfi !}E GRAY LAKE
$TC>>ET NUMBER: 0507
Taxi
ACHNANTHES LANCEOLATA
ANMSTROOeSMUS F4LCATUS
ANKISTPOOESMUS <=ALCATUS
V. HIRAfllLtS
APHANIZOMENON FLOS-AQUAE
ASTERIONELLA FORMOSA
CENTRITRACTUS
CEBATIUH HIRUMHNFLIA
CERATIUM HIRUNDINELLA
<=. FUPCOIDES
CHLAMYOCXONAS
CMPCONONAS ACUTA
CIOSTERIUN il
CLCSTFR1UN »2
COCCONEIS
COELASTRUM MICROPORUN
CRuctGENtA TETBAPEOIA
C'YPTCIMQNAS
CBYPTCMONAS EROSA
CPYPTHHONAS REFLEXA
01 NOSH YON R»VABIC IH
ELAKATOTHRIX GELATINOSA
EUGIENA GRACILI S
FLAGELLATE »2
FRAGIIAPIA CROTONENSIS
FRANCEIA
GOLENKINIA
GOIENKI 1! A RAD! ATA
V. BBFVISPINA
GO»PHONEMA TRUNCATUM
V. CAPITATUM
GYMNOnlNIUH ALBUIU"
GTMNOOINIUH OROINATUM
KIRCHNERIELLA CONTORTA
LAGERHEIMIA OUAORISETA
LYNGBVA •
"SLLOMON4S
MELOSIPA
HELOSIRA OISTANS
M^LCSIBA GP-ANUIATA
MELOSTRA GPANULATA
V. AUGUSTISSIWA
ME'ISHOPEOIA MINIMA
H1CRACTINIUM
HtCRHCYSTIS INCERTA
"OUGEPTIA
NAV1CULA fl
NAV1CULA *2
N1TISCH1A
NIT/SCHU «l
NlTISCHIA 12
NITZSCHIA ACICULAR1S
OSCILLATOR IA
PEBlnlNIUM 1NCONSPICUU*
PAPHIOIOPS1S CURVAT4
SCENEOESMUS BIJUGA
SCENEDESMUS OUAQPICAUO*
SCHPOEDERIA SET|GE°A
SFLENASTRUM MINUTUF
SKtrLETONE^A POTAMOS
ST8UHASTRUX
STAURASTRUN II
STAUBASTRUM CUSPID* TUM
STAURASTRUH TETRACFRUM
SYNEOOA ACUS
SYNEORA ULNA
TA8ELLABIA FENESTRATA
TETRAEORON HUTICUH
TPACHELOMONAS HISPIDA
TBACHELOMONAS LACUSTRIS
TREUBARIA SETIGERUM
TOTAL
CQNT1NUFO
0' 25 74
06 OS
10 '6
FORM
CEl
CEL
CEL
FIL
CEL
CEL
CEL
CEl
CEL
CEL
CEL
CEL
CEL
COL
COL
CEL
CEL
CEL
CEL
CEL
CF.I
CEL
CF.L
CEL
CEL
CFL
CEL
CFL
CEl
CEL
CFL
FIL
CEL
CEL
CEL
CEt
CEL
COL
COL
COL
CEL
CEL
ca
CEL
CEL
CEl
CEL
FIL
CEL
FIl
COL
COL
CEL
CEL
CEL
CEl
CEL
CEL
CEl
CEL
ca
CEL
CEl
CEL
CEl
CEL
Mf.u
WITS
S K PER ML
1 I x
2117.6) 29T
s
4
1
1
2.0
9.8
5.9
13.7
3.9
2.0
3.9
5.9
11.7
-
2.0
3.9
2.0
5.9
9.8
32
159
X
X
96
223
6*
X
32
64
X
96
1,91
X
X
12
64
32
X
Of.
X
X
159
X
aiGil
UNI TS
S *C o?R »L
3
S
*
2
.
1
3.*
0.6
6.9
3.1
0.9
9.6
12.2
0..9
0.6
0.3
3.4
0.3
0.3
66.1
X
317
SB
X
X
i36
X
X
X
299
X
86
X
X
5« .
X
1 11 24
86
58'
2«>
X
X
317
29
X
X
29
6>m
Al. 1", SI
IN! T<
s rr P" «".
1
3111. Dl ?14
5
I
u
2
1
1
!
1
1 x
1
1
1
*.OI 119
10.11 ?'. 4
1
1
1
1
1
IS. 01 !19
1
1
1 x
1
1
H.ftl 71
1
1
I
I
t X
1
1
1
1
1 X
1.71 2'
4.81 9S
I X
1
l.M V
1
1
'1.61 71
2.4| 68
1
4.81 «<
U.5! !*•>
1
1
!
T.2I I4»
1 X
4.91 9S
1 x
2.41 48
7.71 '.41
1
1.21 ?4
3.61 71
1 X
1
1
1 X
1
1 X
1 X
1
4.81 9«
1.21 ?4
1.71 '4
I
1 x
162T 9196 *?!•>
32
-------
LAKE NAME: LAK? ERLING
STORET NUMBER: 0508
NYGAA^O TROPHIC STATE INDICES
DATE 03 25 7* 06 03 74 10 17 74
MYXOPHYCEAN
CHLOROPHYCEAN
FUGLENOPHYT*
DIATOM
COMPOUND
2.00 E
5.03 E
3.43 E
0.6T E
12.3 E
2.50 E
1.50 F
0.37 E
1.50 F
7.00 E
1.00 F
4.50 F
3.36 E
0.83 F
10. 0 F
PALMFR'S ORGANIC POLLUTinN
OATF 03 25 74 06 03 74 10 1
GENUS
SPECIES
07
03
01
00
' 74
01
00
SPECIES DIVERSITY AND ABUNDANCE
OATC 03 25 74 06 03 74 10 17 74
SVERAGE DIVERSITY
NUMBER OF TAX A
NUMB?R OF SAMPLES CQMPOSITFO
MAXIMUM DIVERSITY MAXH
HINUMU* DIVERSITY
TOTAL DIVFRSITY
TOTAL NUMBER CF INDIVIDUALS/ML
>=VENCSS COMPONENT
RELATIVE EVENFSS
MEAN NUMBER OF INC IVIOUALS/TAXA
NUMBER/ML (IF MOST ABUNDANT TAXON
H
S
VI
XH
NH
0
«J
J
PJ
L
K
2.10
23.00
3.33
4.52
0.10
637Q.50
28*55.00
0.46
0.46
125.87
1715.30
2.05
24 .00
3.33
4.58
0 .23
2394.43
1168.00
0.45
0.4?
48.67
491 .30
?.?0
^4.00
3.33
5.00
0.21
4353.80
1979.00
0.43
0.41
58.21
1134.33
33
-------
L5»E NAME: LAKE ERI 1 NO
STr;»ET NUMBER: )10B
CONT1KUCT
TAX* PQGM
V, fLUVIlfU E CEl
AI^5B*! C TYDSPHAER I UM PULCHELLUW COL
01N05BYOM BAVARICUM CEL
OtNCBRYON OIVS'GEN? CFA.
OINHflflYON SOCHLE CEL
EUOrolN* ELEGANS Cm
fir.LFNl CEL
fUGlFMA ACUS CFL
FUNQTtA C€L
CUNOTH PECTINALIS
V. VrWTRlCI?SA CEL
GLENOOINIUN OCULATIM CEL
K 1 PCMNE P I ELLA CEL
LE»OC(NCHS CFL
«ELD5!"« OISTANS CFL
**ELOSFP1 GRANUIBTA CEl
MCLOSIPA GRANLHATA
I/. AUGUSTISSI** CEl
HELC51RS GRANULATA
V. *1GUSUSSI«A F. -SPIHALIS CEt
HICBOCY^TIS AEPUGINOSA COL
M!CBDTY
TOACMeLOMONAS rNTEBMFOIA CEl (
taACM^LOHPNAS VTLVnCtN' CEL 1
1.8
*.*
0. 9
% 9
9.T
0.9
?.!
il. t
13,3
t .*
0."»
o.t
51
ua
?6
It
?6
?9?
x
^6
15*
X
X
X
i m
3fl*
X
]T
s 1
?*
X
X
2ft
II
X
a i r, A t
S tC D<=0 "I
2
1
3
t
4
18.*
2.T
28.
