United States
Environmental Protection
Agency
Environmental Monitoring
Systems Laboratory
P O Box 15027
Las Vegas NV 891 14
Research ancf Development
oEPA
Distribution
of Algae in
Pennsylvania
Working
Paper 689
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DISTRIBUTION OF ALGAE IN PENNSYLVANIA
Working Paper No. 689
National Eutrophication Survey
Office of Research and Development
U.S. Environmental Protection Agency
December 1977
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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 watersheds.
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. The
working paper series reports the results of eutrophication and related
investigations.
-------
CONTENTS
Foreward ill
Part I: DISTRIBUTION OF PHYTOPLANKTON IN LAKES 1
Part II: DISTRIBUTION OF ALGAE IN YORK COUNTY 50
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PART I: DISTRIBUTION OF PHYTOPLANKTON IN LAKES
by
Fabienne A. Hiatt*, S. C. Hern, J. W. Hilgert*, V. W. Lambou,
F. A. Morris*, M. K. Morris*, L. R. Williams, and W. D. Taylor
Water and Land Quality Branch
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
CONTENTS
Introduction ,. 2
Materials and Methods 4
Lake and Site Selection 4
Sample Preparation ,., , 4
Examination 5
Quality Control , 6
Results 7
Nygaard1s Trophic State Indices 7
Palmer' s Organic Pollution Indices 7
Species Diversity and Abundance Indices 9
Species Occurrence and Abundance 10
Literature Cited 11
Appendix: Summary of Phytoplankton Data 12
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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 1973, the Survey sampled 250 lakes in
17 States. Over 700 algal species and varieties were identified and enumerated
from the 694 water samples examined.
This report presents the species and abundance of phytoplankton in the
17 lakes sampled in the State of Pennsylvania (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 PENNSYLVANIA
STORET
4201
4204
4207
4213
4216
4219
4220
4221
4222
4223
4224
4225
LAKE NAME
Blanchard Reservoir
Conneaut Lake
Greenlane Dam
Pymatuning Reservoir
Shenango River Reservoir
Beaver Run Reservoir
Beltzville Dam
Lake Canadohta
Harveys Lake
Indian Lake
Lake Naomi
Lake Ontelaunee
COUNTY
Centre
Crawford
Montgomery
Crawford, Mercer
(Ashtabula in OH)
Mercer (Trumbull in OH)
Westmoreland
Carbon
Crawford
Luzerne
Somerset
Monroe
Berks
(Continued)
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TABLE 1. LAKES SAMPLED IN THE STATE OF PENNSYLVANIA (Continued)
STORE! #
LAKE NAME
COUNTY
4226
4227
4228
4229
3641
Pinchot Lake
(Conewago Lake)
Pocono Lake
Stillwater Lake
Lake Wallenpaupack
Allegheny Reservoir
QCinzua Dam)
York
Monroe
Monroe
Pike
Warren (Cattaraugua in NY)
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MATERIALS AND METHODS
LAKE AND SITE SELECTION
Lakes and reservoirs included in the Survey were selected through dis-
cussions 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 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 repre-
senting 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 (nil) 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 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 supemate and the
volume of the remaining concentrate were measured and concentrations deter-
mined. 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 drop of superconcentrate from the bottom of the test tube was
placed in a ring, of clear Karo® Corn Syrup with phenol (a few crystals of
phenol were added to each 100 ml of syrup} on a glass slide, 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 com-
pound 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
Internal quality control intercomparisons on species identifications and
counts were performed on a regular basis among project phycologists at the
rate of 7 percent. 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 satis-
factory.
-------
RESULTS
The Appendix summarizes all of the phytoplanktqn data collected from the
State by the Survey. It is organized by lake, including 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 STORE! 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 iden-
tify 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 gener-
ally 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, CE) 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
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.
7 Erowonmenisil Protected Agency
Ubrary
4©1 [VI Street, SW, WSM PM-H3.
Weehtagton, D.G,
-------
TABLE 2. NYGAARD'S TROPHIC STATE INDICES ADAPTED FROM HUTCHINSON (.1967)
Index
Calculation
Ollgotrophic Eutrophic
Myxophycean
Chlorophycean
Diatom
Euglenophyte
Compound
Myxophyceae
Desmideae
Chlorococcales
Desmideae
Centric Diatoms
Pennate Diatoms
Euglenbphyta
Myxophyceae + Chlorococcales
Myxophyceae 4- Chlorococcales +
Q.Q-0.4
0.0-0.7
Q.O-Q.3
Q. 0-0.2
0.0-1.0
0.1-3.0
0.2-9.0
Q. 0-1. 75
0.0-1.0
1.2-25
Centric Diatoms + Euglenophyta
Desraideae
TABLE 3. ALGAL GENUS POLLUTION INDEX
(Palmer 1969)
TABLE 4. ALGAL SPECIES POLLUTION
INDEX (Palmer 1969)
Genus
Anaaystis
Ankistrodesmus
Chlamydamonas
Chlorella
Cloatevium
Cyclotella
Euglena
Gcmphonema
Lepoeinclis
Melosira
Mieractinitm
Navicula
Nitssahia
Oscillatorta
Pandovina
Phaans
Fhormidium
Soenedesmus
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
Pollution
Index
Ankistrodeamus faleatus 3
Arttoospira jermeri 2
Chlovella vulgcaris 2
Cyclotella meneghiniana 2'
Euglena gracilis 1
Euglena viridis 6
Gomphonema pavvulw 1
M&losira varians 2
Navicula aryptocephala 1
Nitzsehia acicularia i
Nitzachia palea 5
Oscillatoria chlorina 2
Oscillatoria limosa 4
Qseillatoria princeps 1
Qsaillatoria putrida. 1
Qsoillatoria tenuis 4
Pandorina morion 3
Soenedesmua quadrieauda 4
Stigecalon-Cian tenue 3
Syndra ulna. 3
-------
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 es-
timated from the Shannon-Wiener formula (Shannon and Weaver 1963):
H - -I Pi log, P.,
where P is the proportion of the ith taxon in the sample, which is calculated
from n./N; n. 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 aubsample, 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.
-------
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 impor-
tance 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 calcula-
tions. 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 phyto-
plankton collected at different sampling sites on a 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,
the total diversity CD) was calculated from HN, and the evenness component of
diversity (J) was estimated from H/MaxH (Pielou 1966). Also given in the
Appendix 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).
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 indi-
vidual should not be used in direct comparisons involving various samples
which have different numbers of species. Since MaxH equals log S, the ex-
pression in sits is equal to logg S, or 1. Therefore diversity in sits per
individual is numerically equivalent to J, the evenness component for the
Shannon-Wiener formula.
SPECIES OCCUHRENCE AND ABUNDANCE
The alphabetic phytoplankton species list for each lake, presented in the
Appendix, gives the concentrations of individual species by sampling date.
Concentrations are in cells, colonies, or filaments (GEL, COL, FIL) per
milliliter. An "X" after a species name indicates 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 N. Artin
(ed.), Theory of Probability and Its Applications (translation of "Teoriya
Veroyatnosei i ee Premeneniya") 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.
1,115pp.
Nygaard, G. 1949. Eydrobiological 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 differentr-typ-es-'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 phyto-
plankton. I. The components of the index of diversity from Shannon's
formula. Amer. Natur. 103C929):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 Re-
search Laboratory, Corvallis, Oregon. 91 pp.
Zand, S. M. 1976. Indexes associated with information theory in water
quality. Journal WPCF. 48C8}:2026-2031.
11
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APPENDIX. SUMMARY OF PHTTOPLANKTON 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, MICROGSSTIS 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 uncer-
tainty. 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. '
12
-------
LAKE NAME: BLANCH4PC «ES.
STORET NUMBER: 4201
MYXOPHYCEAN
CHLORCPHYCEAN
SUGLENCPHYTE
DIATOM
COMPOUND
NYGAAQO TPCPHIC STATP INCICES
04 13 72 07 24 73 1C 02 73
0/0 C
0/0 0
01/0 5
0.13 7
03/0 E
2.00 E
24.0 E
0/26 ?
0.12 ?
27.0 E
1.50 E
4.00 E
0.18 ?
1.67 E
9.00 E
PALMER'S C'SANIC POLLUTION INDICES
DATs 04 13 73 07 24 73 10 02 73
GENUS
SPECIES
02
03
06
00
01
00
SPECIES DTVEP.SITY AND ABUNDANCE INDICES
DATE 04 13 73 07 24 73 10 02 73
AVERAGE DIVERSITY
NUMBER OF TAX A
NUMBER OF SAMPLES CCMPOSITEO
MAXIMUM OIVEPSITY MAXH
TOTAL DIVERSITY
TQTAL NUMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
MEAN NUMBER OF INOIVIDUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
S
M
:H
0
N
J
L
K
2.40
20.00
3.00
4.32
1312.30
547.00
0.56
27.35
212. CO
2.94
41.00
3.00
5.36
26659.92
9068.00
0.55
221.17
3680.00
2.24
27.00
2.00
4.75
2009.23
897.00
0.4t
33.22
359.00
13
-------
LAK? NAME:
STCPET MJH861: 4201
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T8AO-ELCHTNAS VOLVOCINA
FOSM
CEL
CSl
FIL
CEL
FIL
COL
CEL
CEL
COL
CCL
CEL
CEL
CEL
CEL
CEL
CEL
C6L
C3L
COL
COL
C«L
FtL
CEL
C?L
CEL
COl
CCL
CEL
C5L
CEL
cei
CEL
CEL
CSL
CEL
CEL
C6L
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CEL
CEL
CEI
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CEL
CEL
COL
CCL
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CEL
CEL
COL
CCL
COL
cot
CCl
COL
CCL
CCL
COL
CCL
COL
CCL
CEL
C«l
CCL
CEL
CEL
CEL
CEL
CCL.
CEL
UGAL ALGAL
1 UMTS UNITS
S tC »ER *L S tC PER ML
I
2
*
S
3
38.9
20.3
11.3
2.2
4.3
6.8
13.7
X
X
X
212
X
x
x
112
62
X
X
X
12
X
37
X
X
37
X
M
4
2
S
3
1
0.8
0.3
2.8
12.5
1.8
0.3
1.0
2.3
3.9
o.;
19.4
40.6
o.«
2.0
1.9
1.0
2.0
o.s
2.0
69
X
X
X
X
23
255
113*
X
162
23
X
X
92
254
3*7
X
46
X
X
1759
3690
X
46
X
X
US
162
«2
X
185
46
X
195
0.31 23
0. 5 1 *6
2.91 2!*
X
X
x
X
ALGAL
UMTS
S tC PE" »L
5
2
3
4
I
0.7
1.4
0.7
2.9
2.9
38.6
4.3
2.7
40. a
2.1
0.7
0.7
0.7
K
X
X
X
6
X
13
X
6
X
26
26
X
34 1
39
2ft
359
19
6
X
X
X
X
•>
6
X
1.4| 13
5*7 90*6 897
14
-------
LAKE NAME: CQNNEAUT LAKE
STCRET NUMBER: 4204
NYGAARC TRQPHIC STATE INDICES
DATE 04 21 73 07 27 *3 10 05 73
MYXCPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTE
OIATCM
COMPOUND
01/0 5
01/0 E
0/02 ?
0.33 E
05/0 E
04/0 =
02/0 E
0/06 ?
C.50 S
08/0 E
3.00 E
2.00 5
0.10 ?
0.30 E
15.0 E
PALMER'S ORGANIC POLLUTION INDICES
DATE 04 21 73 07 27 73 10 05 73
GENUS
SPSCIES
01
00
02
00
00
00
SPECIES DIVERSIFY ANC ABUNDANCE INDICES
DATE 04 21 73 07 27 73 10 05 73
AVERAGE DIVERSITY
NUMBER Of TAXA
NUMBER CF SAMPLES COMPOSITEC
MAXIMUM DIVERSITY PAXH
TOTAL DIVERSITY
TOTAL NUMBER OF INOIVIOUALS/»L
EVENESS COMPONENT
MEAN NUMBER CF INOIVIOUALS/TAXA
o«= MCST ABUNDANT TAXON
H
S
M
;H
0
N
J
L
K
2.36
21. CO
2.00
4.39
2329.32
937.00
0.54
47.00
335.00
3.02
13.00
2.00
4.17
2986.73
939.00
0.72
54.94
203.00
2.39
26.00
2.00
4.70
1479.63
512.00
0.61
19.69
132.00
15
-------
LAKE NAI«E: CCNNEAUT LAKE
STORE! NUMBER: 420*
TAXA
ACHNANTHES WIC
ANABAENA
ANABAENA »Z
ANABAENA PLANCTNICA
APHANGOPSA 7 SLA-rMS'A
APHAM-CAFSA ?LACHSTA
ASTER1CNELLA P3«»3SA
ECTRYOCCCCUS BRAUNI!
CERATlUN HIRUNOI*<-LLA
CHLAHYCCNONAS
CHPCCCCCCUS
CCNTINUEO
0* 21
07 27 73
10 05 73
CLCSTERIU*
CCCCCNE1S
COCCON6IJ PLACFNTULA
V. EUGLYP'A
COCCCN"1S SCUTBLL'J»
COELOSPKAERiu" NA5GSLIANU*
CPYPTCMCNAS
CP>PTC»««AS OVAT»
CPVPT3MCNAS TENUIS T
CVANOPHYTAN PILA»?NT
CYCLGTEULA 8COAN1CA
CYCLOTELLA STELLI36I»A
CYI«BELLA
OINC8RYCN
CINCBPY5N
EPITVE^IA
TU
-------
LAKE NAPE: GR«NLANF 0AM
STCRET NUMBER: 4207
NYGAARC TRCPHIC STATE INDICES
OATg 04 17 73 07 24 73 10 03 73
MYXOPHYCS&N
CHLOROPHYCEAN
EUGLENOPHYTE
DIATCM
COMPOUND
0/0 C
04/0 E
0/04 ?
0.40 £
OS/0 5
2.50 c
3.03 E
0.09 ?
1.50 E
7.50 E
4.GO E
8.00 E
0/12 ?
