Macrobenthic invertebrate survey of Waneta and Lamoka Lakes, Schuyler County, September 16, 1996 and May 12, 1997
|
|
- Regina Wheeler
- 5 years ago
- Views:
Transcription
1 248 Macrobenthic invertebrate survey of Waneta and Lamoka Lakes, Schuyler County, September 16, 1996 and May 12, 1997 M.F. Albrigh( W.N. Harman NTRODUCTON Schuyler County encompasses 331 square miles of the Appalachian Plateau in the Finger Lakes region (Curatolo, 1991). The County's economy is largely tourism-based, relying heavily upon its aquatic natural resources. The eutrophic nature of some of these water bodies, including Waneta and Lamoka Lakes (Figure 1), has had detrimental impacts on traditional lake uses. Macrophyte growth and algal blooms have negatively impacted swimming, fishing, boating, and the perceived aesthetic qualities of theses areas. These changes are believed to have lead to a decline in both tourism and in lakeside property values (Curatolo, 1991). n order to address these concerns, Schuyler County initiated an aquatic vegetation control program in 1986 (Curatolo, 1991). This program was to serve as an integrated approach to manage the county's aquatic resources through monitoring, research, macrophyte harvesting, upland treatment, and public education. n 1990, a comprehensive study was undertaken in order to provide baseline information upon which lake management plans would be based (Curatolo, 1991). This work included a characterization of the physical qualities ofthe local lakes, surveys of their macroinvertebrate benthic populations, a description of macrophyte harvesting activities, a determination of the feasibility of conducting dredging operations in selected areas. t also addressed means of reducing nutrient inputs to these lakes. This document describes a two part benthic survey of Waneta and Lamoka Lakes, conducted 16 September 1996 and May The timing of these collections was to ensure documentation of temporal diversity. This database, when compared to previous work cited, and future works, will document the impacts of macrophyte management on the benthic faunal communities. The background material for this report is derived largely from Curatolo, BACKGROUND Waneta Lake (Figure 2) is 781 acres in surface area, of which over 90% is located in Schuyler County. The lake, at 1099 feet in elevation, occupies a volume of approximately 10,860 acre-feet and has about 6.8 miles of shoreline. This lake has a maximum depth of <30 feet. Approximately 450 dwellings and a Boy Scout camp line the shore. The substrate varies from silty to organic clay. Eurasian milfoil (Myriophyllum spicatum) dominated most of the shallows, 'Staff assistant, SUNY Oneonta, BFS
2 249 LAMOKA LAKE Figure 1. The location of Waneta, Lamoka, and Seneca Lakes in Schuyler County, New York (modified from Curatolo, 1991).
3 .. :: "'6'.,'.,:1 5 of \ \1 ;~ i~ ~ i ~ i ~ ~ 'f.)!~1 4! ~ J~,~ ~ ffi.\,.\ :\\"...., '.). o.~.. ~ BoAT LAUNCH STES ~.-... ffi o Shoreline UNLOADNG STES EXTENT OF VEGETATON SAMPLNG STATON PUBLC ACCESS Point N 250 i '/ Scout Camp,',3 0'. '\ \ \. \.,. 1\ i' 0'.. ~ \'. \. \'.\ 2 1. :-. ' 8 '-'-;J'. L::;J~, 1000 ' Figure 2. Waneta Lake, Schuyler County, New York, showing sampling stations (modified from Curatolo, 1991).
4 251 with plant diversity being considerably higher at the southernmost shores. On both sample dates, all substrates encountered in Waneta Lake were oxygenated. Lamoka Lake (Figure 3), contiguous with Mill Pond to the south and connected to Waneta Lake via a navigable channel to the north, is located in western Schuyler County. This shallow «47ft) eutrophic lake occupies 826 acres in surface area, 16,410 acre-feet in volume, and has approximately 11.3 miles of shoreline. n 1990, about 325 houses occupied the shoreline. Recreational activities include swimming, fishing, and boating (Curatolo, 1991). During benthic sampling, deeper substrates were dominated by anaerobic organic muds; a notable exception was observed at a drop-off at the northeastern shore (Site #L2), where compact sand was encountered. Here, shells ofunionid clams were collected. The predominating macrophytes encountered were the nonindigenous Eurasian milfoil (Myriophyllum spicatum) and curly leafed pondweed (Potamogeton crispus). Toward the southern, shallower end of the lake diversity was considerably higher, with Nuphar, Ceratophyllum, Heteranthera, and Vallisineria being well represented. At the time of sampling milfoil was practically absent from the Mill Pond area. The channel connecting Waneta and Lamoka Lakes exhibited a flora similar to that encountered in Mill pond. Access is provided to both lakes by boat launch sites maintained by the New York State Department of Conservation (NYSDEC). Neither lake is used as a potable water supply. Both lakes have been rated as moderately impaired on the NYSDEC 1989 Priority Problem List (NYSDEC, 1989). Despite inclement weather encountered throughout both days of sampling (45-50 F, steady rain), bird activity was considerable. On 16 September 1996 large numbers of tree swallows (ridoprocne hicolor) were active on Waneta Lake, presumably feeding on emerging aquatic insects. Two ospreys (Pandion haliaetus) and parasitic jaeger (Stercorarius parasiticus) were seen over Lamoka Lake; the latter seabird is extremely rare in this region and was likely displaced by recent tropical storms (Butts, 1996). On 12 May 1997 several species of early migrating songbirds were observed, with diversity being the greatest along the channel between the two Lakes. Two hen mallards (Anas platyrhynchos) were seen sitting on nests, and a pair of Canada geese (Branta canadensis) were seen on Lamoka Lake with newly hatched goslings. WATER QUALTY MONTORNG Temperature, dissolved oxygen, ph, and conductivity were measured using a Hydrolab Scout multiparameter water quality monitoring instrument which had been calibrated the days of data collection following manufacturer's operating manual (Hydrolab Corp., 1993). Readings were taken at 1 meter (m) intervals from the surface to the bottom. The maximum depth encountered at Waneta Lake was 8.2 meters (26.9 feet); that for Lamoka Lake was 13.4 meters (44.0 feet). On 16 September 1996, Waneta was undergoing fall overturn, although slight, presumably temporary stratification was observed below 8 m. Temperature in that area was approximately C less than the rest of the water column and dissolved oxygen was over 2 mg/lless than overlaying waters. Conductivity was between mmho/cm throughout. On
5 252 FLEET.:.-~- COVE 1000 ft N BOAT LAUNCH STES o PUBLC ACCESS ~ UNLOADNG STES -._.- EXTENT OF VEGETATON E9 SAMPLNG STATON POND Figure 3. Lamoka Lake, Schuyler County, New York, showing sampling stations (modified from Curatolo, 1991).