K
X
11
X
3Jfl
X
X
t
X
X
X
491
X
X
31
IT
X
51
M
<^ tr OCD «i
r
i
?
^
i
s
9.6
3.R
!.=>
I.'
1 .9
13.*
•il. «
'.T
1 .9
X
X
X
X
! 10
T!
X
Tft
1«
X
!•
X
1C
y
7f,T
1 1 0*
y
f
y
11
!•!?
'
X
16
X
X
X
X
X
X
X
X
X
1,
-------
LAKE NAME: GRAND LAKE
STORET NUMBER: 0509
OAT?
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTC
DIATOM
COMPOUND
THOPMIC STATE INDICES
03 ?«> 7* 06 0* 74 10 16 74
2.67
7.67
3.16
0.67
13.3
3.33 E
5.33 E
1.23 E
1.00 f
13.0 f
3.00 F
7.67 F
0.06 ?
1.50 F
13.3 P
PALMER'S ORGANIC POLLUTION
DATF 03 26 74 06 "iU 74 11 16 74
GENUS
SPECIES
24
07
07
13
04
SPECIES OIVCPSITY AND ABUNOftNC*
OATF 03 26 74 06 04 74 10 16 74
AVERAGE DIVERSITY H 4.18 3.28 3.15
NUMBER OF T4XA S 59.00 57.00 50.10
NUMBER DF SAMPLES COMPOSITED M 2.00 2.00 ?.00
VAXIMUM nivERSiTY MAXH 5.8* 5.P3 5.64
MINUMUM DIVERSITY MINH O.04 0.01 0.04
TOTAL niVERSITY 0 96570.54 501157.76 54149.50
TOTAL NUMBER OF INDIVIDUALS/ML N 23103.00 152792.00 17190.00
CVENESS COMPONENT J 0.71 0.56 0.^6
RELATIVE FVF.NF.SS HJ 0.71 0.57 0.56
MEAN NUMBER OF INOIVIOU&LS/TAXA L 391.5ft 2680.56 343.80
NUMBER/ML OP MOST ABUNDANT TAXON K 3813.oo 52408.oo 3523.00
35
-------
Oft 0* ••*
T 1X1 F0»*
M-TlHi^aun GAktmMD* CFt
ANABA'HA FH
ANABAFNA PL4NCTQN1TA R 1 L
1 NABACNOP S [^ CIRCUIABTS FfL
AMKISTPODESMllS FILCJTIJS CFL
ANK ISTHDOESmjS e»LC*TUS
<- ACICUliaM CFL
A *JM STttQOE S^uS FAICATUS
V. HlPietLli CEl
CfNT*TC OCiro^ CEL
r HI SM mcr*iQNA s CFI
r HI nftocnc CAL CAN COICNV •$ COL
<" HiC*OGC't*!UH tH.
CuPDDTJCCOS COL
Cn°OOCOCCU5 D1SPF.&SUS COL
CHPDONONAS «CUTA CH.
Cn5TFPTU« CFl
CTFl»5T*UM CA«BR,ICUN
V. INTFHKEDILM C 3L
COSM1B IJM 11 CEl
T1SK1PIJN n r.Et,
CnSM«ojLP« » CFL
CPUtlGENT* TE'HAPFPIA COL
C^UCIGF^IA TRlJHCATA COL
CPYPTHMONAS E^fJSA CEL
CYASOPHVrAN C^LT^V COt
*• y MATH PLF URA fLLtPrfCA CEl
crmTOPLFjai jDLfA CFL
CVNBELL" lINUfl CFl
ninviococcfipSlRk GRANUlATA
v. ANtusTrssi "» TFL
ftLCSTBA GDANULATA
V. * F. SIMR«LM CfL
MFLOSI"* VAR1ANS CEL
« BlSK^eTClt GV^UCI COL
»cprs*opeo74 TmuMsiMA COL
JNl'S
<; »c °<=R «L
1 1 X
11 3»frt B??
*
5
?
1
f
1 X
1
7**l |T1«»
1
{
1
9. It ?0<»J
1
l.nl ?j*
1
1
1 K
1
1
1
I X
4,
1 X
1 X
1
1 6 1 ) 7*
1
1 X
4 x
7.11 lt*1
1
1
O.H T(
1 X
1
1
1
1
10»7I 3*ST
1 X
,
1
1 X
1
1
1 X
1
1
1
0.11 "
l.lH '?*
l.il Ti.
1
1
1. 1 \ 7*8
1
1.01 ?2*
1
|
I
!.Jl '90
ALCil
S 1C *f« »L
?
1
3
1
1
Q .9 | ] ^iji
7.0 **U
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*.9
u?
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K
X
^
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7?6r
r
n
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V
X
23*7
1
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t
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r
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]t
?AI
X
X
10*20
31 21*
?*l
0,?| 261
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! 1 I
1 Z.*l 16*0
1.11 IJSt!
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S T Pc° "1
(
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X
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X
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1«
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K
"
7(1
1173
X
X
X
? \ 1
7(1
1 *1
X
m ?
1 7*
->tlQ«
36
-------
LAKE MMF: C.R'ND HKE
STORE'
VfPIDIS
KOOCYSTIS
H1TZSCHIA 12
NI TZSCHIA * )
H tr?SCHlA HOlSAMCA
nocvSTis
OSCllLATORTA
nsciLHTORI* 7
V. ?
SIMPLEX
v. T
PEWITS DUTO«
PER I3TMU"
PFR1CIHIU*
PFKI01SIUH
PHif US 4FC»IOPSI S
PH4CUS PSEUOONO«OSTFDT IT
PH4CU5 tnerus
(UPMIOIOPSIS CURVAT*
*BH*TUS
V. t
SCF1EF1ESHUS
SCEKFDESNUS
us
1* SEr ICEP»
II
sr EP
V. Wf NUTUL *
SUP IH^LI*
TENER«
T»BFLL«RI» FENEST»«Tl
TfTRifDOON CINUM
TfTRiFO'OK GP4CHE
CR*CILE 7
TF rOFDODN MUTTCU"
Tf TRAST"UM FLEG'NS
7C1PISTRUK HFTE!**C«NT HUH
TFTPASTRUK 5PP.
TFTO*STOUN ST4UROCFN! A
v. nN
TCTJL
FJON
CEl
cm
CEL
CEL
CEl
CFL
CEL
Ftl
FIL
<= IL
CM
CGL
cnt
COL
CFL
CEl
CFL
C^L
CFL
CEl
rOL
-•ni
cot
cot
CflL
COL
cot
cot
CfL
CEL
CFL
CEt
CEL
CEL
CEL
CEL
CEL
CFL
CEL
CEL
CEL
COL
COL
COL
cot
CEL
1
CfL 1
<. *C
1
7 .
T ,
0 .
4.
2.
0.
0 .*
1. 1
O.f.
1.1
1ft. 5
1.5
3.3
0.3
3.?
M. '. • I
IM'S
X
1 '!•>
B>?
7S
10*7
X
673
75
*
X
*
150
X
X
X
75
150
?9Q
K
X
381?
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X
75
7*
X
X
7*8
X
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5 1C
7.5
1.0
*. *
O . j
o.?