0.64 E
19.0 E
PALMER'S CRGANIC POLLUTION INDICES
DATE 04 17 73 07 24 73 10 03 73
GENUS
SPECIES
09
04
02
00
10
06
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES CCMPQSITED
MAXIMUM DIVERSITY MAXH
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
?VENESS COMPONENT
MEAN NUMBER CF INOIVIOUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
04 17 73 07 24 73 10 03 73
H
S
M
:H
0
N
J
L
K
0.67
21.00
4.00
V.39
10231.57
15271.00
0.15
727.19
13676.00
1.65
20.00
i.00
V.32
4557.30
2762.00
3.38
138.10
1967.00
3.02
34.00
3.00
?.09
17688.14
5857. CO
0.59
172.26
1838.00
17
-------
LAKE NAIF: GRE5NLANE 0AM
STCPET NUMBERS «207
"AX*
ACHNANTH6S LANCKCLAT4
ANA8AFNA
APHANIZCPENCN
APHANIZCPENON FL1S-AQUAE
ASTERICNELLA
ASTERICNELLA
V. GRACILLIMA
BCTPYCCCCCLS B««UNTI
CENTPIC 01 ATOM
CERATIU* HIRUNOIK6LU
CHLAMVOCMONAS 7
COCC?I9 CELL
CCELASTRUM PICSCP1RU*
CCELOSPHAE«IU* NAaGELlANU"
CCJNARIUH II
CCSMM1UM »2
CRUCIGENIA APTCULATA 7
CPYPTQKONAS EP.OSA
CPVPTCM&AS fTVA'A
CYCLCTELLA MENEGHIMANA
C1ATQK*
EUNOTIA
FLAGELLATES
FRAGILARIA
FPAGILARIA
CCNTINUfO
0* 17
07
73
10 03 73
V. PPCOUCTA
"SLOSH* OISTANS
CEIOSIPA GPANULAT*
MELOS1PA GRANULATt
V. ANGUS' ISSTM
MELOSIRA ITtLICA
"EIQSIRA ITALICA
v. TENUISSIMA
CEtCSIRA VARIANS
CICPf!CYSTTS AEPUGINCSA
HICPOCYSTJS INCERTA
NAVICULA
NAVICULA *1
NAVICULA »Z
NAVICULA LANCE3LAT* 7
MITZJCHIA
NITJSCHTA II
OOCYS'TS
CICILLATOPIA
PAKOCPTM
PEOTAS'PUM CUPLEX
V. CLATHRATUM
V. PE'ICULATu-4
P6CIASTRU" SIMPLEX
V. COOO?NAPIU."
PPKNAff CIATC«
PHQR"IOIU» "UCICQLA
?CENEO?SIHJS
SCENEOESfg« ACUTUS
v. AL^EPNANS
SCEKEDESI'US C=«tTICUlATUS
SCENEDESKUS t«tT«Ri.BOIUS 1
scEiieoestos OWACOICAUO*
SCEN606?»LS CUA001CAUDA 1
SCENSOE'CUS CUACOICAUOA
V. LCNGISPtNA
SPHAEPQCYSTIS 7 SCKPOETMI
$TAURASTRUI> PAOACCXU»>
«'?PM«(00!SCllf 7
STFPhANCCTSCUS AST'AEA
STEPMANCOISCUS HtNTZSCHII
SUBIPELLA
SYNECPA
JYhFCRA CELICATISSI"A 7
V. ANGl
-------
LAKF NAME: PYMATCNING
STCPET NUMBED: 4213
NYGAAPO TPOPHIC STATE INCICES
DATE 04 21 73 07 31 73 10 06 73
CHLOROPHYCEAN
EUGLENOPKYTE
DIATOM
COMPOUND
2.67 E
6.00 E
0.04 ?
1.00 E
10.3 5
2.40 E
5.60 E
0.05 ?
1.00 E
9.60 E
3.20 5
5.40 E
0.05 ?
1.00 E
10.4 E
PALMEP'S ORGANIC POLLUTION INDICES
OATE 04 21 73 07 31 73 10 06 73
GENUS
SPECIES
19
04
17
04
16
03
SPECIES DIVERSITY AND ABUNCANCE INDICES
DATE 04 21 73 07 31 73 10 06 73
AVERAGE DIVERSITY
NUMBER OF TAXA
MJM8ER OF SAMPLES CCMPOSITEO
MAXIMUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
EV6NESS COMPONENT
»»EAN NUMBER CF INDIVIDUALS/TAX A
NUMBEP/ML OP MOST ABUNDANT TAXCN
H
e
M
MAXH
0
N
J
t
K
2.60
43.00
4.CO
5.43
33152.60
12751.00
0.48
296.53
6169.00
3.90
63.00
4.00
5.98
60736.60
15597.00
0.64
253.92
3769.00
4.24
69.00
4.00
6.11
62603.60
14765. CO
0.69
213.99
2799.00
19
-------
LAKE NAME: PYNATUNtNG
SECRET NUMBER: 4iU
CCNTIKU5C
0* 21 73
07 31 73
K
TAXA
LANCSCLATA
ACTINAJTRUI" HA
ANAPAENA »l
4M6AEN4 «2
AttABAENA »3
ANA8AEN9PSIS
ANABAENCPSIS PMIL IPP1NENSIS
AKKI STRODE SmJS
ANKISTROOESMUS «AI,CATUS
APHANIZC»E^N 7
AStSRICNELLA PO'PQSA
BOTRYPCJCCUS
BCT9YGCCCCLS 3RAUNII
CSRATJU* H1RUN91NELLA
CLCSTERICPSIS
CLCST5RICPSIS 7
CCELASTRUM CAMBRICUM
COSLASTRUM CAH8RICUP ?
V. INTERWEOIUK
CCELASTRlll* CAMBRICU*
V. INTERWEDIU"
CC'LASTRUM MICROP3RUH
CCELASTRU" RrnCULATU"
COELASTRUH SPHA?RICUM
COELOSP^AEPIUM NAEGELtAWJN
CCSNARIUC «l
CCSHARIUM 12
CRUCIGENU APICULA-TA
CRUCIGENU TETRAP«CU
CRYPTOBONAS EROSA
CVCLOTELLA «EN?GHINIANA
PULCHELLUM
OIVERGENS
CINQ8PYCN SE*TUIA*I»
OINCPIAGEVIAT?
EUASTBU*
EUCLENA
PLAGELLATES
PRAG1LARIA
FRAGRJ'IA CROTCKE1SIS
GLENCOINIUO PULVtSCUlUS
GCLENKINIA
t-UNATP CELL
LYNG8YA »1
LYNG8YA n
LYNGBYA LAGERHS1MI
KLOStPA
fELCStRA «Z
MELOSIRi 13
«LQSTR» CISTASJ
CELOSIRA GRANULATA
V. ANGL!T!SSIMA
HERIS»ODEDIA TEXUISS1NA
fTCRACTJMUH PUSILLUK
"TCRCCYfTS AERUG1NOSA
PKROCYSTIS INCERTA
NAVICULA «l
NAVICUIA «2
K1TISCHIA
NinSCHIA &C1CUUARIS
COCYSTtS
CSCILLATCR1A
OSC1LLATORIA ft
CSCILLATCPIA *2
PSCIASTRUM BORYANOH
PECIASTRU" CUPLEJI
CUPLEX
V.
CUPLEX
SIH0LEX
CUCOENARIU"
CR"
CSL
CEL
PIL
PIL
PIL
CEL
CEL
PIL
CSL
C2L
COL
CSL
CEL
CEL
CSL
COL
CCL
CGL
COL
COL
CCL
COL
CEL
CEL
COL
COL
CEL
CEL
COL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
PIL
PIL
PIL
CEL
CEL
CEL
CEL
CEL
CEL
CCL
COL
COL
CCl
*1L
cei
CEL
CEL
CEL
CEL
PIL
PIL
PIL
CCL
COL
COL
COL
COL
ALGAL
UNHS
5 tC P?R "L
1
4
2
0.3
0.6
48.4
2.7
0.6
0.1
3.8
3.5
22.1
2.4
0.3
0.6
1.2
1.2
1.3
0.9
33
75
(169
339
75
X
X
33
489
X
451
X
X
2821
X
X
X
X
301
X
33
X
75
ISO
150
X
X
226
113
X
X
ALGAL 1 A-.vti.
UNITS I .-.:-;
S K PER "L IS 1C c = - "V
3
2
1
4
1.3 292
4.7 74s
0.61 97
1.21 195
1 X
3.21 32
3.2
3.4
3.2
0.2
0.2
2.8
X
X
32
43
X
X
32
X
X
X
X
32
32
X
454
X
0.6 1 97
1 X
1.21 195
23.51 3765
22.31 3570
2.41 389
I
1.61 260
1
1
2.0) 326
1
1.4) 227
0.31 130
1
I X
3.51 552
1
1 X
1
6.91 1103
l.4( 227
0.4| 65
1
1
3.4) 65
0.91 130
1
1
3.21 32
1
1 X .
1
3.21 32
4
•
3
1
5
2
1
1 «
c. 3 1 :• ?
1.11 i;T
'.51 '.'.CO
C.9I 118
o.si lie
0.51 '9
1
3.5i ;n
C.3I 35
1 *
1
C.3I 35
I X
1
1 X
1
3.21 39
1
0.31 39
1
3.31 39
1
1
'..'.I 157
0.31 39
1
1 X
« . 3 1 35
1
0.31 39
O.SI 79
X
1
1 x
X
9.51 1257
1 X
X
1
13.9) 2789
4.01 539
1.11 157
3.51 Ml
0.81 118
I. II 157
1
3.21 471
X
1.11 157
7.51 1100
0.31 39
1 X
5. 1 1 74«
1
X
1
13.01 192!
0.31 39
0.31 39
0.3i 39
0.31 39
20
-------
LAKE
H?: PYMATUNING
NUMBER: 4 12
STAURASTSUM 13
ST4UPASTPUN »*
STEPMANCC1SCUS
STEPMANCO! SCUS ASTHAE»
SVNEWA
•ABEUABIA FENP«T?ATA
TSTPAEO'ON CAUOATUn
TETPAECPCN IOBUL t*(j»
TETRAEORCN MINIMUM
f;TPASO«aN REGULARS
T?TRAECPCN REGULAOE
V. INCUS
TETRASTRUM HETERACANTHUM
STAURC6ENIAEFQRKE
TCTAL
PORf
CCL
CEL
CEL
CEL
CEL
COL
COL
COL
COL
COL
COL
COL
COL
COL
COL
CCL
COL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CCL
COL
CEL
1
5
3
5
tc
0.3
4.»
0.6
0.3
».!
ALGAL
UNITS
PER ML
X
39
*
X
X
X
402
X
X
75
38
451
X
12*51
1
1
IS
5
K
0.2
0.6
2.2
0.2
3.5
3.2
0.2
9.3
2.0
5.2
ALGAL
UNITS
PER *L
32
X
X
97
357
32
552
32
X
32
X
X
X
1331
326
32
X
X
X
X \
1399T
1
IS
tc
0.3
0.3
0.3
4.0
2.4
0.3
o.s
0.3
3.2
1.3
0.3
ALSAL
UNITS
PER HL
X
39
39
39
589
X
354
39
T9
X
35
X
>
'
471
194
39
X
X
X
)
•X
X
14745
21
-------
LAKE NAME: SHENANGQ RIVER RES.
NUM9ER: 4216
NYGAARC TROPHIC STV= INDICES
CATE 04 20 *3 07 30 73 10 C8 73
MYXOPHYCEAN
CHLOROPHYCE«N
EUGLENQPNYTE
COMPOUND
01/0 E
03/0 E
0.25 E
0.29 7
07/0 E
2.20 E
2.90 =
0.04 ?
1.00 E
6.20 E
2.00 E
3.67 E
D.04 ?
1.33 E
9.33 E
PALME* «S ORGANIC PGUL'JTKN INDICES
04 20 73 07 30 73 10 08 '3
GENUS
SPECIrS
10
03
13
00
21
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
GATE 04 20 73 07 30 73 10 C3 73
AVERAGE DIVERSITY H 1.75 3.60
NUMBER CF TAXA S I*.00 46.00
NUMBER HF SAMPLES CCMPQS1TEC M ^.00 3.00
MAXIMUM DIVERSITY MAXH 4.09 5.52
TOTAL DIVERSITY 0 628'+.25
TOTAL NUMBER OF INDIVIDUALS/ML N 3591.00
EVENESS COMPONENT J 0.43
MEAN NUMBER OF INOIVIOUALS/TAXA U 211.24
NUMBER/ML OF MOST ABUNDANT TAXON K i706.oo 1506.03
3.34
39.00
i.oo
5.29
14823.40 110450.00
&119.00 2S77S.OO
0.65 0.73
99.54 737.32
6050.00
22
-------
LAK* NAM5: SHF.NAKGC STVFR RES.
STCRFT NUMBER: 4216
TAXA
ANA8AENA
AKABAEM «l
ANA8AFNA §2
ANABAENA PLANCTCNICA
ANKISTRCOESMUS
ANKISTRqOESMUS HI
AM» 7
fELCSIPA GRANULAT*
V. OELICATISSI»«A
f«LOSIPA I'ALJCA
••EPISHCPEOIA
P6RISMCPEOIA PUNCTATA
MFRISMOPEOIA fBMgisjin*
KICPCCYSTIS
"ICPOCY5TIJ AERUGINOSA
flCROCYSTTS IMCERTA
NAVtCULA
MITZSCMIA
CCCYSTI!
OSCILLATQP.IA
QSCILLATCOIA
C*i 20 73
07 30 T3
10 Ofl 73
"*•
v.
PSOIASTRUN
V
SCEN60FSMUS
SCEN'E06S»US «1
SCSNeof SWUS BtJUCt 7
V. 8ICAUCATUS
SCEKEOeSMfS OU4CRICAUDA
V. LTNGTSPINA
SFLENASTRUP
SPMAEPCCYSTIS 7 SCMPCSTERI
S SCM06T5PI
FORM
FIL
FIL
FIL
FIL
CEL
CEL
CEL
CfL
FIL
CEL
CCL
CEL
CEL
CEL
CEL
CEl
COL
CEL
CEL
CEL
COL
CCL
COL
COL
CEL
COL
COL
COL
COL
CEL
CEL
CEL
COL
CQL
CEL
CEL
CEL
CEL
CEL
CEl
CEL
CEL
ceu
CEL
CSL
CEL
CEL
FIL
CEL
CEL
CEL
CEL
CEL
COL
CCL
COL
COL
CCL
COL
CEL
CEL
ca
PIL
FIL
COX
COL
CEL
CCL
COL
COL
COL
cn.
CEL
COL
COL
1LG4L
IJNfS
s tc «R ML
?
t
*
3
2
"
2.3
3S.T
J.J
U 1
**.5
l.T
.
59
1339
193
X
*0
X
X
X
X
X
X
1706
X
60
X
0.61 20
ALGAL
UMTS
S tC PER ML
1
21 T.8I 123
1136.61 1506
^
*
5.91 2*2
0.7| 27
1
1
1 X
7.31 323
1
1 *
1.31 5*
1
0.71 27
2.01 31
1
1
1
2.01 31
1
1 X
1 X
1
1.31 !*
1
1 X
1
1
1
2.01 31
1
1
1 X
1
1
1
0.7 1 21
1
3.21 21?
t
1 X
1
1 X
1
1
1 x
1
1 X
3.9| 161
1
1
1
O.TI 27
2.61 108
1
1 X
1.31 5*
1
1.31 34
1.31 i*
1 X
1
1 X
1
0.71 2T
1
1 X
1
1.31 34
1
1
0.7) 27
1
1
3.T| 27
1
1
1
1 X
t
• LG»C
UMT5
t jc P?B ML
1
2
3
1 *
1
1
1
1
3.1! 330
1.71 ««!
1 X
1
1
1
0.61 169
1 >
1
1 «
21.01 6C?C
12.61 3630
1
1
1
1
1 x
0.31 220
1
1
1
0.21 :;
1.01 275
1.31 385
1
1
t.7| l«!
1
3.1f 88C
1
0.21 55
1 X
1.01 27!
1
1
1
C.4I IK
1
1.9t ISO
6.11 1760
1
1
1
1
1 >
1.01 27*
1
1
1
2.9) 0032!