0.7
15.2
S.fc
0.?
1.?
if. «l
nil Tt
\
1 1147?
1 155«.
t
5215
1
X
?M
X
X
X
X
X
Z61
10*1
X
? 3 ? 0*
X
SM*
X
761
?61
X
< Tr
\ °i.?
M 1 ^.
i T.
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n. «*
7.0
t.2
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(1* ' r e
P rr MI
\ le^
>>; i 7
y
*
in *> n
M
X
35
£
TE
i n*,
v
t
K
' 16
K
1*
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t
M
K
l • Q a
X
V
1 s
1<;
X
37
-------
LAKE NAME! LAKE HAMILTON
STnPET NUMBER:
9ATF
MYXOPHYCEAN
CHLOROPHYCEAN
DIATOM
COMPOUND
TPDPHIC STATE INDICT
?7 74 16 0? 74 11 15 74
01/0 F
03/0 F
0/04 ?
0.67 F
10/1 F
9.00 E
10.0 F
0.05 ?
0.50 E
33.0 F
?.oo
6.75
0.09
I .?5
10.7
PALMER'S ORGANIC POLLUTION INPtCFS
DATE 33 27 74 rj6 •)«; 74 j-j 15 74
06
GENUS
SPECIES
OS
TD
12
13
SPFCIES DIVERSITY AND ABUNDANCE IN1IC»=S
DAT? 73 ?7 74 06 05 7* U 15 7A
DIVERSITY
NUMBER OF TAXA
NUMBER PF SAMPLES COMPOSITED
MAXIMUM DIVERSITY MAXH
MINUMUM DIVERSITY MINH
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
FVENFSS COMPONENT
RELATIVE EVENFSS
MEAN NUMBER OF INDIVIDUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
s
t
XH
NH
n
N
J
RJ
L
K
2.41
24. 05
6.00
4.58
0. 07
11199.27
4647.00
0. 53
0.52
193.63
254^.00
3 .58
37.00
6.00
5.21
0.22
7296.04
2038.50
0.69
0.68
55.08
528.00
3.59
62.00
6.00
5.95
0.1 5
20168.62
5618.00
0.60
0.60
90.61
1976.00
38
-------
LAKE NAME: LAKE HAPRTCN
STORET NUMBER: 0510
CONT
13 27
06 05
10 fi
ANABAENA
ANABACNA II
«Z
TRODE SHUS FALCATUS
AMK ISTPOOESMUS-JALCATUS
v. MIPABILIS
ipHtNi/QMENON FLOS-AOUAF.
APHANnTHECF.
ASTEPinNELLA FORMOSA
ATTHEYA
CENTRIC DIATOMS
CEPATIUM HIRUNDINELLA
c. BOACHYCERAS
CHPOCMQNAS ACUTA
CLOSTFPIUM
CHELASTRUK PROBOSCIOEU*
COFLASTRUM RETICULATUM
V. POLYCHOROON
COFLASTRU* SPHA=R1CUM
COSMARIUM ;
CPUCIGENIA AP ICULATA
CRUCIGF.NIA CHUCIFEPA
COUCIGEMIA FENESTR«TA
CP.UCIGENIA TETRAPEOIA
CPUC1GFNIA TRUNCATA
CRYPTOMONAS EROSA
CR.Y«OMONAS MAPSSflNII
CBVPTOHONAS REFLEXA
CYCLOTFLLA STELLIGFRA
CYMBEILA
OAcrnococcoPSis IPREGULARIS
OICTYOSPHAERIUH PULCHfLUUH
DINCBPYON
OINnBPYON CYLINDRirUM
EU»ST»UM OENT ICULATUM
SUGLENA
EIJGLENA ACUS
FQAGILARU CROTONENSIS
GGlfNK IN I A
GGNATOZYGON MONTAEMUM
GY«NOPINIUM OROINATUM
KIOCHNERIELLA
LAGEPHFIMIA SUBSALSA
IYNGBYA
MALLOMONAS
MEL05IRA 01STANS
MELOSIR* CRANULATA
"?LOSIRA GBANULATA
V. ANGUSTISSIMA
HFRISMOPfOIA MINIMA
K6S05TIGMA VI RICH $
M1CROCYSTIS AERUGINOSA
MCUGfOTIA
NAV ICIILA
NIT2SCHIA
NIT;SCHIA il
NITZSCHIA *2
OSCILLATORIA
«";DIA<;TRUM
FORM
FIL
FIL :
FIL
CEL
CFL
FIL
COL
r.fl
CFL
CEL
CEL
CEL
CEL
CEL
COL
COL
fOL
CEL
.COL
COl
COL
COL
COL
CEL
CFL
CEL
CEL
CfL
CEL
CEL
COL
ca
CEL
CF.L
CEL
C6L
CFL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
FIL
CEL
CEL
CFL
CEL
COL
CEL
cm
FIL
CEL
CFL
CEL
CF.L
CEL
«=IL
COL
ALGAL
UNITS
5 1C »ER ML
'.
«•
1
!
1.1
6.3
I.I
5«.T
'
1.1
1.1
5.3
?.l
11.6
6.3
5.3
l.l
'
49
X
293
49
25*3
'
49
•
"
49
245
X
.
X
X
X
98
X
518
?93
X
X
2*5
49
ALGAI
UNI TS
S 1C OCR ML
3
5
2
I
*
5.5| 113
1
3.71 «
3.7
1.9
3.7
1.9
9.3
2K.9
3.7
7.4
14.8
1.0
7.*
X
X
X
X
7?
ie
X
-
75
X
3P
1R9
X
X
SJ8
X
7?
151
302
10
X
151
X
X
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AL'V!
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S tC «" »L
•
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3
*
1 x
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3.5
0.7
0
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3.5
3.5
«
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1 96
. X
X
X
X
»
i.X
X
X
*0
X
.X
X
41*
•
1974
X
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I
X
X
X
X
X
t
X
!5R
X
?37
X
X
.„„
• oq
X
X
19?
I X
1
39
-------
l*KF HUME: LIKE HAMILTON
STO»f» NUNBFR: OMO
Oi 27
TiXA FORK
PFCIASTOLIM BIRAOIATLIN
V. 1 ONGFCOP.NUT"UM CDL
p^niASTmjM IETPHS
V. f^TPAOOON COL
PF» 10 I Nl U* CEL
P5RI01NIUM INCONSPICUU" CFl
°H«CUS CEl
& A<*HI oi OP si s i FIL
R4PHIMOPS IS CUPVATA 7 FIL
»^I7DSnLFNIA CEL
SCCMEriESHUS ABUNOANS COL
SCENEQFSMUS OENT ICUL AfUS COL
SfFNFOFSMLIS OtTlRPMUS cnt
SCf.NEOESHUS INTERKFDIUS COL
SCENECESMUS INTEBHEOIUS
V. BIC4UOATUS COL
SCENEOESHUS OUACWICAUDA COL
5nu»»STBuc «i ca
SYAlJPlST^U** TfTP,ACFflU*< CFL
SttPHANOOISCUS CFL
SYNFDCA fl CFl
SYNEOPA ACUS CFI
SYNFOPA CAPITATA CEL
SYNFDBA OELICATISSIKA CEl
^YNFO»A ULNA CFL
'*TRAfnoo* rfunST**T* CE''
V. LONCISPINLW rFl
TCTRAE DION CONSIR ifTUH ca
'F'RAFDRQN UMNFTKUX CEl
TEtftAFDRON *(IN1^UM CFl
TETRAFORON MINI MUM
V. SCR1BICULATUH CFl
T*T»AFO«0<< TRIGONUM CFL
75TRAEORON TRICONUM
V. CRACH.E CEL
T«TPAST»UM HETERACANTHUH COL
T P ACHel DMONAS CFL
"FUBARIA SETIGSR.LI" CEI
TOTAL
5 tC
3.2
H r.AL
UNITS
OF« H\_
X
1*7
X
X
46*7
S *C
!.•)
1.0
1."
1.1
l.t
OCP ML
18
X
1«
J8
X
X
X
•»«
X
11
X
;m»
s
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0.7
t.\
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9."
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Af.AL
UN ' ' 5
pco u(_
X
„
X
X
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41
X
f SI
'3'
TO
41
(
X
X
41
7Q
Sftl »
40
-------
LAKE NAME: MILLWOOD LAKE
STORET NUMBFR: 0511
MYXOPHYCE AN
CHLOROPHYCEAN
EUGLENOPHYTE
DIATO"
COMPOUND
NYGAARD TROPHIC STATE
)3 2? 74 06 33 7* I) 17 74
03/3 e
36/) E
O/QO ?
0.27 ?
12/0 F.
06/0 E
11/0 E
0.06 ?
0.44 F
22/0 E
? .00 «=
9.0T P
0.30 F
0.67 F
!7.0 c
PALMER'^ ORGANIC POLLUTION INDICES
OATF. 03 2S 74 06 03 74 10 17 74
GENUS
SPECIES
11
13
08
03
01
00
SPECIES DIVERSITY AND ABUNDANCE INIKFS
D«TC 03 25 74 06 03 74 10 17 ^4
4VERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY 1AXH
MINUMUM DIVERSITY MINH
TOTAL DIVERSITY
TOTAL NUMBER HF INDIVIDUALS/ML
FVENFSS COMPONENT
RELATIVE EVENESS
MEAN NUMBER OF INDIVIDUAL S/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
s
M
XH
NH
0
N
J
RJ
L
K
3.33
29.01
^.00
4.86
0. 12
9780.21
2937.03
0.69
0.68
101.28
698.00
3.84
40.00
3.00
1.32
0.08
2760^.76
7189.00
0.72
0.72
179.73
2010.00
2.73
31.00
3.00
4.9*
0.2*
3458.91
1267.33
0.5S
0.53
43.87
438.00
41
-------
LAKE NAVE! MILLWOOD LIKE
NUKBER: 0511
TAXA
ACHNANTHES MICROCEPHAL»
ANABAENA
ANK1STRODESMUS
ANKI STRODE S«US FALCATUS
ANMSTPOOESMUS FALCATUS
V. ACICULARIS
APHANI70MENON FLOS-AOU4E
ASTEPIONELLA fORMOSA
ATIHEYA 7
CAPTEOIA KLEBSIt
CENTRIC DIATOMS
CHRPOMONAS ACUTA
COCCONE.IS
COEIASTP.UN SPHAERICUM
CRUCIGF.N1A -TETRAPEDIA
CRYPTOMONAS
CRYPTOMONAS EROS A
CRYPTOMONAS MARSSONII
CYCLOTELLA
CYCLOTELIA MENFGHIN1ANJ
CVMBELlA
CYMBELLA VENTRICOSA
OACTYLOCOCCOPSIS
OINCBRYON BAVAHICUM
OINCBOVON SOCIALE
FUASTPUM
EUOORINA ELEGANS
EUGLENA TRIPTEPIS
FUNOTTA
F.UNOTIA PECTINALIS
v. MINOR F; IHPRESSA
FLAf.FU.ATE «2
FLAGELLATE •*
FRAGILARIA CHOT OMENS IS
GPLENKINIA
GYMNOntNIUM
KIPCHNERIELL*
KIRCHNERIELLA CONTORT A
I EPOC INCUS
LYNGBYA
HALIOHONAS
MELOSIRA OISTANS
"FtOSIRA GRANULATA
"ELOSIRA GRANULATA
V. ANGUSTISSIMA
NEP I S»tlPED I A MINIMA
HE30STIGHA VIRIOIS
MICRACTINIUM
MICROCYSTI S INCERTA
MCUGEOTIA
NAVICULA
NAVICULA 11
NAVICULA 12
NAVICULA VIRIDULA
V. LINEARIS
NEPHROCYT IUN
NITZSCMIA
NITZSCHU «1
'
CONTINUEO
01 25 T4
06 03 Tfc
10
NITISCHIA It
NIT2SCHIA fA
NITZSCHU ACICULARIS
OSCILLATOR It
PEOIASTOUK DUPLEX
PEDUSTOUM DUPLEX
V. 7
PEDIASTRUM TETRAS
V. Ti?TRAOOON
PERID1NIUM
PERIOINIUM UMBONATUM
PHACUS LONGICAUDA
PTEROMONAS ANGULOSA
SCENEDESMUS ARCUATUS
V. PLATYOISCA
SCENEDESMUS BICAUDATUS
SCENEOF.SMUS DENTICULATUS
SCENEnESMUS DIHORPHUS
SCENEOESMUS OVALTERNUS
V. GRAEVENIT2II
FORM
CEL
ML
CEL
CEl
CEL
FIL
CEL
CEL
CEL
CEL
CEL
CEL
COL
COL
CEl
CEL
COL
CEL
Cft
CEL
CEL
CEL
CEL
CEL
CEL
COL
CEL
cet
C?L
r.EL
CEL
CEL
CEl
CF.L
CEL
CF.L
CEL
' = 11
CEL
CEL
CEL
CEL
COL
CEL
COL
COL
FIL
CEl
CEL
CEL
CEL
CEL
CEL
CEL
Cfl
CEL
CEL
ca
FTl
COL
COL
COL
CEL
CEL
CEL
CEL
COL
COL
COL
COL
COL
M.GAI
UNITS
S *C PER ML
4
2
J
S
.
1
1
1.31 37
1 X
J.5I 73
2.5
T.5
23.8
7.5
2.5
'7.5
23.8
5.0
1.3
5.1
3.7
3.7
.73
220
648
X
220
X
X
X
73
X
220
"
698
X
'
X
X
1*7
37
X
X
1*7
no
110
1.31 37
ALRAI
UMTS
S «C l>ER ML
1 1 X
11 7.51 5*1
3
2
4
5
1
1.61 116
1
1
l.ll 77
1 X
0.51 V>
1
1
1
1
0.51 39
1
1
1.61 116
1 X
1
|
1
1 X
5.<)| 425
7.01 502
1
1
1 X
1
1
I
1
5.91 *?5
0.51 39
2.T| 101
1
1 '
1.61 116
1 X
1.11 77
3.21 232
1
28.01 201J
5.9| 425
5.4| 3«7
2.21 155
4.31 309
I X
5.9| 425
1 X
1 X
1
1
1
1 X
1
?.7| 193
1
1
1
1
1
1
1 X
1
1
1
1
1.6) 116
1
1
1
1
1
0.51 39
1 X
1
1
1
1LT,»L
UN' T^
S rr oco m
1
5
6
3
2
34.6
'S.4
3.9
T.7
3."
15.4
11.5
3.9
3.0
1
1.
<•-!*
1 Of
X
49
X
>
97
X
X
X
X
X
10
X
X
1°5
!4*
• X
X
40
X
X
X
X
49
X
42
-------
LAKE NAME I MI LLWOGP LAKE
STC«fT NUMBER! )511
TAX*
SCHROP0ESJA SETIGEPA
CONTINUED
01 25 7*
06 OJ 74
10 !
SVNEORA ULNA
TABRIARIA FENESTRATA
TFTB4EORON MINIMUM
V. SCPOBICULATUM
TETRAEORON REGULARE
TRifHELOMONAS
TOT At
FORM
riT"
CEl
ca
cei
cet
CEL
CEL
CEL
s *c
1.3
ALGAl
UNITS
•ER ML
37
X
X
S
tc
2.7
ALGAL
UNIT*
PER Ml
\n
X
X
X
X
s
tr.