1
1
10.51 3135
1
1
C.2I f!
1
1
o.2l ;:
I
I
I
I
;.2I 55
3.61 104!
S.2I 01770
1
C.3I 220
1
1
1
1
C.2I if
1
1
23
-------
LAKE N»»e. SHEBANG? BtvER RES.
STOR<-T
CCNTINU'-O
04 20 73
OT 30 '3
10 CB 73
TAXA
STAU»A£TBU* «I
S7AURASTSU* »Z
-------
LAKE NAME: BEAVER RUN RES.
STCPET NUMBER: 4219
NYGAARO TROPHIC STAT5 INDICES
DATE 0* 23 73 07 28 73 10 05 73
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTE
QIATCM
COMPOUND
0/0 Q
0/0 0
0/0 7
o.ao E
04/0 E
2.00 E
4.00 E
0.17 ?
3.00 =
10.0 =
01/0 5
01/0 E
0.50 E
1.25 E
08/0 E
BAUER'S ORGANIC POUUTICN INDICES
DATE 04 23 73 07 28 73 10 05 ?3
GENUS
SPECIES
00
00
01
00
01
00
SPECIES DIVERSITY AND A8UNCANCS INDICES
DATE 04 23 73 07 23 73 10 05 *3
AVERAGE DIVERSITY H
NUMBER OF TAXA S
NUMBER Q«= SAMPLES CCMPQSITED M
MAXIMUM DIVERSITY PAXH
TOTAL DIVERSITY 0
TOTAL NUMBER OF INDIVIDUALS/ML N
EVENESS COMPONENT J
MEAN NUPB5R OF INOIVIDUALS/TAXA L
NUMBER/ML OF MOST ABUNDANT TAXON K
2.56
16.00
2.00
4.00
773.12
302.00
0.64
13.98
101.00
1.45
19.00
2.00
4.25
1193.35
823.00
4.34
43.32
48 7'. 00
1.36
19.00
2.CO
4.25
2103.£6
1131.00
0.44
59.53
686'. 00
25
-------
LAKE NAME: BEAVER "UK RES.
NUMBER: 4219
OH 23 73
07 28 73
10 05 73
TAXA
ASTERTCNFLLA
CEPATIU" HIRUNOIN«LLA
CHICP"PHYTAN FILAMENT *l
CLOS'S'IUM «l
CCELASTQUM RETtCULATUI 1
CCJCINCOISCUS
COSCINCOISCUS LACUSTRIS
CPYPTCPCNAS EROSA
CR>PTOI>CI*AS CVA-A
CYCLffTLLA 800ANKA
CYCLSTELLA STELLIGFRA
CYM8ELLA "URGIHA
CINOBRYON eAVARICU*
CINCBRYCN OIVERG6NS
OINCSRYCN SERTULA^IA
CIN4BPYON SERTULARIA
V. PP«?fUB5«IANS
EUELENA
FLAGELIAT? »i
PLASELLATE «2
fLAGELLATf «9
FRA6IL**IA
GLOEOCYJTTS PLANCTONICA
"ALLCMCNAS ALPTNA
XELCSTRA
"?LC5IPA 01STAM5
•ELCSIPA OISTANS 7
*fir
-------
LAKE NAMP: BELTZVUL6 CAM
STOPST NUMBER: 4210
NYGAARO TRCPHIC STATE INCITES
DA"11? 07 24 73 10 04 T3
MYXOPHYCEAN
CHLQRCPHYCEAN
EUGLSNCPHYTE
DIATOM
COMPOUND
o/o r
02/0 E
0/02 ?
i.oo e
05/0 E
01/0 E
01/0 £
0/02 ?
0.5* 5
04/0 E
PALMER'S ORGANIC PCLLUTICN INDICES
DATE 0? 24 73 10 04 73
GENUS
SOECIES
02
00
01
00
SPECIES OTVEPSITY AND ABUNDANCE INDICES
OA'S 07 24 73 10 04 73
AVERAGE DIVERSITY H
NUMBER CP TAXA S
NUMBER DP SAMPLES CCMPOSITED M
MAXIMUM DIVERSITY MAXH
TOTAL DIVERSITY C
TOTAL NUMBER OP INDIVIDUALS/ML N
EVENESS COMPONENT J
MEAN NUM8?R CF INDIVIDUALS/TAX A I
NUMBER/ML OP MOST ABUNDANT TAXON K
2.21
15.00
4.00
3.91
5558.15
2515.00
0.57
167.67
1115.00
1.55
11.00
3.00
3.46
2162.25
1395.00
0.45
126.82
619.00
27
-------
L»KF NA*F: ea'VVTLLE t»4"«
STPR6T NUMBER: 4229
TAXA
4STEP.ICNHLA PQ8I*3SA
CCNTINUED
CCELCSFI-Afeiu* NA«
C»LCm?NIA TSTPAPI-3I4
CPYPTOMONAS Ei"3?A
CYCLOTELLA STELLri5«H*
OIN08PYCN PAVAPICU*
C!NC8BYCN CIVB'CSNS
OINOBPYCN T48SLL»«1»E
= 12
«9
PIAGEIL4TE?
GLCfO>:>S''IS GIG4S 7
GYMNOOINIO" N6GLECTUI> 7
KELOSIP4
061CSTR4 »1
9IJUC4
07
73
10 CA
N4VICUL4
SCENEOESP
SYNFOP4
CR?
CEL
CEL
CCL
C2L
CSL
CSL
CSL
CEL
CEL
CSL
CSL
CSL
CEL
CSL
CEL
CEL
CSL
CEL
CEL
COL
CEL
CEL
ALGAL
UNITS
S TC PP.P «L
2127.01 6'8
4
3
S
6.1
!.2
1.7
9.!!
S.2
X
X
1!3
131
X
44
X
241
X
131
X
0.91 22
1 X
1144.31 1115
1 ALGAL
1 UNITS
IS tC PEP ML
I
I
j
15
1
11
1
12
1
1
I
14
13
I
I
1
1
1
|
j
1
I
1 X
1
X
1.41 20
44.31 418
X
42.9) !?8
f
1
1
1.41 20
10.0) 139
X
X
X
TOT4l
2515
139?
28
-------
LAK? NAPE:
STCRET NUMBER:
CANACOKTA
NYGAARC TPQPHTC STAT= INCICES
DATE 07 27 73 10 05 73
MYXCPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTE
DIATCM
COMPOUND
4.50 E
2.50 E
0.0? ?
I. 00 ?
9.00 E
7.00 5
3.00 E
0/10 ?
1.50 E
13.0 E
PALMER'S CBGANIC PCLLUTICN INDICES
DATE 07 21 73 10 05 n
GENUS
SPECIES
06
04
01
00
SPECIES DIVERSITY ANO ABUNCANCE INCICES
DATE 07 27 73 10 05 73
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OP SAMPLES COMPOSITED
MAXIMUM DIVERSITY PAXH
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
PEAN NUMBER CF INOIVIOUALS/TAXA
NUMBER/ML OF MOST ABUNOANT TAXON
H
s
M
;H
D
N
J
L
K
2.47
27.00
1.00
4.75
2924.43
1194*00
3.52
4?.S5
469.00
1.57
20.00
1.00
4.32
4991.33
3179.00
0.36
15e.95
2342.00
-------
LAKF N4M«: IAKF.
STCRET NUMBER: 4221
CCNHMJEC
0' 2» 73
10 05 '3
TAXA
ANABAEM PLAKCTCNICA
ANK! STPODE S"US
APM4NOCAPSA ELACHSTA
v. PLAM:TCNICA
ARTHROSPIRA GONONTIANA
CEPATIU? HIPUWIM-LLA
CHLA«YCOKONAS
CHLAPYCCWNAS GLCHOSA
CHP09COCCUS
CCCCONE1S
CCELASTRUM
COELOSPHAER1UW
COELOSPHAERIU*
C2ELOSPHAERIUM PALLlCUf ?
CCSNARIUK
C'YPTCKCNAS EROSA
CVANQPHYTAN *ILA"«««IT
ClrClCTELLA 600ANICA
CYfBEtLA
PLAGELLATE
FIAGRLATE 19
FLAGELLATES
FBAGILAOIA CRnTCNgNSIS
? 1.ACISTRIS
H«LOSIP«
fELQSTP* 12
MCPOCYS'tS INCEP*A
OOCYJftS
COCYSTIS PAOV*
CSCtlLATCKTA LI»N*TICA
OSCIILATCMA TENUTS
PHACLS ACUMIMTUS
5CENEOESMUS 8IJUCA
SPHAEKCCYSTTS ?
STAU9ASTO.UH ANftTINUM 7
STAUPA^TPUX OEJ?CTUH
S^EPHANQO! SOUS
SYNECPA
TETRAECPCN
TOTAL
FOP"
FIL "~
CEL
CEL
FIL
CSL
CEL
CEL
CEL
COL
CEL
COL
COL
COL
COL
CEL
CEL
«1L
CEL
CEL
CEL
CEL
CEL
CEL
COL
CEL
CEL
CEL
COL
CEL
CEL
«tl
PIL
CEL
COL
COL
CCL
CEL
CEL
CSL
CEL
CEL
ALOAL I ALGAL
UNITS 1 UNITS
5 tC °E« ML IS 1C °5R ML
2
3
5
»
1
1.91 22 121 6.31 215
1 X 1
1 1
1 14
1 x
C.5I 11
1
1
1
0.91 11
1 X
1
9.91 11
1 X
1 x
1 x
39.41 *49
1
1 X
1 X
1
T.JI 99
».0l *'
1 X
1
1.91 22
1
1 X
3.91 *5
0.91 U
1
0.91 11
32.01 3'9
1 x
0.91 11
1
3.81 *5
1 X
1
1
1
1 X
5
3
I
6.4
0.3
1.4
O.T
3.6
3.9
T3.7
1.8
0.7
0.3
0.3
204
11
4S
X
X
X
23
113
124
2342
ST
x
X
23
X
11
X
11
X
113* 31T9
30
-------
LAKE NA*E: HARVEY'S LAKE
STORET NUMBER: 4222
NYGAARO -RCPHIC STATE INDICES
OATE 04 12 73 07 23 73 10 02 13
MYXCPHYCEAN
CHLCROPHYCEAN
EUGLENOPHYTE
DIATOM
COMPOUND
03/0 E
01/0 E
0/04 ?
0.75 F
07/0 5
6.00 E
3.00 E
0/09 ?
0.33 E
10.0 E
5.00 £
2. CO E
0/C7 ?
0/01 ?
7.00 E
PALMER'S ORGANIC PCLLUTICN INDICES
D4 12 73 07 23 73 10 02 73
GENUS
SPECIES
00
00
01
00
00
00
SPECIES OIVERSITY AND ABUNDANCE INDICES
DATE 04 12 73 07 23 73 10 02 73
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES CCMPOSITED
MAXIMUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
MEAN NUMBER OF INOIVIOUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
S
M
MAXH
0
N
J
L
0.62
15.00
2.00
1.91
1992.60
2430.00
0.21
162.00
2. 86
la.oo
2.00
4.17
2765.62
967.00
0.59
53.72
2097.00
299.00
2.59
13.00
2.00
3.70
613.83
237.00
l$'.23
75.00
31
-------
LAK5 NAME: HABVEVS
STCRFT HUM6ER: *222
•"•AXA
ANA6AENA »1
AM8ASNA »2
ANKIS'ROOSSMUS
CCNTTNU-O
APHAN1ZOENON ?
APt-ANTZCfENCN FLCS-ACUAE
ASTFRITNELLA FORMOSA
CFKTKIC CIATQM
CEBATIUM HIRUNOIN5LLA
CHLORELLA VULGAR IS 1
CHRCCCCCCUS
fCFLOSPhAE'tUM CCNFSR'a*
CCEtaSP^AfRIU" PALLICU*
COSCIMOniSCUS
CVANQPfYTiN CQLCNV
CtANOPH>T»N MLAK«»|T
CYCLCTELLA 300ANICA
OCLCTELLA (N»
Oie'VCSPHAi-P.tUM EHREN9EPGIANUM
PUlCt-ELLUM
19
F»AGILA9IA CPOTCKENSIS
GLCECCYST!?
7
ACA»CIO«S
NAVtCULA HOIQSA 7
NITZSCMIA
OSCTUA'C'TA
04 12 »3
OT 23 T3
10 02 73
FORM
FIL
FIL
CSL
CEL
FIL
FIL
CEL
CEL
CEL
CEL
COL
CCL
COL
CEL
CEL
COL
FIL
CEL
CEL
CCL
COL
CEl
CEL
CEL
CEL
CEL
COL
CEL
CEL
COL
CEL
CEL
FIL
COL
CEl
CEL
CEL
ALGAL
UNITS
S K P?" "L
.
1
3
4
2
5
86.3
2.6
3.9
5.1
1.3
0.4
3.4
X
2097
X
63
X
21
X
198
31
10
x •
to
X
X
ALGAL ALGAL
UNIT? UNIT;
S tC PER ML S tC PEP ML
I
2
4
3
5
X 1
1.91 18
1
3.61 35
1
30.91 299
9.1
1.9
1.9
14.5
3.t>
20.0
. .-
4.1
3.6
X
X
98
X
18
18
140
35
X
193
x
88
35
X
x
4
2
3
I
10.51 25
X
5.1
10.5
21.1
31.6
10.5
10.5
12
25
X
SO
75
25
X
25
X
X
X
2430 967 237
32
-------
LAKE NAHE: INDIAN LAKE
STCeET NUMBER: 4223
NYGAARO TROPHIC STATE INDICES
DATE 0* 23 73 OT 25 73 10 04 73
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENOPHYTE
DIATOM
COMPOUND
0.50 £
0/02 0
0/01 7
1.00 E
1.50 E
0/0 0
02/0 E
0/02 ?
0.50 E
03/0 E
0.67 E
1.67 E
0/07 7
0.33 E
2.67 E
PALMER'S ORGANIC POLLUTION INDICES
DATE 04 23 73 07 25 73 10 04 73
GENUS
SPECIES
00
00
01
00
03
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE 04 23 73 07 25 73 10 04 73
AVERAGE DIVERSITY H
NUMBER CF TAXA S
NUMBER OF SAMPLES COMPOSITED M
MAXIMUM DIVERSITY MAXH
TOTAL DIVERSITY 0
TCTAL NUMBER OF INOIVICUALS/ML N
EVENESS COMPONENT J
MEAN NUMBER OF 1NOIVIOUALS/TAXA L
*fimER/Ml OF MOST ABUNDANT TAXON K
2.37
12.00
3.00
3.58
552.21
233.00
0*66
I?.42
100.00
1.32
10.00
3.00
3.32
1676.40
1270.00
0.40
12».00
949.00
1.65
18.00
3.00
4.17
3633.30
2202.00
u.40
122.33
1559.00
33
-------
NA»F.: I NO UK LAKE
STOR£T NUMBER: 4223
TAXA
ANKISTPCOFSNUS
APHANIZC«FNCN FLCS-ACUAE
CONTINUED
N CELL
CHRYSOPHYTAN COLCNY
CLCSTEPtUM
CRUC!G?NI« TET9AFEOIA
CYANOPMYTAN COCCCtO CELLED CCLTNY
CYCLOTELLA 800ANICA
CYCLSTELLA STSLLIGER*
CESMICIU«t 8AILEY1I
BAVA
-------
LAKE NAPE: LAKE NACMT
STORED NUMBER: 4224
NYGAARO TPCPHIC STATE INDICES
OATE 07 23 73 10 03 73
MYXOPHYCEAN
CHLGROPHYCEAN
EUGLENOPHYTE
0I ATOM
COMPOUND
0.50 E
2.00 E
0.20 ?