ALC.AL
I«IT«
»eo m
X
X
X
2937
71S9
1267
43
-------
LAKE NAME: NIMROO LAKE
STORET NUMBFP: 0512
NYGAA^O TROPHIC STATE INDICES
OATF 03 27 ft 06 07 7* 10 18 74
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLFNOPHYTF
DIATOM
COMPOUND
02/0 F
05/3 E
0.5^ E
1.00 F
14/0 E
04/0 E
01/0 E
0.80 F
0.80 F
13/0 E
04/0 f
06/0 *
0/10 7
0.57 F
14/0 ?
PALMER'S ORGANIC POLLUTION INOKCS
DATE 53 27 74 06 57 74 15 18 74
10
GENUS
SPECIES
09
03
01
00
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES COMPOS ITFO
MAXIMUM DIVERSITY
MINUMUM DIVER si TV
TOTAL DIVERSITY
OF I NTM VI DUALS/ ML
CVFNESS COMPONENT
RELATIVE EVENESS
OF INDIVIDUALS/TAX*
MOST ABUNDANT TAXON
TOTAL NUMBER
MEAN NUMBER
NUM8EK/ML OF
SPFCIES DIVERSITY AND ABUNDANCE INDICES
53 27 74 06 07 74 15 19 74
H
S
M
MAXH
MtNH
n
N
J
RJ
L
K
1.93
2f>.00
?.oo
4.70
5.10
6183.72
3204.00
1.41
0.40
123.23
1933.05
3.04
22.00
2.00
4 .46
0.25
2927.5?
96^ .00
5.69
0.67
43.77
394.00
3.12
27.50
2.00
4.75
0.1 0
11232.00
3600.00
0.66
0.65
133.33
1296.00
-------
I AKF NAKE: M«r-no LAKE
STDRFT NUMBER: 051?
CONHNUET
TAXA
SCHNANTMES MICROCEPHAl*
ACT fNASfRUf
ANABAFMA
ANK IJTRCIOESMUS FALCATUS
ASTERI^NELLA FORMOSA
CENT" 1C DIATOMS
CEPAT1UM HIRUNOINELLA
f. FtlRCOfDFS
CHPCOHONAS ACUTA
CnFLASTRUM SPMAEBKU*
CPYPTOMONAS
c«YPT9MjN*s EROS*
C YfLOTFLLA
OACTYinCOCCOPSIS
niCTYOSPHAERIUK PUICHEILUM
EUGIF.NA *l
PUG LENA OXYUKIS
V. HINOR
FL»GHL»TES
CRAGILARIA CROTONENSIS
GLENOCINIUM OCULATUM
HANTZ5CHIA
PCIRCHNERIELLA
IFPOC1NCL1S
HALLC*ON*S
«AUOMON«S PSFUOaCr"ON*
MELOS1BA OISTANS
HELOSIR* GR»NUt*T*
MFLOSIR* 6«A»IUIAT»
V. ANOUSTISSI**
MEKISMOPCOIA GLAUC*
»EP I 5"0IA TENUISSfMl
XF.SOSTIGM* VIH10IS
•MCOACTINIUK POSILLU"
MCHOrYSTIS INCERTA
"OOGFOTM
NAVICUt*
NITZSCHU
NITZSCHfA tl
TETR»S
V. TfTPAODON
PENXATE DIATOM
PE» JOIN 1UM
PHiCUl
PHORH101UM MUCICOIA
PTFBOHONJS
R^UO^OLENIA
5CFNEDESHUS BIC»UO»TUS
5CEXECESWS OENTICUIATIIS
srENtnF sxus PROTUBERANS
SC'NEOESHUS 9U»ORICAUOA
4NGU5IA
SYNEOR* DEL ICATISSIMA
SYN«C«A OCIICATISSIMA
V. ANGUST1SSIMA
SYNURA 1
TABFLL40IA FENFSTRATA
T»ACHfLOMONAS INTERMEDIA
CEl
FIL
C?L
CEl
CFL
CF.L
CEL
C*L
cm.
CFL
CFL
CFL
Fit.
COL
CEL
CEL
CEL
CEU
r?L
CfL
CEL
CFL
CEL
CFL
CEL
CFL
CEL
CEL
COL
COL
CBL
cot
COL
FIL
CFL
cei
CFL
FIL
COL
CFL
CFL
ca
FIL
CCL
CFL
COL
COL
COL
COL
ca
CFL
CEL
CEL
CFL
CFL
1
1
IS
1 1
1 1
1 1
nm
i i
i i
1 1 2
1 1
1 1
1 1
1 1
1 1
17113
1 1
1 1
1 1
1 1
1 1
1 |
1
11 160.
1 t
HI 1.
1 1
1 1
1 1 1.
1 1
1 1
1 1
1 1
1 1
1
1 1
1 1
1 1
I
1
1
1
1
* 1 2 .
1
1
1
1
1
1
1
1
1
1
1
1
1
t
1
1 1
1 1 1.5
1C
1
1
1
.?!
1
1
.91
1
1
1
1
1
.21
1
1
1
1
(
1
1
31
1
51
|
1
51
|
1
1
1
1
1
1
1
1
1
1
1
|
|
|
9|
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
UGAl 1 Sir.AL 1
IJNITS | UNIT1 |
"-B "1 IS »C P*« «{. IS T
III II
X 1 1 1 II
X II XII
42* 1 1 1 II
1 1 J.6I '5 1
XIII 1
9* 1 1 1 1
III 1
X 131 2.61 2^ | 1
X 1 M 1 0. 3 1 •>" II'.
Ill 1 1.
XII 1
424 |*| S.ll 49 1 «.
1 1 «.ll 40 | 4.
1 1 5. II 49 |S1?.
X 1 1
1 1 ?.6I 25 1
XIII 1
1 1 1
III X 1
1933 III 1
III 1
47 1 1
II II
II II?.
47 || X|
1 1
1 1 1
X 2110.31 90 11 !A.
X 11*0. 0| J04 V
t 1 1
II 1 XII
III II
III X 1
III 13.*
1 1 2.6 1 25 1
1 1 711 3.
XII 1
II 1 3.4
II 1 1.1
1 1 1
9* | 7..6I 25 1
1 1 1
XII 1
I 2.61 25 1
III 41 *.«
XII 1
1 1 1
XII 1
1 1 1
1 1 1
1 1 1
II 1 1.1
XII 1 3.4
1 1 1
9* 1 1 X 1
1 I XII
II II
XII II
1 1 5.11 49 II
X 1 1 1 XII 1
47 | | 2.61 *.•> 1 1 1
A 1 C A 1
- oc^ M,
t
\1\
4n
74">
!»7
UL •>
X
K
91
X
X
1 ?9*
l 2 1
X
! ?!
406
I 2 T
41
*
•H?
X
X
*
K
40
! 21
X
45
-------
LAKE NAME: NORFORK LAKE
STORET NUMBER: 051?
NYGAARD TROPHIC STATE INDICFS
OA'T<= 04 04 To 06 19 74 09 03 74 10 10 76.
MYXOPHYCEAN
CHLOOOPHYCEAN
DIATOM
•COMPOUND
02/0 F
02/0 E
A / .-)A 9
J/ -It f
1.10 E
11/0 F
0/01 0
1.00 E
1.00 E
4.00 E
5. 00 E
2.00 c
0.17 ?
9.00 F
06/0 F
05/0 F
0. 75 P
15/0 ?
PALMER'S ORGANIC POLLUTION INDICES
DATE 04 Ot 74 06 19 74 09 03 74 n 10 74
GENUS
SPECIES
01
do
01
00
10
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE
4VERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES COMPOSITED
KAXIMUM DIVERSITY
MINUMUM DIVER SITY
TOTAL DIVERSITY
TOTAL NUMPER OF INDIVIDUALS/ML
CVENF.SS COMPONENT
RELATIVE EVENFSS
MEAN NUMBER OF INDIVIOUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
04 04 74 06 19 -"* 09 03 74 10 10 74
H
S
q
MflKH
MINH
D
H
J
RJ
L
K
2.28
20oOO
7.00
4.32
0.16
3210.24
1408.00
0.53
0.51
70.40
556.00
2.45
17.00
7000
4.09
0.11
4304,65
1757.00
0.60
0.5P
103.35
645.00
3.24
19.00
7.00
4.? 5
0^06
13588.56
4194.00
0.76
0.76
220.74
805.00
3.??
28.00
7.00
4.81
0.12
10277.25
?P°5.00
0.70^.00
46
-------
LAKE NAHE: NORFflRK LAKE
STORET NUMBER I 05111
TAXA
ACMNANTHES MICROCE PHAl A
ANABAFNA
ANK isrHtiOESxus FAIT.ATUS
APH»«I1 70MENHN FLOS-AQUAE
ASTERttiNEiiA FORMOSA
C?NTPIC DIATOM
CFPATIUM HIRUNDINELIA
F. FURCOIOES
CERATIUM H1RUNDINEUA
F. ROBUSTUM
CIWOCWONAS ACUTA '
CHP.OOMONAS ACUTA ?
CIOSIFRIUM
COSMA"HIM
CPUCIGFNIA TETRAPEDIA
CRYPTOMONAS
CRYPTOMONAS EROSA
CRYPTOMflN»S HARSSONII
CYCLOTFllA
CYClOTEllA COMTA
CYCLOTF.IM MIC1MGANIANS
CYCIOTPILA STELIIGFRA
CY1BF1LA TUMIDUIA
nACTvi.ncoccoPSis
OIATPHA VULGARE
V. B'EVE
DINORRYON SOCIALE
CNTOMPNEIS ORNATA
EUGLEN*
FUCFILATE 12
TKAGHARIA CROIONFNSIS
fBUNCEIA OVALIS 7
LVNCBYA BIKGEI
HALLOMONAS
MIMAOHONAS PSEUOOtORONATA
OI5TAN5
GRANULATA
MFLOSIRA VAR1ANS
MERISMOPEDIA MINIMA
MF.RlSMijPEOtA
MICPOCYSTIS INC?R'A
MOUCEOTIA
MAV1CUIA
NEPHROCYTIUM
C1NTINUEO
r)4 04 74
11 11 74
NITZSCHIA II
NITISCMIA »J
NITrSCHIA VERMICULARIS
nsc IUATHRIA
PEDIASTRUM SIMPLEX
PEOIASTRUM SIMPLEX
V. PUOOENARIUM
PFRlnlNIUM
PERI01NIUM (2
PER1DINIUM MUNUSCUIUM
PFPIDINIUM (JUAORIOrNS
PFRIOINIUM SPP.
PHACUS MEGAtOPSIS
RBPHlniOPSIS CURVATA
SCFNEDESMUS OUAHRICAUOA
SCHBOfOERIA SEIIGEPA
STE"HANODISCUS NIAC.ARAE
ST|P|TOCOCr.US
SY"EPRA ACUS
rABELLARIA FENESTRATA
TETRAEORON MINIMUM
V. SCROBICULATUN
TOTAL
CEl
F1L
CEl
Fll
CEl
CEl
CEl
CEL
CEL
CEL
C€l
CEl
COl
CFL
CEL
CEL
CEL
CEl
CEL
CFl
CF.L
r.Fi
CEL
CEL
CEL
CEl
CEL
CEl
CFl.
Fll
CFl
CFl
CFl
CEl
CEl
COl
COl
COl
CEl
CEl
CEl
CEl
CEl
CFl
CEl
Fll
COL
cm
CEl
en
CEl
cri
CEl
CEl
Fll
cm
CFl
CEl
CEl
CEl
CEl
CEl
ALGAL
UNITS
S »C PFR ML
5.3
7 39.5
« 5.3
5 5.3
I 29.0
3 5.3
11). 5
X
X
74
556
74
X
X
X
X
X
7»
408
X
X
X
X
X
X
7«
l*B
.
AlGAl
UNITS
S *C PER Ml
f
3
'
»
1
5
.
2.0
4.1
6.1
4.1
4.1
2.0
34.7
36.7
'
2.0
2.0
2.0
16
X
72
X
X
117
77
72
36
600
X
645
;
X
X
.
36
36
36
Alf.Al
UNIT*
s tr P" MI
51 0.6| '-07
1.
4
3
2
6.R
(
19.7
0.7
15.1
1.4
11.1
1 .4
R.7
1.4
8.7
X
•>B7
X
flfll
X
'45
X
637
ST
A'»
X
ST
?45
5T
X
145
K
S.5| 230
IIM1TS
1 V Pep M|
'
1
S
ft
1
1.4
4.7
1 1.1
1.4
fl. <
17.5
•i.6
4.7
70. P
6.0
5. 6
7. n
6.0
6.0
X
41
X
171
'
«0
377
4D
741
X
r
3*7
161
V
X
17'
60'
70'
X
|M
X
X
r
"1
701
K
201
1408 1757 4104 2»9S
47
-------
LAKE NAME: LAKE OUACHITA
NtlMBEP : OM4
NYGA4T) TROPHIC STATE
DATf 03 2^ 74 06 06 74 10
74
MYXOPHYCEAN
CHLOROPHYCF. AN
EUGLFNOPHYTC
OI4TOM
COMPOUND
0/0 0
03/3 E
l/D"* ?
2.00 F
07/0 ?
1.00 F
0.67 ?
1.40 F
0.50 F
3 .00 f
7.00 c
2.00 P
1/19 7
0/0' ?
9.00 *
PALMER'S TJGANIC POLLUTION INOf
03 23 74 06 06 T4 10 17 74
GFNUS
00
00
01
00
01
00
AVERAGE DIVERS ITY
NUMB6P OF TAXA
NUMBER "^ S-1MPLFS CO»1PnSITEO
HAXTMUM DIVERSITY
"I NU^U" 01 VFRSI TY
TOTAL OWFPSITY
TOTAL NUMRER OF I NO IV I (XI AL S/ML
5P=riFS OtVFOSITY AND ABUNDANCE
03 25 74 06 06 74 10 17 74
RELATIVE FVENESS
MEAN NU^SEP OF I NOI V IDU ALS/ T AX A
NU^RFR/Mt OF M05T ABUNDANT T4XON
H
S
M
MAXH
MJNM
T
N
J
PJ
L
<<
1.47
12.00
6. 01
3,58
0.46
3?3.41
??0.00
0.41
0. 33
lfl.33
m. 11
2.71
20.00
f.30
^.32
0 .OR
8176. -)7
^017.00
O.fr3
0.63
1 50. 9S
77.13
3. 44
2! .00
6. 37
4.3°
0.14
S841 .1 ?
169*. 00
0.78
0. 78
80. «6
766.11
-------
»MFI L«Kf OUKHI'l
WB6B: HI*
c-JiM
AfllFIUjt PLANCTONICA *Il
,N, rSTooDES«US FALCATtlS CFl
V. « !»ABIl IS l~-t
1PHAM70MFNON FlOS-AOU»€ ML
ABTMPTESMUS MIWI3P 7 CEL
_ fOHFI 1 A FORMOSA rcl
C?»,fP!C DIATOM r-ft-
' lornlnF* rFL
rHc"nnwnnAS »CUT* CEI
r L OSTC° inpsr s ^*-
CICSTEBIU1 CFl
rayoTOMONHS MiRSSONII ' E l
OICTTIOCOCCOPSIS CFl
iMNOS'YfJN ^f-
FL«OEII»TE «? cn-
SY«SODIN[U" A18ULU" CFl
L TVGBVA c "•
MAlirM^Sfc^ PS EUOOCPRHN AT A CEt
^cinc'RA TTSTANS CFL
Mfn^ipArRftNUt4T* ^^*-
• cpjsMrPECI" TE»IUISSI«A COl
M[C0OC»S^1S INC6R" COl
"TUG^OTIA c "•
"SC tlL*TOtt» It '"•
otrTA
700
«
?)'