3.40 E
4.00 E
0/05 0
1.00 E
0/05 7
0.21 ?
1.60 E
PALMER'S ORGANIC POLLUTION INDICES
DATE OT 23 73 10 03 73
GENUS
SPECIES
03
02
00
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
OATE 07 23 73 10 03 73
AVERAGE DIVERSITY
NUMBER CF TAXA
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INOIVIDUALS/ML
EVENESS COMPONENT
MSAN NUMBER OP INOIVIDUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXCN
H
S
M
MAXH
0
N
J
L
K
2.71
22.00
I. 00
*.46
11062.22
4032.00
0.61
135.55
-1784.00
2.43
36.00
1.00
5.1*
3810.24
1569.00
0.4T
43.56-
-851.00
35
-------
LAKF NAME: LAKE NAOMI
NUMBER! 42?*
TA»A
ANKISTROCESMUS FALCATUS
CPNTINU=0
0» 23 73
10 03 T3
ASTEP1CNELLA FORdGSA
ASTERIONELLA PQ«P>rSA 7
CHLAMVOOMONAS
CHLOROPHYTAH CELL
CHBVSOPMYTAN COCCOIO CELL
CHRYSOPMYTIN FLACELLATE «
CRUCIGFN1A CUACRATA
CRUCIGENIA TETRAPECIA
CPYFTCMCNAS E»0«*
CRYFTOMONAS OVATA
CYANQPMYTAN FILAMENT
CYMBELLA GRACIL1S
OlCTYOSPt-ASRIUM PULChELLUH
EUNCTIA PECTINALIS
V. XI NOB 7
EUNOTIA TSNELLA
"LAGELLATE fl
FLAG a LATE 12
FLAGELLATE 13
FLAGELLATES
FPANCEIA
FPUSTULIA
GLFKQOINtUf ARMATU"
»ALLC"CNAS
M«LOSIRA 01«TANS
MELOSI9A GRANUIATA
fELOSIBA ITALIC*
«LQ!IR« ITAIICA 7
MELCSIOA VARIANS
NAVICULA 7
OOCYST1S
PE'tOTMIUM HTSCCNSINENSE
PT^NULIPtA ACUHTNATA
V. SmAUSKU
PINNULA«!A BICEPS
FUNULARIA FCWICS
SCENEDEJMUJ
SCEf'fOESKUS ABUNCANS
SCE^E?'Sl>tiS 8TJUGA
S'AURASTRUM
S'AURASTRUf O'MEARII
STAURGNEI!
SURTRELLA LINEAR!? 7
SURIRELLA CVALIS
SYKECRA
SYNECPA RACIAMS 7
TA8ELLARIA FENESTRATA
TABELLABIA FLOCCULOSA
TBACKELCMCNAS HISPICA
V. CtJRCNATA
TOTAL
FCRM
CEL
CEL
CEL
CEL
CEL
CF.L
CEL
CEL
CEL
CEL
COL
CEL
CEL
FIL
CEL
ecu.
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL •
CEL
CEL
CEL
CIL
CBL
CEL
CEL
CEL
C«L
CEL
CEL
cm.
CCL
COL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
ALGAL
UNITS
S «C PF.9 ML
5
3
2
*
1
1
5.51 223
T.&l 312
2.T
0.3
I. I
1.6
1.1
0.3
13.7
14.2
4.4
I. I
Ul
0.5
43.7
0.5
X
112
22
43
67
43
22
X
X
538
'
380
178
45
X
45
22
X
17J4
X
22
1
ALGAL
UNITS
S K PER *L
I
2
3
3
4
1. 01 16
1.01 16
1
2.11 33
1
4. 1 1 45
1.0
8.4
6.2
34.3
8.4
1.0
1.0
9.4
1.0
1.0
X
16
131
X
X
X
X
98
X
351
131
X
16
X
16
X
X
147
16
X
X
X
X
X
X
X
X
X
16
X
X
X
4082 1568
36
-------
LAKE NAME: LAKE CNTELAUNEE
STQRET NUMBER: 4225
NYGAARC TROPHIC STATE INDICES
DATE 0* 13 73 07 24 73 10 03 73
MYXQPHYCEAN
CHLCRCPHYCEAN
EUGLENCPHYTE
DIATOM
COMPOUND
0/0 0
01/0 E
0/01 ?
0.27 ?
05/0 5
1.00 E
5.33 E
0/19 ?
0.33 F.
«».67 5
2.50 E
a.so E
0.10 ?
l.CO E
7.00 E
PALMER'S ORGANIC POLLUTION INDICES
OATC 04 13 73 07 24 '3 10 03 73
GENUS
SPECIES
01
00
04
04
01
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE 04 13 73 07 24 73 10 03 *3
AVERAGE DIVERSITY
NUMBER OF TAX A
NUMBER OF SAMPLES COMPOSITED
MAXIMUM DIVERSITY *AXH
TOTAL DIVERSITY
TCTAL NUMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
MEAN NUMBER CF INOIVIOUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
s
M
;H
c
N
J
L
K
1.77
23.00
?.oo
4.52
179 '+.79
101*. 00
0.29
44.09
630.00
3.23
29.00
2. 00
4.86
2 20*. 44
671.00
0.67
23.21
131.00
1.40
2*. 00
2.00
4.46
11419.40
8156.00
0.31
370.73
4597.00
37
-------
LAKE NAfE: LAKE CNTELAUNE5
STCPET NU»8ER» 4225
TAXA
*CI-NANT»-ES LANCECLATA
V. DUB 1 4
ANABAF.MA
APHANIZCCENCN 7
ASTERICNELLA FQ«»>GUST«T«
TABfLLARIA FL3CCUOS*
TET1iAIC•C^
TREUBAPIA THIAPOCNOiCULATA 7
TC'AL
FORM
:EL
FIL
FIL
CEL
CEL
FIL
CEL
COL
COL
CCL
CEL
CEL
CEL
CCL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEl
CEL
CBL
CEL
COL
CEL
cot
CEL
CEl
CEl
CEL
CEL
COL
COL
CCL
CEL
CSL
cn
CEL
CM.
CEL
COL
COL
CCL
CEL
CEL
CTI
COL
CCL
COL
CCL
CCL
CCL
CEl
. CSL
CEl
CEl
CEl
CEl
CEL
ALGAL
UMT;
s tc PER ML
*
2
3
J
I
IC.i
6.6
6.6
2.7
2.7
1.3
t.3
'..3
67.1
X
107
X
67
X
X
X
X
X
X
X
67
27
X
X
27
X
13
13
13
680
X
X
ALGAL
UMTS
S K P?a •«.
*
2
1
3
5.3
11.0
2.4
3.7
19.5
2.*
7.3
11.0
13.5
12.2
1.2
4.1
X
X
44
U
It
X
25
X
X
X
X
X
131
X
I*
*5
X
7»
x
*
flOCSl
X
X
32
)
X
»1
X
X
ALC-AL
UNITS
S tC °fB PL
5
2
»
1
3
0.4
C.2
1.1
0.1
0.1
C.I
37.8
1.2
5t.*
0.1
1.0
0.1
1.2
30
2C
91
X
10
X
10
X
X
1C
3oe;
X
101
459*
»
10
X
ai
10
101
X
X
673
8156
38
-------
LAKE NAPE: PINCHCT LAKE
NUMBER: 4226
NYGAARC TRCPhIC STATE TNCICSS
DATE 0* 13 73 0? 24 73 10 02 73
PYXCPHYCEAN
CHLQROPHYC5AN
EUGLENCPHYTE
OIATCM
COMPOUND
0/0 C
02/0 E
0/02 7
0.33 E
05/0 E
1.40 =
0.60 ?
0.40 E
1.00 E
3.40 E
0.29 ?
2.00 E
0.12 7
0.62 E
3.29 E
PALMER'S CRGANIC POLLUT1CN IN01CES
OATE 04 13 73 07 24 73 10 02 73
GENUS
SPEC15S
05
00
13
00
00
00
SPECIES DIVERSITY ANC A9UNCANCE INDICES
OATE
04 13 73 07 24 73 10 02 73
AVERAGE DIVERSITY
NUMBER OF TAXA
NUMBER OF SAMPLES CC1POSITEO
MAXIMUM DIVERSITY
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
MEAN NUMBER CF INCIVIDUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXON
H
S
M
MAXH
0
N
J
L
K
2.66
20.00
2.00
4.32
21636.44
9134.00
0.62
406.70
235*. 00
1.99
28.00
2.00
4.81
10375.86
5214.00
0.41
186.21
3551.00
2.60
43.00
2.00
5.43
4401.80
1693.00
0.48
35.37
565.00
39
-------
UK= NAPE: PINCHCT L»KE
: 4226
TAXA
ANABAENA PLAKCTONICA
ANKISTROOESMUS
AQTHPOSPIRA
ASTERIONELLA F3PHOSA
CI-LOPOPhYT«M CELL
CLCSTERIU"
CCCCOIC CELL
CCELASTRUM RETICULATUM
CCELASTHU* SBMAEPtCUf
CnELOSPHAERlUM NAEGELIANUM
CCNTINUEC
0* 13 73
07 2* 73
10 C2 '3
<2
CCSMAR1UW 13
CCSfARtUF 6IPUNCTATU*
C°UCIGENIA APICULATA ?
CRYPTOHCNAS
CRYPTOFCMS QVATA
CYANOPHYTAN F!LA«ENT
CYCLOTHLA STELLIGERA
CYP9ELLA
CISTULA
6AVARICUW
OINCBPYCN 3IVE»GENS
fUASTBUM
EUGLENA n
EUGLENA «2
EUGLEN*
EUNCTIA
PL«eaLATE *i
FLAGELLATE n
^LACaLATE ««
FLAGRLATES
FPAGILAP.IA
MAGILAUTA
GLENCOtNTUK QCULATUN
GCCPHOKE^A 7
V. COPCNATA
CCWPHOSPHA6P1A LACUSTRIS
- ». CONCACTA-7 --
MELOSIPA GPANULATA
V. ANGLSTISSIHA
MELOSIPt ITALIC*
»FLOSIP» fALICA ?
f*LCS!P« VAPIANS
NICPOCVJTTS AenuGtMOSA
NAVICULA
NEPHROCYTIU"
NITZSCHIA
CCCYS-'TS
QOCYJTIS PAPVA
CSCILLATORTA 41
CSCILLATCBU TEHUtS
PEOUSTRLf DUPLEX
V. ?
PEOIASTP.UP SIMPLEX
V. OUOOENAP.IUN
PENNATE CIATOM
PHACLS H6LIKOI06S
RMI20SOL?NIA LONGISETA
SCENEOESfUS 8TJUC*
SCEKEDESmjS 8TJUCA
V. Al-f?PNANS
SCHHOEDE*TA
SPHAEPOCYS1TS 1
U^ II
STE»HANf!OT SCUS
II
GPACILE
TPACHELCWKAS HI5PICA
TBACHELCMCNAS VOLVCCTNA
TO'AL
prR«
FIL
CEL
FIL
CEL
CEL
CSL
CSL
CCL
CCL
COL
CEL
CEL
CSL
CEL
CCL
CEL
CEL
ML
CEL
CEL
CCL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CCl
CEL
CEL
CE.I
C?L
CfL
CEL
CEL
CSL
_CEL
CCL '"
CEL
CfL
CSL
CEL
CCL
CEL
CSL
CSL
CSL
CEL
FIL
FIL
COL
CEL
CEL
CEL
CCL
CCl
CEL
CCL
COL
CEL
CEL
CEL
CEL
CEL
CCL
CEL
CEL
ALGAL
UMTS
S tC Pf« PL
2
1
4
3
9
1
I. 01 79
6.8
0.3
31.1
11. 0
26.0
7.1
4.1
0.7
0.3
0.7
0.3
4.1
1.3
X
111
26
X
2912
998
2113
507
"x"
37C
X
•3
X
26
13
2*
37C
106
X
ALGAL
UNITS
S 1C PER "L
1 1. 01 11
1 1
1169.11 3111
3
4
2
4.4
0.1
0.1
o.;
0.1
2.0
1.0
*.9
2.5
7.3
2.5
J.5
230
26
X
26
26
X
26
102
11
X
25!
128
X
X
383
X
128
X
X
26
X
X
X
0.11 26
1
O.SI 26
111 2.91 113
AL5AL
UN!TS
S tC P£° »L
1133.41 «65
1
4
2
3
1 x
1
1
2.21 37
2.91 4«
1.41 24
2.91 4?
4.4
2.2
2.9
32.6
j.7
12.3
0.7
3.7
0.7
»
X
X
X
X
74
37
X
X
X
*
49
•!2
X
I
X
12
X
X
X
X
Jl
X
209
y
X
X
x
X
12
X
12
X
%
X
12
X
8134
1214
1693
40
-------
LAKE NAPE: POCONC LAKE
STCRET NUMBER: 4227
NYGAARO TROPHIC STATE INDICES
DATE 04 17 73 0* 23 73 10 03 73
MYXOPHYCEAN
CHLOROPHYCEAN
EAJGLENOPHYTS
DIATOM
COPPCUNC
0/0 0
02/0 E
0.50 5
0.17 ?
05/0 E
0.33 ?
4.33 6
3.29 5
0.37 5
).OQ E
1.00 E
4.00 E
0.40 E
0.30 ?
10.0 E
PALME?'S ORGANIC POLLUTION INDICES
DATE 04 17 73 07 23 73 10 03 *3
GENUS
SPECIES
00
00
07
00
06
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
CA'E 04 17 73 07 23 73 10 03 73
AVERAGE DIVERSITY
NUMBER Of TAXA
NUMBER OF SAMPLES COMPQS1TEC
MAXIMUM DIVERSITY MAXH
TOTAL DIVERSITY
TOTAL NUMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
MEAN NUMBER CF INDIVIDUALS/TAXA
NUMBER/ML OF MOST ABUNDANT TAXQN
H
S
H
;H
c
N
J
L
K
2.16
21.00
?-00
4.39
132*. 24
6U.OO
0.49
29.24
247.00
3.69
54.00
2.00
5.73
7450.11
2019.00
0.64
39.09
301.00
2.92
44.00
I. 00
5.46
3559.84
1262.00
0.52
28.63
469.00
41
-------
LAKE MAKE: PCCONC LAKE
STORET NUMBER: 422?
TAXA
AChNANTHES LANCECLATA
V. DUE! A
ANKISTR<30ESMUS PALCATUS
ARTHPCCESfLS
ASTERICNELLA
ASTSBICNELLA
V. CRACILLIM
CHLOROPHYTAN CELL
CHLOROPHYTAN
CHRYSOCCNAC C1?LL
CLCSTER1UN
COCCCNEIS PLACENTULA
V. SUGLYPTA
CCSMAR1UM ?
C9UCIGEN1A TSTBAPSCtA
CPYPTCHCNAS ERQSA
CYCLOTELLA
CYCLOTELLA
CYCLC"ELLA STELLI5«RA
CYKSRLA »1
CYCBELLA «2
DACTYL OCCCCOPSTS ACICULARIS
CIATCHA
CCNTINUSO
CICTYOSPHAERIUM EfcRENBERGIANU*
CINCBRYCN SERTULARU
EUOO'INA
EUGL EN A
EUCLENA GR1CTLIS
EUNQTIA
EUNOTIA
FLAGEILAT* »\
FLAGELLATES
FR»SILAB!A
MAGtLARTA
*t
FRUSTULIA 12
GCfPHTNEMA
GY^NCOINIUN MOINATU"
LYNGBVA
"ELOSIRA «3
ANGUSTISS1MA
fALTCA
VARIANS
fCUGEOTtA
NAVICULA
NAVICULA *1
NAVICULA *2
NAVICULA *3
NAVICULA *4
KAVICULA L»ruS'Rt
NITZSChIA
II
v
PENNATE
PENNATE
OSCILLATCRIA
P*CIASTHUH CUPLEX
V. 1
*i
t;
«3
tSCQNS(>tCuit»
RE8CMELLA ?
PHACL'S
PfACUS »l
PMACUS «2
PHACUS HELIK01DES
PINNULARIA
RHtZCSCLENIA
PHIZOSOLENIA 7
!CENFDE«»L'S
5CENEOESMUS fl
SCENFCESMUS ASUNCANS
o* IT n
23 T3
10 03 73
PORN
CEL
CEL
CEU
CEL
CSL
CSL
PIL
CEL
CEL
CEL
CEL
COL
CEL
CEL
CEL
C8L
CEL
CEL
CEL
CEL
COL
CCL
CEL
CCL
CSL
CEL
CSL
CIL
CEL
CEL
CSL
TEL
CSL
CSL
CEL
CEL
. CEL.
CEL
ML
C«l
CSL
CEL
CEL
CEL
ML
CSL
CEL
CEL
CEL
CSL
CEL
CEL
CEL
CSL
ML
CCL
COL
CCL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CSL
CEL
CEL
COL
COL
COL
ALGAL
UMTS
S 1C PER »L
1
1
2
3
4
3.4
40.2
1.9
36.4
1.9
1
1.3
1.9
....
21
X
X
X
2*7
11
226
X
11
-
X
u
X
X
11
X
ALGAL
UNITS
S tC RER ML
1
2
5
_
1
|
1
a.?l »
•J.'l 1!
1
13.41 271
0.7| I!
'..11 22
1 X
1
1
1
t X
0.31 T
t'.,4l 294
0.7 1 15
0.31 T
0.3
0.3
10.9
1.9
7.4
3.4
14.9
3.3
O.T
3.4
1.1
0.3
X
X
X
T
X
X
X
7
219
X
3!
-. _
X
ISC
i3
301
X
X
X
X
7
X
X
X
15
68
22
X
X
X
7
X
2.21 43
ALCAL
UMTS 1
S tC PER »L
!
3
4
2
1
1
1 »
2.91 3t
1 »
1.4
1.4
2.9
2.9
2S.9
1.4
4.3
10.0
37.2
1.4
2.9
U4
18
X
19
36
36
X
X
X
X
X
X
32 5
X
X
13
X
X
54
126
46?
18
X
36
X
X
X
>
«
X
is
1.41 19
2.91 36
42
-------
LAKE NAPE: erC^NC IAK5
STPRET NU18ER: *227
TAXA
~5C£NSffE"5T»lS
06NTICULATUS
OENTICUl»'U$
V. UNglRIS
SCENE3ESMUS IN'ERHEO IUJ
CCNTINUEC
0* 17 73
07 23 '3
10 03 T3
ST»URON«IS
SYNE OR*
SYNECRA
TABELL»»!A
TA6ELL49IA FLOCCULCSA
TETRACCPCN
TETRAEOPCK
TETPAFOWN T
TETHASTSUM GLABRUM
"ACHFIOTNAS VCLVCCINA
TOTAL
CPB»
COL
COL
COL
CCL
COL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
CEL
C3L
CEL
<:EL
1 ALGAL 1 ALG»L 1 ALGAL
1 UNITS 1 L'NITS I UNITS 1
IS tC RFR ML IS tC PER CL IS tC P?R fl 1
5
1.9
9.9
u a
X
a
X
54
a
X
4
1
0.7
0.3
13.0
0.7
15
x
1
X
263
15
X
X
X
5.6) 113
X
X
X
X
X
X
X
X
>
614 2019 1262
43
-------
LAKE NAME: STUlhATER LAKE
STQRET NUMBER: 4228
NYGAA9C TROPHIC STATE INDICES
OATE 07 23 73 10 03 73
MYXOPHYCEAM
CHLOROPHYCEAN
f-UGLF.NOPHYTE
OTATQM
CQMPCUNO
03/0 E
07/0 E
0.20 ?
0.33 E
13/0 "•
0/03 0
2.67 E
0.12 ?
0.25 ?
3.6» E
PALMER'S ORGANIC POLLUTION INDICES
OATE 07 23 73 10 0.3 11
GENUS
SPECIES
02
00
04
02
SPECIES DIVERSITY ANO ABUNOAN'c INDICES
CATS 07 23 73 10 03 73
AVERAGE OIV5BSTTY H
NUMBER OP TAX A S
NUMBER OF SAMPLES CCMPOSITEO M
MAXIMUM DIVERSITY MAXH
TOTAL DIVERSITY 0
TOTAL NUMBER OF INDIVIDUALS/ML N
EVENESS COMPONENT J
MEAN NUMBER OF INOIVIOUALS/TAXA L
NUMBER/ML OF MOST-ABUNDANT TAXON K
2.15
29. 00
1.00
4.66
1563.C5
727.00
0.44
25.07
391.00
0.69
25.00
1.00
4.64
3986.13
5777.00
0.15
231.08
5236.00
44
-------
LAKE NAME: STRICTER LAKE
JTCRET NUMBER: 4223
CONTINUED
0' 23 73
10 03 '3
ANKISTBODESMUS
ASTEB!CNELLA FOBPOSA
BOmOCCCCUS BRAUNII
CKAWYOCWNAS PSLSOOPERTYI ?
CHLORSLLA VULGAR IS
CM.CROPMYTAN COCCOIC CELL
CCSMASIUM EXCAVATUN
CPUCIGEMA TETRAMCIA
CRYPTC»CNAS OVATA
CYANCPMYTAN COCCOIC C5LLEC CCL3NY
CYANCPHYTAN COCCCIC CELLEO CCLONY
OINCBPYON
DINC8RYCN CANPANULOSTIPITUM
EUGLENA
EUGLENA ELCNGATA
EUNQTIA
FLAG a LITE n
FLAGELLATE tz
FLASELLATE »3
'LAGELLAT; n
6LENOCINIUM «l
GLCECCYSTIS
NALLCMCNAS 7
"ELOSIFA GPiNULATA
(•ELOSIBA yALICA
COCYSTIS
PSCIASTHUH TERRAS
V. TftACCCN
PEPIOINIU" I*ONS»ICUUC
P»NNUL*»IA 'OPTA ?
ROWER I A GRtCUtS 7
SCENEOESMJS it
BIJU6A
QUAORICAUCIA
SCKP.CECEP.tA SET1GER*
STJUR4JTRU" 12
STAURC»E!S PMO?MCE*TEPCN
STEPHANOOI SCUS
SUPIR'LLA II
-------
LAKE NAME: LAKE WALLENPAUPACK
S-CPET NUMBER: 4229
NYGAARC TPCPHIC STATE INCICES
DATE 04 12 73 07 23 73 10 03 73
MYXOPHYCEAN
CHLCROPHYCEAN
EUGLENG«>HYTE
DIATOM
CCMPCUNO
02/0 E
01/0 E
0.33 E
0.14 ?
05/0 E
6.00 S
UGO E
0/07 ?
0.50 E
9.00 E
1.33 5
0,33 7
(J.2C 7
0.33 S
2.47 E
PALMER'S ORGANIC PCLLUTICN INDICES
DATE 04 12 73 07 23 73 10 03 73
GENUS
SPECIES
CO
00
00
00
01
00
SPECIES OIVERSITY ANO ABUNDANCE INCICES
CAT? 04 12 73 07 23 73 10 03 73
AVERAGE OIVERSITY
NUMBER CF TAXA
NUMBER OF SAMPLES CCMPOSITEC
MAXIMUM OIVERSITY MAXH
TOTAL DIVERSITY
TOTAL NCMBER OF INDIVIDUALS/ML
EVENESS COMPONENT
MEAN NUMBER CF INOIVIOUALS/TAXA
NUMBER/ML OP MOST ABUNDANT
H
s
M
:H
0
N
J
L
K
1.27
23.00
4.00
*.52
3923.03
3039.00
0.29
134.30
2447.00
1.90
14.00
4.00
?.8l
3767.70
1993.00
C.SO
141.64
1250.00
2.98
2C.OO
•».CO
4.32
2199.24
733.00
0.69
36.90
174.00
46
-------
LAKE NAMF.: LAKE tiALLENPAUPACK
SECRET NUMBER: 4229
TAXA
CCNT!^UED
0* 12 73
07 23 73
10 03 73
ACA8AEKA «2
ANA8AENA PLANCTONIC1
ANABAEKOPSIS
A*!KISTPCOFSHJS FALCATUS
APHANUO-EHO FLCS-AOJAS
APHANOTt-ECE N10ULANS
ASTERICNELLA FORMOSA
CHLWCCCCALEAN
CHLOPQPHYTAK CELL
CHFCCCCCCUS
CHPYSOPHYTAN BL»
COELCSPHAF.BIUM NAEGELIANUM
COELOSPHABOlgM PALLIOUP 1
COSCINOOISCUS
CBVPTCMCK'AS EPOS A
DINCSRVON MVAPTCUM
CINCBPVCN SSPTULAXIA
EUCC»!NA ?L=GANS
EUGLENA GR4CILI? ?
'LASELLATE »9
FLAGELLATES
FRAGILARIA C'OTQN^HS IS
ALBULUN i
GYMNC^TNIUM NBGLECTUM
LEPQCINCLIS FUSIFORM IS
PALLCPCNAS 7
MEICSIP* TTALICA ?
KAVICULA
PENNATB DIATOM
PEP! 01 MUM
SCENEDESHUS ABUNOANS
STAUP.ASTP.UC
STAURASTPUt" LEPTCCLAOUf
STfPf-ANOOISCUS OUBIUS
SUPI95LLA
SYNE OP A
SYNUBA
TA6ELLARIA FENfSTRATA
XANTHIDIUM SU8HA5TIFEPUM
TCTAL
B09.M
CEL
FIL
FIL
FIL
FIL
CEL
FIL
FIL
CEL
CEL
CSL
CCL
CSL
CCL
CEL
CCL
CCL
CEL
;EL
CEL
CEL
CEL
CEL
CEL
COL
CSL
CEL
CEL
CEL
CEL
CEL
CSI
CEL
CEL
TEL
CEL
CEL
CEL
CEL
CEL
CCL
CEL
CEL
CEL
CSI
CEL
CEL
CEL
CEL
ALGAL
UNITS
5 1C PES *L
1
*
3
2
3
0.3
T9.2
3.7
!.9
!.3
2.9
0.3
3.9
1.1
X
2;
244 T
X
X
115
X
X
191
X
X
155
91
8
U
X
33
X
X
'
X
X
X
ALGAL
UNITS
s xc PEP ML
1 1
4| 4.11 «2
2
1
5
1
1
l.»l 27
12.4
1.4
1.4
63.0
1.4
2.T
1.4
X
24S
27
X
27
.
1250
X
27
5*
2T
X
0.31 S 13110.91 217
1 III
ALGAL
UNITS
S »C PER ML
1
3
5
4
2
23.6
9.8
9.3
1.4
19. 5
16.7
1.4
6.9
1.4
4.2
t
174
T2
72
X
X
»
10
144
123
10
X
X
51
X
10
t
31
5.61 41
1 X
3089
19S3
733
47
-------
LAKE NAPE: KINZUA DAM
STQRET NUMBER: 3641
NYGAARO TRCPHIC STATE INCICES
DATE OT 27 73 1C 05 73
MYXOPHYCEAN
CHLOROPHYCEAN
EUGLENCPHYTE
DIATOM
COMPOUND
05/C 5
02/0 ?
0.14 7
0.17 1
10/0 E
02/0
01/0
0.67
0.25
07/0
PALMER'S ORGANIC PCLLUTIGN INDICES
DATE 07 27 73 10 05 73
GENUS
SPECIES
09
03
00
00
SPECIES DIVERSITY AND ABUNDANCE INDICES
DATE 07 27 73 10 05 73
AVERAGE DIVERSITY H
NUMBER OP TAXA S
NUMBER OF SAMPLES CCMPOSITED M
MAXIMUM DIVERSITY MAXH
TOTAL DIVERSITY o
TOTAL NUMBER OF INDIVIDUALS/ML N
EVENESS COMPONENT J
MEAN NUMBER OF INDIVIDUALS/TAX* L
NUWBER/ML OF MOST ABUNDANT TAXQN K
3.72
29.00
0.00
4.86
7700.40
2070.00
0. 7*
71.38
572.00
2.21
25.00
0.00
4.64
2291.77
1037.00
0.48
41.48
429.00
48
-------
LAKE NAME: KINZUA
STPET MJH8ER: 36«t
CONTINUEO
ANABAENA
AFH«NIZCfeNON FLOS-AQUAE
ASTERICNFLLA F
-------
PART II: DISTRIBUTION OF ALGAE IN YORK COUNTY
by
Robert L. Frock
113 Fulton Street
Hanover, Pennsylvania
17331
CONTENTS
Introduction 51
Description of Study Area 51
Materials and Methods 53
Results r.. rr. 55
Literature Cited 56
Bibliography , 57
Appendix: Species List of the Freshwater Algae
in York County, Pennsylvania 58
50
-------
INTRODUCTION
Previous surveys dealing with Pennsylvania algae have been sketchy
and often included taxa that have since undergone revision in nomenclature.
Seldom were taxa identified to species. Most algal surveys were in connec-
tion with specific reservoir, water supply facility, or pollution studies.
Francis Wolie (1887, 1892) made the most extensive survey of Pennsylvania
algae, especially for the desmids. This survey reports on 152 genera and
502 species of fresh-water algae found within a 16-kilometer (km) radius
of Hanover, York County Pennsylvania. Included are 16 genera and 159
species of desmids. I am greatly indebted to Drs. Gerald W. Prescott,
Hannah T. Croaadale, L. A. Whitford, and Mr. William D. Taylor, for their
most generous assistance with identifications and manuscript suggestions.
DESCRIPTION OF STUDY AREA
Emphasis in this study was placed on Lake Marburg and Glatco Lodge
(Haldeman's Pond) from which the majority of species was found. All of
the habitats studied are presented in Table 1.