"
M
'0"
ft T
' on
x
?6 ^
X
»
1 1
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X
• *> ^ 1
1.0 "
1
49
-------
LAKE NAME: TABLE ROCK LAKE
NUMBER: 0515
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTC
DIATOM
COMPOUND
NYGAA^O TROPHIC STATF INDICES
04 OS 74 06 18 It* 09 04 74 11 13 74
03/0 E
01/3 E
0/04 7
1.23 F
10/3 E
05/0 F
06/0 F
0/11 1
1.33 F
15/3 E
1.00 F
7.67 F
o.oo ^
1.50 e
5.33 F
1.50 F
1.00 f
0.60 P
0.40 F
5.30 F
PALMER'S ORGANIC POLLUTION INDICES
DATE 34 35 74 36 18 74 09 04 74 \3 13
GENUS
SPECIES
06
00
03
30
05
33
00
33
SPECIES OWEBSITY ANO ABUNDANCE INOtCFS
DATE 34 35 74 36 18 ^4 39 -)i, 74 13 10
AVERAGE OIVERSITY
NUMBER f?F T\XA
NUMBER CF SAMPLES COMPOSITED
MAXIMUM DIVERSITY
MINUMUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIOUALS/ML
F.VENESS COMPONENT
RELATIVE F.VENESS
MEAN NUMBEP OF INOIVIDUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
S
M
,XH
NH
D
N
J
RJ
L
K
2.89
10.03
0.00
4.25
3. ~>7
9554.34
3306.00
3.68
0.68
174.00
882.00
3.49
29.30
9.00
4.86
3 .?!
5528.16
1584 .00
0.72
0.71
54.62
264.00
1.29
26.33
9.00
4.70
3.32
28796.67
22323.00
0.77
0.28
858.58
17906.00
1.01
24.33
o.OO
4.58
3.3?
16806.40
16640.00
0.2?
0.?2
693. 3'
13893.00
50
-------
LAKf NAXf: TABLE ROCK I. »K E
SIT>FT MUMPER I 051«
CONTINUET
MICROCEPHAL*
APHANI ZO'ENON
iSTFRIONELLA FORMOSA
CfMBIC DIATOM
CFOATIUM M1RUNOINELLA
C«»A1IUM HIRUNDINEILA
F. 60ACHYCERAS
CFRATIU- HIRUNOINELLA
F. FIIRCOI06S
CHPCHMONiS ACUTA
COFLiSTRUM SPMA6R1CUM
r.rjsf.«p IIJH »i
cnr.MisiuM »2
CRU<~ K.ENIA OUAORATA
CRYP70MONAS
CPVPinMONAS EROSA
CYCLflTELLA STELLIGFRA
nuc.mncoccopsis
OIN06PYON SOCIALE
FRAGR A°IA
FR4GILARIA CROTONENSfS
GLFNCiniNIUM
GlENOOINIUM
GIF NODI NIU"
GYMNOOINIUM
«IRCHNERIELL«
NAILCV01AS
HELO«;iRA
HELOSIRA DISTANS
MFIOSIRA GRANUIATA
NELOSIRA ITALIC*
MFlOStRA VARIANS
HFRH-OPEOJA MINIMA
«FR ISMOPfOIA TENUISSI<ENNATf 01 ATOM
PENNATE DIATOM •!
PF«iniNIUM »1
PER10INIUM 12
PfRIOlNIUM IMCONSPTCUUM
RAPHlOtOPSIS CURVATA
SCENEDESMOS ABUNOANS
SCENEOESMUS 8ICAUOATUS
SCENEDESMUS OUAORICAUDA
V. OUAOOISPINA F. SP1IHOSUS
SCHROfOEHIA SETIGERA
SCYTONEOA
STAURASTRUM
STAURASTXU" TETRACERUM
STFPHANOOISCUS
STEPHANOOISCUS NIAGARAE
SYNEORA
SYXEOKA OELICATISSINA
V. ANGUSTISSIMA
TETRAFORON MINIMUM
V. SrvOBICUlATuM
TRACHELOMONAS *1
TRACMFLOMONAS f2
T»EU6»R|A SFTIGERUM
TOT»l
FORM
CFL
FIL
CFL
FIL
CFL
CFL
CFL
CEL
CEL
CEL
CCL
CEL
CEL
COL
CEL
CEL
CEL
C6L
CFL
CEL
CEL
CEL
CFL
CEL
CFl
CEL
CEL
CEL
CEL
Cfl
CEL
CEL
COL
COL
CFl
FIL
CEL
F IL
FIL
COL
COL
CEL
CEL
CEL
CFL
CEI
CE
FIL
cm
COL
COL
COL
CEL
FIl
CFL
CFL
CEL
CEL
CFL
CR.
cei
CH
en
CFl
ALGAL
UNI TS
s *c PFR ML
T.H
5 6.7
<. 7.7
1 23.3
1 .1
3.3
1 26.7
1.1
3.3
1.1
1.1
1.1
? 20.0
X
X
257
220
73
771
37
X
110
8R2
X
37
X
110
37
37
17
661
1.11 37
AIGH
UNI TS
S tC PFR M(
3
1
2
4
2.11 n
1
1 • ^ 1 132
ff.il 112
16.7
12.5
X
X
X
264
X
19*
X
1
2.11 33
1
4.21 61^
4.2
2.1
4.2
2.1
2.1
14.6
2.1
X
6*
3J
66
33
J?
211
X
X
X
X
X
X
X
31
X
Al r.A L
5 V pco ML
1 l»0.? 1 1 70fl*
5
4
3
2
3.0
1 f T
0.2
0.7
0.4
1.1
•>.?
2.6
7.?
0.7
0. ?,
i->o
X
t 0^
40
g
X
14*
X
X
X
X
X
97
?43
40
58?
X
! frO '
4Q
49
X
X
III II
15114.61 2JI 1 | l.T 1g*
III II
III II
III II 1
MC.AI
UNIT
^
77
X
X
1 1
1 1
1 1
3t 3.01 <0>
II X
1 1 X
1 1
«°6 1584 22^73 1*640
51
-------
LAKE NAME: GREEK'S FERRY LAKE
STOPET NUMflPR: 0516
NYGAARD TROPHIC STATE INDICES
DATE 03 2~> 74 06 06 74 09 03 74 10 16 74
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYT?
OIATO**
COMPOUND
2.51 E
2.50 P
0.20 7
0.43 P
7.50 E
3.00 E
3.00 f.
0/06 ?
0.75 f
9.00 E
1 .33 e
1.00 F
0/07 ?
J/02 ?
2. 33 F
1.33 F
1.33 F
0.?5 c
1.0!) e
4. 13 P
PALMER'S ORGANIC POLLUTION INDICES
OAT? 03 27 74 06 06 74 0<» 03 74 10 16
GENUS
SPECIES
04
00
04
00
01
00
01
00
SPECIES OIVERSITY ANO ABUNOSNCP INOICFS
AT^ 03 2~> 74 06 06 74 09 03 74 10 16
AVERAGE DIVERSITY
NUMBER OF TAX A
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY MAXH
CINUMUM DIVERSITY MINH
TOTAL niVFR SITY
TOTAL NUMBER OF INOIV I fX) AL S/ML
FVFNESS COMPONENT
RFL^lVE F.VFNFSS
MEAN NUMBER OF INOIVIOUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
S
•4
!H
IH
D
N
.)