Lake Marburg is located in Heidelberg, Manheim, and West Manheim Town-
ships of York County, Pennsylvania, about 6.4 km east of Hanover (Selcher,
1972). This reservoir, impounded in 1967, is owned by the Pennsylvania
Department of Environmental Resources, and is crossed by Route 216.
Lake Marburg has a surface area of 516 hectares and a drainage area
of 5808 hectares (Selcher, 1972). The lake has a maximum depth of 32
meters (m) and an average depth of 12.2 m. There are about 45 km of shore-
line. Nature of the bottom is organic silt and mud. The surrounding terrain
is hilly with pastures and hardwood trees. The shoreline profile is usually
steep.
Because of mixing prompted by rapid draw-off at a depth of 21 m
by the P. H. Glatfelter Paper Company of Spring Grove, Pennsylvania, the
dissolved oxygen content of the lake is sufficiently high to accommodate
the needs of salmonid fish down to 21 m at the dam (Selcher, 1972). The
region of the lake unaffected by the maximum mixing efforts of the drawoff
shows a more typical summer dissolved oxygen pattern, with concentrations
too low to support trout below depths of 4.6 to 6 m. The normal range of
pH is from 6.0 to 9.0 (Selcher, 1972). At depths from 0.3 to 21 m the
temperature decreased from 23.5° C to 7.0° C. The alkalinity (as CaC03),
ranges from 36 to 39 milligrams/liter (mg/liter). The dissolved oxygen
ranges from 8.7 to 3.6 ppm.
51
-------
Extensive limnological data for Glatco Lodge (Haldeman's Fond), the
major source of algal samples, are not available. About 100 years ago it
was an iron ore quarry and was subsequently abandoned due to low grade ore
and the exposure of springs. The average range of pH is from 6.0 to 8.0,
using the paper strip testing method. Large quantities of Ferric oxides
appear to be present. The pond ia surrounded by pine, oak, and maple trees,
The aquatic shoreline vegetation consists mostly of Elodea, Lemna, and
Sphagnum. The pond is owned by the P. H. Glatfalter Paper Company of
Spring Grove, Pennsylvania. It is well stocked with trout by the
Pennsylvania Fish Commission and by local Rod and Gun Clubs. Table 2
summarizes the limnological data available for the Lake Marburg and
Glatco Lodge impoundment.
TABLE 1. HABITATS SAMPLED FOR FRESHWATER ALGAE IN
YORK COUNTY, PENNSYLVANIA
Glatco Lodge (Haldeman's Pond) (GL)
Lake Marburg (Codorus Creek State
Park) (LM)
Reek's farm pond (RF)
Budd's farm pond (BF)
Storm drain ditch (SD)
Sheppard Myers Reservoir (SM)
Hanover High School
Nature Study Pond (EH)
South Western Intermediate
School Nature Study pond (SW)
Detailed description in text
Detailed description in text
A small, privately owned pond,
fed by springs and run-off
A small, privately owned pond,
fed by springs and run-off
A small stream east of Hanover,
about 10 centimeters (cm) deep,
1 m wide, and slow flowing all year,
A large impoundment about eight
kilometers southeast of Hanover,
which is the city's main water
supply.
A small pond
A small pond
52
-------
MATERIALS AND METHODS
Collections were made at least once per month during the years 1971
through 1975. Six 500 ml wide mouth jars with screw lids were used for
each sample. Shallow water vegetation such as Elodea and Sphagnum, and
allocthonous material, e.g. pine needles, maple and oak leaves, were placed
in a jar with water about one inch from the top. The lid was screwed on
and the jar vigorously shaken. The contents were then squeezed out into
the jar. This was repeated several times for each jar. Finally, a small
amount of vegetation was placed in the jar to complete the collection.
This method proved satisfactory in obtaining a good variety of desmids and
epiphitic forms.
Samples were taken to the lab as soon as possible where they were ex-
amined with a. binocular brightfield microscope (Olynpus model KEG) . Most
specimens were examined live using a flat-bottomed well slide (20 x 28iam)
with a coverglass. Other examinations were made of materials preserved
in Transeau's 6-3-1. A portion of each sample was preserved as part of
the author's permanent collection. Permanent slide mounts were made only
for the examination of diatoms. An extensive illustrated diatom species
list will be published at a later date.
TABLE 2. PHYSICAL CHARACTERISTICS OF LAKE MARBURG AND
GLATCO LODGE IMPOUNDMENT
Lake Marburg Glatco Lodge
Surface area (hectares)
Drainage area (hectares)
Maximum depth (m)
Average depth (m)
Length of shore line (k)
516.0 9.0
5808.0
32.Q
109 ____ _
l£.^. "" "
45.0 1.1
pH (standard Units) 6.0-9.0 6.0-8.0
Dissolved oxygen (ppm) 3.6-8.7 ——•——
Temperature (°C) 7.0-23.5
Alkalinity (as CaC03) 46.0-39
53
-------
A freehand drawing was made of each species on a 5 x 8 index card.
Additional information on the card included the name of the organism, dimen-
sions, habitat, and date. This material was used by Drs. G. W. Prescott,
H. Croasdale, and L. A. Whitford for species verification.
The primary references used to make identifications included: Gojdies
(1953), Irenee-Marie (1939), Prescott (1962, 1970), Prescott et al. (1972,
1975), West and West (1904-1923), and Whltford and Schumacher (1969).
The following notations as to the relative abundance of species refer
only to my collections and are not intended to be generalized for other
Pennsylvania areas.
Common: Abundant in all habitats.
Fairly common: Not abundant; restricted to certain habitats.
Uncommon: Found only a few times in a specific habitat.
Rare: Found only once from one site.
54
-------
RESULTS
A species list with habitat and abundance records is presented in the
appendix. Reported are 502 species of 152 genera. Table 3 summarizes the
number of genera and species by phylum. There are 293 new species for
Pennsylvania including, to the best of my knowledge, 3 species new for North
America. The species new for North America are Euglena proxima var.
amphoraeformis Szabados, Trachelomonas conica Playf., and Menoidium
bibacillatum (author?). These species were rare or uncommon in the study
samples. Another species, Tetrastrum tetracanthum G.S.W. Brunnthaler, is rare
in the United States, having been found only at one station in Alabama. In
this survey it was found several times in Reek's farm pond.
TABLE 3. NUMBER OF GENERA AND SPECIES BY PHYLUM
Genera Species
Chlorophyta
Cyanophyta
Chrysophyta
Euglenophyta
Cryptophyta
Pyrrhophyta
Chloromonadophyta
91
24
17
10
5
5
1
152
335
67
31
55
5
8
1
502
55
-------
LITERATURE CITED
Gojdies, M. 1953. The genus Euglena. Univ. Wisconsin Press. 268 pp.
Irenee-Marie, F. 1939. Flore Desnidiale de la region de Montreal. Laprairie.
547 pp. Pis. 69.
Preacott, 6. W. 1962. Algae of the western Great Lakes area. Win. C. Brown Co.
977 pp. Pis. 1-136.
Prescott, G. W. 1970. How to know the freshwater algae. Wm. C. Brown Co.
348 pp. Figs. 533.
Prescott, G. W., H. T. Croasdale, and W. C. Vinyard. 1972. Desmidiales.
Part 1. Saccodermae, Mesotaeniaceae. North American Flora. N. Y. Bot.
Garden. II, 6:1-84. Pis. 1-8.
Prescott, G. W., H. T. Croasdale, and W. C. Vinyard. 1975. A synopsis of
North American desmids. Part II. Deamidiaceae: Placodermae, Section I,
Univ. of Nebraska Press. 275 pp. Pis. 9-57.
Selcher, J. 1972. Lake Marburg. Pennsylvania Angler. Nov. 1972. pp. 13-15.
Smith, G. M. 1950. The fresh-water algae of the United States. 2nd. ed.
McGraw-Hill. 719 pp.
Taft, C. E. and C. W. Taft. 1971. The algae of western Lake Erie.
Ohio Biol. Surv., 4(1):1-189. Figs. 1-654.
Tiffany, L. H. and M. E. Britton. 1971. The algae of Illinois. Hafner
Publishing Company, (fasc. of the 1952 ed.) 407 pp. Pis. 1-108.
West, W. and G. S. West. 1904-1923. A monograph of the British Desmidiaceae.
Vols. I - IV; V(1924, with Nellie Carter), Ray Soc. London.
Whitford, L. A. and G. J. Schumacher. 1969. A manual of the freshwater algae
in North Carolina. North Carolina Agriculture Experimental Station.
Tech. Bull. 118:1-313. Pis. 1-71.
Wolle, F. 1887. Freshwater algae of the United States. Bethlehem, Pennsylvania.
364 pp.
Wolle, F. 1892. Desmids of the United States and a list of American Pediaatrum.
Bethlehem, Pennsylvania. 182 pp.
56
-------
BIBLIOGRAPHY
Buck, W. S. 1935. The common algae of Berks County, Pennsylvania. Proc.
Penna. Acad. Scl. 9:100-107.
Buck, W. S. 1938. A key to the algae of Berks County. Proc. Penna. Acad.
Sci. 12:84-87.
Coutant, C. C. 1963. Stream plankton above and below Green Lane Reservoir.
Proc. Penna. Acad. Sci. 37:122-126.
Croasdale, H. T. 1973. Freshwater algae of Ellesmere Island, N. W. T.
Nat. Mus. Canada, Publ. in Bot. 3:1-131. Pis. 1-18, 2 maps, 3 graphs.
Gottschall, R. Y. 1930. Preliminary report on the phytoplankton and pollution
in Presque Isle Bay, Lake Erie. Proc. Penna. Acad. Sci. 4:69-79.
MacEntee, F. J. 1970. A preliminary investigation of the soil algae of
northeastern Pennsylvania. Soil Scl. 110(5):313-317.
Mbrrlssey, R. V. 1928. Summer survey of algae in ponds on Presque Isle, Erie,
Pennsylvania. Penna. Acad. Sci. pp. 47-51.
Rosowske, J. R. and B. L. Parker. 1971. Selected papers in phycology. Univ.
of Nebraska Press. 876 pp.
Scott, A. M. and R. Gronblad. 1957. New and interesting desmids from the
Southeastern United States. Acta Soc. Scl. Fenn. n.s. B. 2(8):1-62.
Pis. 1-37.
Van Dersal, W. R. and J. L. Cartledge. ? . The blue-green algae of
Pennsylvania. Penna. Acad. Sci. pp. 82-88.
57
-------
APPENDIX
SPECIES LIST OF THE FRESHWATER ALGAE
IN TOPIC cowrr, PENNSYLVANIA
An asterisk (*} indicates a new species for the state, while
a double asterisk (**) indicates a new species for North America.
Abbreviations for habitats follow the author-citation and are enclosed
In parentheses. The abbreviations are as follows: Glatco Lodge (GL), Lake
Marburg (LM), Reek's farm pond (RP), Budd's farm pond (BF), storm drain
ditch (SD), Sheppard Myers Reservoir (SH), Hanover High School Nature Study
Pond (BE), and South Western Intermediate School Nature Study Pond (SW).
Tunnedlately following the habitat is a lower case letter indicating abundance:
c (common), f (fairly common), u (uncommon), and r (rare).
58
-------
<£>
CHLOROPHYTA
CHLOROPHYCEAE
VOLVOCALES
Carteria
C. klebsii (Dang.) Dillwyn - (GL)u
Chlamydomonas
*£. angulosa Dillwyn - (GL)c
*C. cienkowskli Schmldle - (GL,SM,SW)u
£. globosa Snow - (GL-SW)u
*C_. pseudoperty Pascher - (LM)r '
Chlorogonium
£. elongatum (Ehrenb.) Dang. - (GL)r
Haematococcus
*H. lacustris (Glrad.) Rostaf. - (ceramic ,
bird bath)r
Eudorina
E. elegans (Ehrenb.) - (GL,HH)f
Gonium
£. pectorale Muller - (GL,LM)f
Pandorina
£. morum (Muller) Bory - (GL,HH)f
Pleodorina
*.P. illinoisensis Kofoid - (GL,HH,SW)f
Volvox
*V. aureus Ehrenb. - (GL)r
*\L perglobator Smith - (GL)r
*V^. tertius A. Mayer - (GL,SW)c
TETRASPORALES
Schizochlamys (Placosphaera)
*S_. compacta Prescott - (GL)r
Tetraspora
T^. gelatinosa (Vaucher) Desvaux -
(GL)u
*J. lamellosa Prescott - (GL,HH)f
T_. lubrica (Roth) C. A. Ag. - (GL)c
Asterococcus
*A. limneticus G. M. Smith - (GL)r
Gloeocystia
£. ampla (KUtz.) Lagerh. - (GL,HH)f
*£. gigas (KUtz.) Lagerh. - (LM)u
Stylosphaeridium
*£. stipitatum (Bachm.) Geitler & Gimesi
(GL)r
CHLOROCOCCALES (CHLOROSPHAERALES)
Characium
£. ambiguum Hermann - (GL)c
*C. falcatum SchrBder - (GL)r
-------
*£• hooker! (Reinsch) Hansg. - (SD)r
£. limneticum Leram. - (LM)r
*£. obtusum A. Braun - (GL)r
*C. ornithocephalum A. Braun - (GL)f
£. pringsheimii A. Braun - (GL)£
*£. roatratum Reinhard - (GL)r
Chlorococcum
*£. hum! co la (NHg.) Rabenh. - (GL)c
Closteridium
*£• lunula Reinsch - (LM)r
Planktosphaeria
£. gelatinosa G. M. Smith - (lM,SW)r
g TetraBdron
*•
(Reinach) Hansg. - (RF)r
*T. hastatum
var. palatinum (Schmidle) Leram. - (RF)f
*^T. limneticum Borge - (GL,RF)u
*T\ lobulatum var. crassum Preacott - (RF)r
T\ minimum (A. Braun) Hansg. - (LM,RF,SW)c
T\ muticum (A. Braun) Hansg. - (GL)r
*TP. muticum
var. punctulatum (Reinsch) De Toni - (GL^)r
*T\ pentaedricum W & W - (RF)r
*^. quadricuapidatum (Reinsch) Hansg. - (RF)r
*^. regulare var. incua Telling - (RF)u
*T_. trigonum
var. gracile (Reinsch) De Toni - (RF)r
Palmella
P_. mucosa KUtz. - (HH)f
Sphaerocystis (Palmellocyatia)
£. schroeteri Chodat - (LM,SW)u
Ankistrodesmus
A_. convolutua Corda - (LM)f
A. falcatus (Corda) Ralfa - (LM,SW)f
i *A. falcatus var. acicularia (A. Braun) (LM)r
G. S. Weat - (LM)r
*A^. falcatus var. mirabilis W & W - (LM,SW)r
*A. falcatus var. tumidus W & W - (LM)r
*A_. spiralls (Turner) Lemm. - (LM)u
Chlorella
£. vulgaris Beyerinck - (GL,LM,HH,RF,SW)c
Zoochlorella
*Z^. paraaitica Brandt - (LM)c
Chodatella (Lagerheimia)
*£. citriformis
var. paucispina Tiff. & Ahls. - (GL)r
*C_. quadriseta Lemm. - (LM)r
*C. subsalaa Lemm. - (LM)r
-------
a\
Closteriopsis
*£. longissima var. tropica W & W - (GL)r
Eremosphaera
IJ. vlridis De Bary - (GL)r
Franceia
*]?. droescheri (Lemm.) - (GL)r
Kirchnerlella
*K. contorta (Schmldle) Bohlin - (GL)u
*JK. lunaris
var. irregularis G. M. Smith - (RF)f
Nephrocytium
*N. agardhianum NHg. - (LM,RF)c
*N. obesum W & W - (LM,HH,RF)c
Oocystis
0. borgei Snow - (GL,LM,SW)c
*0. parva W & W - (LM,RF)f
*£. puailla Hansg. - (GL)c
Quadrigula
*£. chodatii (Tan. - Full.) G. M. Smith - (LM)r
£. lacustris (Chodat) G. M. Smith - (GL,RF)r
Selenastrum
*£. bibraianum Reinsch - (LM,SW)f
S_. gracile Reinsch - (LM,SW)c
*£. minutum (Nag.) Collins - (GL)u
*£. westii G. M. Smith - (GL)f
Trochiscia
*T^. reticularis (Reinsch) Hansg. - (GL,LM,SW)u
Golenkinia
*£. paucispina W & W - (GL)r
£. radiata (Chodat) Wille - (GL)r
Micractinium
*ll. pus ilium Fresenlus - (GL)r
Botryococcus
B^. braunii KUtz. - (GL)r
Dimorphococcus
*I). lunatus A. Braun - (UI)r
Actinastrum
A. gracillimum G. M. Smith - (LM)u
Coelastrum
£. cambricum Archer - (GL,RF)f
£. microporum NHg. - (GL,RF,SW)c
*£. sphaericum NHg. - (LM,RF,SW)u
Crucigenia
£. rectangularia (A. Braun) Gay - (LM,SW)r
*£. tetrapedia (Kirchner) West - (LM)u
*C. truncate G. M. Smith - (LM)r
-------
Scenedesmus
*£. abundans (Kirchner) Chodat - (LM)f
*J5. abundans
var. asymmetrica (SchrUder) G. M. Smith -
(LM)u
*S_. abundans var. brevicauda G. M. Smith - (GL)u
*S_. abundans
var. longicauda G. M. Smith - (LM,RF,SW)c
*£. acuminatus (Lagerh.) Chodat - (GL)r
*S. acutiformis SchrBder - (GL)u
*S_. arcuatus
var. platydisca G. M. Smith - (RF)r
§.• bijuga (Turpin) Lagerh. - (GL,LM,HH)c
*S_. br as i liens is Bohlin - (LM,SW)r
*!S. brevispina (G. M. Smith) Chodat - (LM)r
*j>. denticulatus Lagerh. - (GL)u
S_. dimorphus (Turpin.) KUtz. - (LM)u
*S_. incraasatulus
var. mononae G. M. Smith - (GL)u
*S>. longus Meyen - (GL,HS)u
*j>. longus
var. naegelii (BrSb.) G. M. Smith - (GL,LM)u
*S.« obliquus (Turpin) KUtz. - (GL,LM,HH)u
*!S. opoliensis P. Richter - (GL,LM,RF)f
*j>. opoliensis var. contacta Prescott - (SD)u
Si. quadricauda (Turpin) Bre"b. - (GL,LM,HH,
RF,BF,SW)c
*J3. quadricauda var. longispina (Chodat)
G. M. Smith - (GL,HH,BF)c
*S^. quadricauda var. maximua W & W - (SD)r
*S^. quadricauda var. parvus G. M. Smith - (SD)r
*S^. tibiscenais Uherkovich - (GL,SW)r
Tetradesmus
*T. wisconsinense G. M. Smith - (GL,RF)r
Tetrastrum
^. staurogeniaeforme (SchrOder) Lemm. - (GL)u
*T^. tetracanthum G. S. W. Brunnthaler - (RF)r
Hydrodictyon
H. reticulatum (L) Lagerh. - (GL.LM.HH,
RF,BF)c
Pediastrum
P_. boryanum (Turpin) Menegh. - (GL,LM,AQ)c
*£. boryanum var. longicorne Racib. - (LM)u
P^. duplex Meyen - (GL,LM,RF)c
*P_. duplex Meyen
var. clathratum (A. Braun) - (LM)u
P_. duplex var. gracillimum W & W - (RF)u
*P_. duplex var. reticulatum Lagerh. - (RF)r
P_. simplex Meyen Lemm. - (GL,RF)c
P_. simplex
var. duodenarium (Bailey) Rabenh. - (RF)r
(Ehrenb.) Ralfs - (GL,LM,RF,
BF,SM,HH,SW)c
-------
U)
*£. tetraa Ehrenb. Ralfs
var. tetraodon (Corda) Rabenh. - (GL,HH,RF)c
Sorastrum
*£. americanum (Bohlin) Schmidle - (LM,SW)r
*JJ. spinulosum N3g. - (LM,SW)r
ULOTRICHALES
Chlorhormidium (Hormidium)
*C. klebsli G. M. Smith - (GL,LM)c
Geminella
G. minor (NMg.) Heering - (GL)r
*G. mutabilis (Br6b.) Wille - (GL)r
Radiofilum
*,R. flavescens G. S. W. - (GL)r
Stichococcus
*S_. scopulinus Hazen - (GL)u
£. subtills (KUtz.) Klercker - (HH)u
Ulothrix
£. aequalis KUtz. - (GL)c
*_U. subtilissima Rabenh. - (GL)u
£. tenerrima KUtz. - (GL)c
*_U. variabilis KUtz. - (GL)c
IJ. zonata (Weber & Mohr) KUtz. - (SD)r
Uronema
*]J. elongatum Hodgetts - (LM)u
Microspora
*M. pachyderma (Wille) Lagerh. - (GL)u
*M. willeana Lagerh. - (GL)u
Cylindrocapaa
*£. conferta W. West - (GL)c
£. geminella var. minor Hansg. - (GL,HH)u
ULVALES
Schizomeris
S^. leibleinii KUtz. - (GL)r
Schizogonium
*£5. murale KUtz. - (LM)r
Chlorosarcina
*C^. consociata (Klebs) G. M. Smith - (GL)r
Chaetophora
'*£• attenuata Hazen - (LM)u
Protococcus (Desmococcus)
Z.- viridis C. A. Ag. - (bark,north side
of tree)f
Draparnaldia
*D. acuta (C. A. Ag.) - (SM)r
Microthamnion
*M. Btrictissium Rabenh. - (GL)r
Protodertna
P. viride KUtz. - (GL)r
-------
ON
Stigeoclonlutn
*j>. flagelliferum KUtz. - (SD)u
S^. nanum KUtz. - (juvenile stage) (SD)u
*S_. pachydermum Prescott - (SD)c
£. subsecundum KUtz. - (LM)u
£. tenue (C. A. Ag.) Kfftz. - (LM)u
Aphanochaete
A. repens A. Braun - (GL)r
A. vermiculoides Wolie - (GL)r
Chaetosphaeridium
*C. globosum (Nordst.) Klebahn - (LM)r
Coleochaete
£. orbicularia Pringshelm - (GL,LM)f
£. scutata Br£b. - (LM)u
£. aoluta Pringsheira - (LM)r
Dicranochaete
*I). reniformis Hieronymus - (IM)r
OEDOGONIALES
Oedogonium
*(). inconspicuum Hirn - (LM)r
*0. rufescens
var. exiguum (Elfv.) Tiff. - (GL)u
*0. suecicum Wittr. - (LM)r
*0. vulgare (Wittr.) Tiff. - (LM)f
CLADOPHORALES
Cladophora
£. glomerata (L) KUtz. - (GL)u
*£. inaignis (C. A. Ag.) KUtz. - (SD)u
Rhizoclonium
R. fontanum KUtz. - (SD)u
R. heiroglyphicum (C. A. Ag.) KUtz. - (GL,HH)c
*R. hookeri KUtz. - (SD)r
ZYGNEMATALES (Conjugales)
Spirogyra
S^. condensata (Vaucher) KUtz. - (LM)r
S^. weberi KUtz. - (GL,HH)r
Zygnema
*£. pectinatum (Vaucher) C. A. Ag. - (LM)r
ZYGNEMATALES (Conjugales)
MESOTAENIACEAE
Gonatozygon
*£. kinahani (Archer) Rabenh. - (GL)f
*G_. monotaenium De Bary - (GL)u
£. pilosum Wolle - (GL)u
Netrium
*N. digitus (Ehrenb.) Itzigs. & Roth - (GL)u
-------
ON
Oi
*N. dlgitus
var. lamellosum (Br6b.) Grbnblad - (GL)r
*l±. in t err up turn (Br£b.) LUtkm. - (GL)r
Spirotaenia
Su condensata Br£b. - (GL)r
*S. trabeculata A. Braun - (SM)r
DESMIDIACEAE
Actinotaenium
*A. dlplosporum (Lundell) Telling
var. americana W & W — (GL)r
*A. perminutum (Turner) Telling - (GL)u
*A. rufescens (Cleve) Telling - (SM)r
Arthrodesmus
*A. incus var. ralfsii W & W - (GL)r
Closterium
*C1. abruptum W & W - (GL)f
Cl. acerosum (Schrank) Ehrenb. - (GL,HH,RF)u
*C1. acerosum (Schrank) Ehrenb.
var. elongatum Breb. - (GL,BF,SU)u
Cl. angustatum KUtz. - (GL)u
*C1. cynthia De Not. - (GL,LM)u
Cl. didymotocum Corda - (GL)r
*C1. gracile Br6b.
var. intermedium Irenee-Marie - (GL)r
*C1.
*C1.
*C1.
Cl.
Cl.
*C1.
Cl^.
Cl.
|*C1.
i
*C1.
~~
i Cl.
*C1L.
*C1.
*C1.
Cl.
*C1L.
*C1.
idiosporum W & W - (GL)u
incurvum Breb. - (GL,LM,SW)u
intermedium Ralfs - (GL)f
Intermedium
var. hlbernicum West - (GL)r
lanceolatum KUtz. - (GL)u
leibleinii KUtz. - (GL,RF)f
libellula (Focke) Nordst. - (GL)r
lineatum Ehrenb. - (GL,HH,BF,SW)u
lunula (MUller) Nitzsch - (GL,BF,SW)r
lunula (MUller) Nitzsch
fa. minor - (GL)r
lunula (MUller) Nitzsch intermedium Gutw.
(GL)r
moniliferum (Bory) Ehrenb. - (GL.LM,
HH,SM,BF,SW)c
navicula (Br6b.) LUtkm. - (GL,SM)r
praelongum Br^b. - (GL)r
prltchardianum Archer - (RF)r
ralfsii Br6b. - (GL)r
ralfsii Breb.
var. hybridum Rabenh. - (GL)r
strigosum Br6b. - (GL,BF)c
striolatum Ehrenb. - (LM,BF)r
subulatum (KUtz.) BrSb. - (GL)u
tumidum Johnson - (GL,SM,SW)f
-------
Cl. turgidum Ehrenb. - (GL)r
Cl. venus KUtz. - (GL,RF,SW)u
Cosmarium
*Cos. abbreviatum Racib. - (LM,HH)u
*Cos. angulare Johnson - (GL,SM,BF)f
*Cos. anguloaum Br6b. - (GL)r
*Cpjs. binum Nordst. - (GL,RF)u
Cos, bloculatum Br£b. var. depreasum
(Schaarschm.) Schmidle fa. minus - (RF)r
Cos. circulare Reinsch - (GL,BF)r
*Cos. contractum Kirchner _ (LM)r
Cos, dentatum Wole - (GL,RF)u
Cos, depreasum (Nag.) Lundell - (GL)r
*Cos. furcatospermum W & W - (GL,LM,HH,
RF,BF,SM,SW)c
*Cos. globosum fa. minor Boldt - (LM)r
*Cos. globosum Bulnh.
var. subaltum Messlk. - (GL)r
Cos, granatum Breb. - (GL,LM,HH,RF,BF,SM,SW)c
*Cos. hammer1 Reinsch
var. protuberans W & W - (GL)r
Cos, holmlense Lundell
var. integrum Lundell - (LM)r
*Cos. Impressulum Elfv. - (GL)r
*Cos. inconspicuum W & W - (RF)r
*Cos. latifrona Lundell - (GL)r
*Cos. margaritatum (Lundell) Roy & Biss.
, fa. minor (Boldt) W & W - (GL)r
*Cos. meneghinii Br£b.
fa. reinschii Istvan. - (GL)r
*Cos. obliquum fa. minor Nordst. - (GL)r
Cos. obsoletum (Hantzsch) Reinsch - (GL)r
*Cos. obtusatum Schmidle - (SM,BF,SW)u
'i
., Cos. ornatum Ralfs - (GL)u
Cos. ovale Ralfs - (GL)u
Cos, pachydermum Lundell - (GL)r
*Cos. porrectum Nordst. - (LM)r
Cos, portianum Archer - (GL,LM)u
Cos. protractum (NHg) De Bary - (LM)u
Cos, pseudobroomei Wolle - (GL,LM,SW)f
*Cos. pseudoconnatum Nordst. - (GL,BF)f
*Cos. pseudoprotuberans Kirchner - (HH,RF)u
Cos. punctulaturn Breb. - (SM)r
*Cos. punctulaturn
var. subpunctulatum (Nordst.) BOrg. -
(GL,LM,SM)u
*Cos. pusilium (Bre"b.) Archer - (GL)r
Cos, quadrature Ralfs - (GL)r
*Cos. regnellii Wille - (LM)r
*Co8. regnellii Wille
var. minimum Elch. & Gutw. - (GL,LM)f
-------
Cos, regnesi Reinsch - (GL,LM)f
*Coa. regnesi var. montanum Schmldle - (GL)r
Cos, reniforme (Ralfs) Archer - (GL,LM,HH)f
*Cos. sexangulare fa. minima Nordst. - (GL,LM)u
Cos, sportella Breb. - (LM)u
*Cos . subcostatum Nordst. - (GL)r
Cos, subcrenatum Hantzsch - (GL,LM,HH,RF,BF)c
*Cps. subspeclosum Nordst. - (LM)r
*Cp8 . succlsum West - (GL)r
*Cos . tenue Archer - (GL)r
Cos. turplnll Breb. - (GL)r
Cos, turplnll Br6b.
var. podollcum Gutw. - (GL)r
*E. dubium
- (GL)r
Cos. venustum (Br6b.) Archer -
*Cos. zygomorphlcum Taf t - (LM,RF)r
Desmldlum
*D. aaymmetrlcum GrUnblad - (m)r
*D. grevellll (KUtz.) De Bary - (GL)r
I). swartzll C. A. Ag. - (GL)r
Euastrum
E. afflne Ralfs - (LM)r
]L. ansatum Ralfs - (GL)r
£. binale (Turpln) Ehrenb. - (GL,LM)r
E^. didelta (Turpin) Ralfs
var. ansatiforme Schmldle - (GL)r
E. inaulare (Wittr.) Roy - (GL,LM)u
*E^. obesum Josh. - (RF)r
E. oblongum (Grev.) Ralfs - (GL)r
^. yentrlcosum Lundell - (GL)r
E_. verrucoBum Ehrenb. - (GL,RF)u
E_. yerrucosum Ehrenb.