J
L
K
3.35
29.00
4.00
4. 8#>
0.14
8291.25
2475.00
0.69
0. 69
85.34
500.00
2.29
19.00
4.00
4.25
O.Ofl
6666.1 9
2911 .00
0.54
0.53
153.21
1579.00
l.PO
17.00
4.00
4.09
0.05
7941 .60
4412.00
0.44
0.44
?59. 5-»
3098.00
2.3?
?3.00
4.00
4 .1?
0.15
4268.^7
1801 .00
0.5?
0.5'
78.30
678.00
52
-------
LAKE SAME: GREFR'S FFRRY LAKF
STORF.T N
CONTINUE1)
OS 27 74
06 06 74
09 03 74
4NABAENA PLANCTON1CA
ANABAFNOPSIS-
APHAN! ZCtENON
APHANIZOMENON FLti$-AOUAE
ASTER lONELLA FORMOSA
CENTRlr DIATOM .
CERATIUH HIRUNDINELLA
CERATIUM HIRUNOINELLA
<=. FUPCOinES
CHROCMONAS ACUTA
CCELASTRUM HICROPORUM
COSNAOIUM
CRUC1GENIA TETRAPF01A
CRYPTOHONAS
CPVPTQMONAS EROS*
CYNBELIA
OACTYLOCOCCOPS1S
nES"tD
EUGLF.NA
FLAGELLATE
FLAGELLATE 02
FOAGILARIA CPOTONENSiS
F°ANC°I A
GLOEOCYSTIS
GCVPHONEHA GRACIL'E
GYMNOOINIUM ALBULU*
LEPOCINCL IS
LYNGBYA
LVHG8VA 01
LYNG6YA 01
HALLOMONAS ACAR010ES
HFLOSIRA OISTAN5
HE LOS IRA GRANULATA
HfLOSIRA GBANULATA
V. ANGUS! ISS1HA
ME«IS"OPEO!A GLAUCA
-EC ISXOPFOIA PUNCTATA
HERIS'fnPEOfA TENUISSI"'
fICBOCYSTIS INCERTA
NEOHROCYTIUM
NITZSCHIA
11 TZSCMIA 01
1ITZSCHIA 02
OCCYSTIS
CStlLLATORIA
PEOIASTPUM BIRADIATUM
V. LONGECORNUTUM
PER10INIUH ?
P5RIOINIU" MUNUSCULU" 7
PFOIOIMUM UMBONATUM
SCENEDESMUS DENTICULATUS
SCEMEDESMUS D1HQRPHUS
SK£LETOMEMA POT AMOS
STAURASTRUM
STAURASTRUM 01
STAUPASTRUM 02
STtURASTRUM 03
STAURASTRUM TETRACEPUM
SU°I»FLLA
SYNEORO OELICATISSIMA
V. ANGUSTISSINA
TABCLLARIA FENESTRATA
TETPAFORON
TETRAEORON CAU04TUP
TFTPAFOROM M1NIKUP
TETRAEORON MINIMUM
V. SCROBICULATUH
TRACHELOMONAS HISPIDA
TOTAL
FORM
FIL
Fit
FR
FIL
CEL
cei
CEL
CEV
CEL
COL
CEL
COL
CEL
CEL
CEL
CEL
CEL
CEL
CFL
CEL
CEL
CEL
COL
CEL
CFL
CEL
FIL
FIl
FIL
CEL
CEL
CEI
CEL
CEI
COL
COL
COL
COL '
CEL
CEL
CFL
CEL
COL
CIL
COL
CEL
CEL
CEL
COL
COL
CFL
CEL
CEL
CEL
CFL
CEL
CEL
CEL
CEL
CF.L
CEL
CEt
CEI
CFL
ALGAL
•JNITS
S tC PER ML
1
2
3
•>
*
'
3.0
20.2
14.1
2.0
9.1
2.0
1.0
18.2
2.0
2.0
4.0
4.0
1.0
13.1
3.0
1.0
'
X
. X
T>
500
X
350
X
50
X
X
22S
50
X
25
450
50
5O
X
100
100
X
X
25
325
X
7*
2S
X
X
ALGAl
UNITS
S »C PER ML
2
5
3
*
1
1.4
6.9
1.4
6.9
4.2
1.4
1.4
16.7
1.4
2.8
1.4
54.2
X
40
202
40
X
207
121
X
40
40
-
486
X'
40 .
81.
40
X
X
X
1579
AL^.Al
UN' T<
S f. P?" «l
?
it
\
3
,
5
1.4
' .
'
'.1
4.3
?.9
70.2
0.7
5.0
1.4
O.T
2.i)
•).T
f.9
*1
31'
!9»
12"
X
1091
?!
'
710
6'
• • " •
I!
125
1!
X
tl
^25
X
AI r.r.\
'INI r«i
5 »;• oco v|
c
4
.1
2
1
'.2
7. •>
1.?
?T.».
6.4
9.T
1.1
7.?
13.4
1.1
I.!
X
X
•«<>
X
10
X
«s
X
X
X
678
X
1 1*
]T4
X
X
X
1»
30
X
61!
'9
1°
1
2475
4412
53
-------
TECHNICAL REPORT DATA
(Please read Instructions on the reverse before completing)
. REPORT NO.
EPA-600/3-78-101
3. RECIPIENT'S ACCESSION NO.
4. TITLE AND SUBTITLE
DISTRIBUTION OF PHYTOPLANKTON IN ARKANSAS LAKES
5. REPORT DATE
December 1978
6. PERFORMING ORGANIZATION CODE
. AUTHOR(S)
J.W. Hilgert, F.A. Morris, M.K. Morris, W.D. Taylor,
L.R. Williams, S.C. Hern, V.W. Lambou
8. PERFORMING ORGANIZATION REPORT NO.
. PERFORMING ORGANIZATION NAME AND ADDRESS
Environmental Monitoring and Support Laboratory
Office of Research and Development
U.S. Environmental Protection Agency
Las Vegas, NV 89114
10. PROGRAM ELEMENT NO.
1HD620
11. CONTRACT/GRANT NO. .
12. SPONSORING AGENCY NAME AND ADDRESS
U.S. Environmental Protection Agency-Las Vegas, NV
Office of Research and Development
Environmental Monitoring and Support Laboratory
Las Vegas, NV 89114
13. TYPE OF REPORT AND PERIOD COVERED
03-15-74 to 11-20-74
14. SPONSORING AGENCY CODE
EPA/600/07
15. SUPPLEMENTARY NOTES
16. ABSTRACT
This is a data report representing the species and abundance of phytoplankton
in the 16 lakes sampled by the National Eutrophication Survey in the State
of Arkansas. Results from the calculation of several water quality indices are
also included (Nygaard's Trophic State Index, Palmer's Organic Pollution Index,
and species diversity and abundance indices).
17.
KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
b.IDENTIFIERS/OPEN ENDED TERMS
c. COSATl Field/Group
*aquatic microbiology
lakes
*phytoplankton
water quality
Arkansas
lake eutrophication
Nygaard's trophic indices
Palmer's organic pollu-
tion indices
Species diversity and
abundance indices
06 C,
08 H
13 B
M
18. DISTRIBUTION STATEMENT
RELEASE TO PUBLIC
19. SECURITY CLASS (This Report)
UNCLASSIFIED
21. NO. OF PAGES
60
20. SECURITY CLASS (This page!
UNCLASSIFIED
22. PRICE
A04
EPA Form 2220-1 (Rev. 4-77) PREVIOUS EDITION is OBSOLETE
------- |