var. alatum Wolle - (GL)r
Hyalotheca
H. dlsslllens (J. E. Smith) Bre"b. - (GL,LM)u
]I. mucosa (Dillwyn) Ehrenb. - (GL,LM)r
Mlcrasterlas
*M. abrupt a W & W - (LM)r
M. amerlcana (Ehrenb.) Ralfs - (GL)r
M. aplculata (Ehrenb.) Menegh. - (GL)r
M. aplculata
var. flmbrlata (Ralfs) Nordst. - (GL)r
M. crux-melltensls (Ehrenb.) Hassall - (GL)r
M. denticulate Brgb. - (GL)r
M. laticeps Nordst. - (GL,LM,BF)f
M. murlcata (Bailey) Ralfs - (GL)r
*M. radiata Hassall - (GL,LM,SW)f
M. rotata (Grev.) Ralfs - (GL,LM)u
*M. triincata var. semiradiata Cleve - (LM)r
Penium
]?. margaritaceum Ralfs - (GL,LM,RF,SW)c
-------
o>
00
£. spirostriolatum Barker - (LM)r
Pleurotaenium
PI,, ehrenbergii (Breb.) De Bary - (GL,LM)u
*P1. maximum (Reinach) Lundell - (LM,HH)f
PI. nodulosum Breb. - (GL)r
PI. trabecula (Ehrenb.) NSg. - (GL.LM,
RF,BF,SM,HH,SW)c
*P1. trabecula (Ehrenb.) NHg.
fa. clavata (KUtz.) W & W - (GL)r
PI. truncatum (Breb.) NSg. - (GL,SW)f
Spondylosium
*Sp. moniliforme Lundell - (GL)r
*Sp_. planum (Wolle) W & W - (GL,LM)f
Staurastrum
S£. alternana Breb. - (GL,HH,RF,BF)f
*St. apiculatum Brlb. - (GL)r
St. arctiscon (Ehrenb.) Lundell - (GL,LM)f
St. arcuatum Nordst. - (GL)r
St. avicula Br6b. - (GL)r
*St. avicula var. aubarcuatum West - (GL,BF)r
St. biennaenum Rabenh. - (LM)r
St. brebissonii Archer - (GL,LM,BF)f
St. brevispinum Br6b. - (GL)r
St^. dickiei Ralfs - (GL,LM)f
St. dilatatum Ehrenb. - (RF)r
St. furcatum (Ehrenb.) Br6b. - (GL)r
St. gladiosum Turner - (GL)r
St.. gracile Ralfs - (GL,LM,RF)f
*St. gracile var. nanum Wllle - (GL,SW)f
*St. hexacerum (Ehrenb.) Wlttr. - (GL,RF)r
St. hirautum (Ehrenb.) Brgb. - (RF,SW)r
*St. orbiculare
var. depressum Roy & Biss. - (GL,LM)f
St. paradoxum Meyen - (LM,RF)f
St. polymorphum Br^b. - (GL,LM,RF,
BF,SM,HH,SW)c
*St. polymorphum var. pusillum West - (GL,HH)r
*St^. radians W & W - (GL)r
St. aetigerum Cleve - (GL)r
St. striolatum (NMg.) Archer - (GL)r
St. tetracerum Ralfs - (LM,RF)f
i
*St. tetracerum
var. validum W & W - (GL,RF,SW)f
Xanthidium
3C. antilopaeum (Br6b.) KUtz. - (LM)r
CHAROPHYCEAE
CHARALES
Chara
*C. braunii Gmelin - (GL,LM)f
-------
so
*C. schweinitzii A. Braun - (GL)r
EUGLENOPHYTA
EUGLENALES
Euglena
*JE. acus var. longa Johnson - (GL,HH)f
*I5. acus var. rigida Hueber - (GL)r
E_. deses Ehrenb. - (GL)r
!• ehrenbergli Klebs - (GL,LM)f
*E. elastlca Preacott - (GL)r
JE. gracilis Klebs - (HH)r
E. ignobilis Johnson - (HH)r
IS. mlnuta Prescott - (GL,HH)f
E_. oxyuris Schmarda - (GL,LM)fc
IJ. oxyuris Schmarda
var. minor Delf. - (GL)r
E_. proxlma Dnag. - (HH)r
**E_. proxlma
var. amphoraeforrola Szabados - (SD)r
IJ. splrogyra Ehrenb. - (HH,BF)r
*JE. splrogyra var. fuslformls Def 1. - (HH)r
*E. vlrldls Ehrenb. - (GL)r
Eutreptla
*E. vlrldls (Klebs) - (SD)r
Lepoclnclis
L. ovum (Ehrenb.) Lemm. - (GL)r
*L. texta (Duj.) Lemm. - (HH)f
Phacus
P_. acumlnatus Stokes - (GL)r
P_. acumlnatus
var. drezepolakll Skvort. - (GL,LM)f
P^. anacoelus Stokes - (GL)r
£. caudatus Huebner - (GL,RF,SW)f
*P_. chlbroplastes Prescott - (GL)r
*P_. curvlcauda Swiren. - (GL,HH,BF)f
L- longlcauda (Ehrenb.) Duj. - (GL,HH,RF)f
*P. orblcularls Huebner - (LM)r
P_. pyrum (Ehrenb.) Stein - (GL)r
*£. segrettl var. ovum Prescott - (GL,HH)f
P_. splrogyra var. maxima Prescott - (GL,HS)fc
*P_. sueclcus Lemm. - (GL)r
*P_. tortus (Lemm.) Skvort. - (LM)r
£. trlqueter (Ehrenb.) Duj. - (GL)r
*P_. warszewlczll (Allegre & Jahn) - (LM)r
Trachelomonas
*T_. abrupta (Swiren.) Defl. - (GL)r
*^. acanthostoma (Stokes) Defl. - (BF)r
*T. armata (Ehrenb.) Stein - (GL)r
*TL_. armata
var. longlsplna (Playf.) Defl. - (GL)r
^. conlca Playf. - (GL)r
(Swiren.) Defl. - (LM)r
-------
T\ granulosa Playf. - (GL)r
T\ hispida
vaic. coronata Lemm. - (LM,HH,BF,SW)f
*T. intermedia Dang. - (BF)r
*J. lacuatrls Dreze. - (GL,RF,BF)f
*T\ robust a Swiren. - (LM,HH)f
*T\ rugulosa (Stein) Defl. - (RF)r
*T\ superba (Swiren.) Defl. - (GL,SW)f
*T_. superba var. swireniana Defl. - (GL)r
I.- volvocina Ehrenb. - (GL,LM,RF,
BF,SM,HH,SW)c
Astasia
A. klebsi Lemm. - (GL,LM,HH)f
Menoidium
**M. bibacillatum - (HH)r
M. incurvum - (RF,HH)r
Anisonema
A. ovale Klebs - (GL,LM,HH)f
Peranema
£. trichophorum (Ehrenb.) - (GL,HH,BF)f
Petalomonaa
*£. abscissa (DuJ.) Stein - (GL)r
*P. mediocanellata (Klebs) - (GL)r
PYRRHOPHYTA
DINOKONTAE
Gymnodinlum
*G_. pulyisculus (Ehrenb.) Stein - (GL)r
Glenodinium
(J. armatum Levander - (GL)r
*G_. kulczynskii (Wolosz.) Schiller - (GL)r
Peridiniuro
*£. bipes Stein - (GL)r
P_. inconspicuum Lemm. - (GL,HH)f
*P. willei Huit. - Kaas - (HH)r
Ceratium
C. hirundinella (MUller) Duj. - (GL,HH,
RF,SW)c
DINOCOCCALES
Cystodinium
*C. iners Geltler - (GL)r
CRYPTOPHYTA (CRYPTOPHYCEAE)
Chroomonas
*£. nordstedtii Hansg. - (LM)r
Cryptochrysis
*£. commutata Pascher - (GL)c
Chilomonas
£. paramaecium Ehrenb. - (GL,LM,HH,RF)c
-------
Cryptomonas
iC. ovata (Paacher) - (GL,LM,HH,RF)c
Cyanomastix
*C. morgani Lackey - (GL)r
CHLOROMONADOPHYTA
Gonyostomum
*(J. semen (Ehrenb.) Diesing - (GL)r
CHRYSOPHYTA
XANTHOPHYCEAE (HETEROKONTAE)
RHIZOCHLORIDALES
Stipltococcus
*S^. crasslatipatua Prescott - (GL)r
*£. urceolatus W & W - (GL)r
MISCHOCOCCALES j
Botrydiopsis
*B. arhiza Borzi - (LM)r
Gloeobotrys
*£. limneticus (G. M. Smith) Pascher - (GL)r
Characiopsis
*JC. cylindrica (Lambert) Lemm. - (LM)r
*C. pyriformia (A. Braun) Borzi - (LM)r
Ophiocytium
0. capitatum Wolle - (GL)r
*0. gracilipes (A. Braun) Rabenh. - (GL,HH)f
'*0. mucronatum (A. Braun) Rabenh. - (GL)r
(). parvulum (Perty) A. Braun - (GL)r
TRIBONEMATALES
Tribonema
T. bombycinum (C. A. Ag.) - (GL,BF)r
*TT. bombycinum var. tenue Hazen - (GL)r
T. utriculosum (KUtz.) Hazen - (GL)r
VAUCHERIALES
Vaucheria
V_. aversa Hassall - CGL)r
*V^. polysperma
var. fontinalls (L) Christensen - (GL)r
*Y« sessilis
fa. clavata (Klebs) Heering - (GL)r
RHIZOCHRYSIDALES
Rhizochrysis
*R. limnetica G. M. Smith - (GL)r
*R. scherfellii (Pascher) - (GL)r
-------
Is)
Lagynion
*L. acherfellli Pascher - (GL)r
*L. triangularis
var. pyramidatum Prescott - (GL)r
CHROMULINALES
Chrysococcus
*C. rufeacena Kleba - (HH)r
Chrysopyaix
*C. bipes Stein - (GL)r
Chrysocapsa
*£. planctonica (W & W) Pascher - (GL)r
OCHROMONADALES
Cyclonexis
*C. annularis Stokes - (LM)r
Uroglenopsis
*IJ. americana (Calkins) Lenun. - (GL)r
Dinobryon
I), bavaricum Imhof - (GL)r
I), sertularia Ehrenb. - (GL,LM,RF,HH)c
I), tabellariae (Lerara.) Pascher - (GL)r
Mallomonaa
M. acaroides Perty - (GL)r
*M. caudata Iwanoff - (GL)r
Synura
*J5. uyella Ehrenb. - (GL)r
CYANOPHYTA
CHROOCOCCALES
Aphandcapsa (Anacystis)
*A. rivularia (Carm.) Rabenh. - (GL,HH)f
Aphanothece
A. nidulans P. Richter - (GL)r
*A. saxicola NMg. - (GL)r
*A. stagnina (Spreng.) A. Braun - (GL)r
Chroococcus
*C_. disperaua var. minor G. M. Smith - (GL)r
*£. minor (KUtz.) N3g. - (GL)r
*£. minutus (KUtz.) NSg. - (GL)r
C. turgidua (KUtz.) NHg. - (LM,HH)f
Coelosphaerium
*£. collinaii Drouet & Daily - (GL,LM)f
£. kuetzingianum NMg. - (LM)r
£. naegelianum Unger - (GL,LM,HH)f
Gloeocapaa
G_. aeruginoaa (Carm.) KUtz. - (GL)r
G. magma (Br^b.) KUtz. - (IM)r
*£. punctata NMg. - (GL)r
G. rupeatria KUtz. - (GL,RF,SW)f
-------
Gloeothece
*•
NMg. - (GL)r
Merismopedia
*M. elegans A. Braun - (LM,HH)f
*M. elegans var. major G. M. Smith - (GL)r
M. glauca (Ehrenb.) NHg. - (GL,HH)c
M. punctata Meyen - (LM)r
M. tenulssima Leram. - (GL)r
Microcystla
M. aeruginosa Klitz. emend. Elenkin - (GL,HH)f
11. incerta Lemm. - (LM)r
CHAMAESIPHONALES
Xenococcus
*)C. achousboei Thuret
var. pallida Hansg. - (GL)r
OSCILLATORIALES
Borzia
*B/ trilocularis Cohn - (GL)r
Lyngbya
1^. aerugineo-caerulea (KUtz.) Goraont - (GL)r
*L. birgei G. M. Smith - (GL,RF)f
*L. epiphytica Hieronymus - (LM)r
*L. major Menegh. - (GL)r
Microcoleus
*M. lynpbyaceous (Ktitz.) Crouan - (GL,LM,HH)f
Oscillatorla
*(). amoena (KUtz.) Gomont - (LM)r
£. amphibia C. A. Ag. - (LM)r
£. anguina Bory - (GL,LM)f
*(). angusta Koppe - (LM,HH)f
(). forroosa Bory - (GL,BF,SW)f
*0. lacustris (Kleb.) Geitler - (GL)r
0. limnetica Lemm. - (GL,LM,HH,SW)f
£. limosa (Roth) C. A. Ag. - (GL,SM)f
0. princeps Vaucher - (GL,LM,HH,SW)f
0. splendida Grev. - (GL,HH,RF)f
^. tenuis C. A. Ag. - (GL)r
Phormidium
*£. ambiquum Gomont - (LM)r
£. miisicola Nauman & Huber-Pestalozzi - (BF)r
*£. retzii C. A. Ag. - (LM)r
Schizothrix
S.' calciola (C. A. Ag.) Gomont - (GL,
LM,HH,SW)f
Spirulina
*S^. laxissima G. S. West - (LM,RF)f
*S. major KUtz. - (LM,HH)f
-------
*£. princeps W & W - (LM)r
*£. subaalaa Oersted - (LM)r
Symploca
S. muscorum (C. A. Ag.) Gomont - (LM)r
Nodularia
Anabaena
NOSTOCALES
Leram. - (GL)r
A. clrclnalis (KUtz.) Geitler - (GL)r
*A. constricta (Szafer) Geitler - (GL)r
A. f los-aquae (Lyngbye) Br£b. - (GL)r
*A. hellcoldea Bernard - (GL)r
*A. subcyllndrlca Borge - (GL)r
A. varlabllls KUtz. - (HH)r
*A. wisconsinense Fresco tt - (GL,HH)f
Anabaenopsls
*A. elenklnll Miller - (GL)r
Aphan 1 z omenon
A. flos-aquae (L) Ralfs - (GL)r
Cylindrospermum
C_. ma jus KUtz. - (GL)r
C. musclola KUtz. - (GL)r
haryeyana (Thw.) Thuret - (HH)r
spumlgena Mertens - (GL,HH)f
Nostoc
*N. linckla (Roth) Bornet & Thuret - (HH)r
N_. sphaericum Vaucher - (LM)r
Calothrix
£. fusca (KUtz.) Bornet & Flan. -'
(ceramic bird bath)r
------- |