6 May 1997, the earliest signs of stratification were observed, with sight decreases in temperature and dissolved oxygen observed at the greatest depths. Temperature, dissolved oxygen, and ph profiles are graphically presented in Figures 4A and 4B. Lamoka Lake was stratified on 16 September, with the thermocline located between 6 and 7 m. Hypolimnetic waters were essentially anoxic «0.3 mg/l), a situation similar to that reported by Curatolo (1991) for corresponding dates in 1988, 1989 and Conductivity was approximately 190 mmho/cm through the epilimnion and increased below the thermocline to 213 mmho/cm at the bottom. Spring turnover was underway on 12 May, 1996.Temperature, dissolved oxygen, and ph profiles are graphically presented in Figures SA and 5B. These data, while limited, do not indicate any further shift toward eutrophy in either Waneta or Lamoka Lakes since Water samples collected on 12 May were analyzed for calcium content using the EDTA titrimetric method (APHA, 1989). Surface concentrations were 18.9 and 17.4 mg/l in Waneta and Lamoka Lakes, respectively. Water transparency was measured using a standard 20 em Secchi disk. Transparency was 2.0 m (6.6 ft) in Waneta and 1.9 m (6.2 ft) in Lamoka on 16 September 1996 and 1.2 m (3.9 ft) in both Lakes on 12 May Values reported by Curatolo (1991) indicate that Lamoka was somewhat more transparent and Waneta twice as transparent in 1996 compared to similar dates in THE BENTHC NVERTEBRATE COMMUNTY METHODS Macroinvertebrates were collected from nine sites on Waneta Lake and nine sites on Lamoka. These sites included eulittoral, littoral muds, littoral vegetation, and profundal benthos. The objective was to obtain faunal diversity and density data for comparison with previous (e.g. Curatolo, 1991) and future surveys to ascertain any effects of macrophyte and algae control programs, as well as other changes in water quality or the colonization of non-native species, on these populations. Benthic samples were collected in triplicate using either a 23 X 23 cm 2 or a 15 X 15 cm 2 Ekman dredge. The larger dredges, using a conventional cable and messenger, were used in deeper locations; in shallower areas, the smaller dredges were employed using extension handles. Eulittoral samples, where the substrate tended to be stony, were acquired by manually gathering all material within a 23 X 23 cm 2 quadrangle. Vegetative samples were collected by sweeping the macrophytes with a triangle net five times and rinsing the contents from the net. Effort was made to include the entire depth distribution of the macrophyte bed. Each vegetative sample was collected in quadruplicate. While it is recognized that these vegetative samples cannot be interpreted as truly quantitative, the attempt was made to standardize the method as much as possible so that future comparisons may be made.
7 254 A B ~ 6 7 o:s ~ J:: (1) 0... (1) Q 8 Q SD= 2.0 M SD= 1.2 M Temperature -- ph -.- Dissolved Oxygen Figure 4. Profiles of temperature (Qq, ph, and dissolved oxygen (mg/1) for Waneta Lake, 16 September, 1996 (A) and 12 May, 1997 (B).
8 255 A B i SD= 1.9 M 14 SD= 1.2 M --- Temperature -- ph -..- Dissolved Oxygen Figure 5. Profiles of temperature (OC), ph, and dissolved oxygen (mg/l) for Lamoka Lake, 16 September, 1996 (A) and 12 May, 1997 (B).
9 256 Upon retrieval, multiple samples were composited and passed through a #30 mesh brass screen, thus retaining all particulate matter over 583 microns. This material was transferred to one-gallon plastic jars, to which 95% ethanol was added until a final concentration of approximately 70% ethanol was reached. Several milliliters of rose bengal were added to each sample to later aid in the recognition of benthic organisms. n the laboratory, organisms were separated from the substrate by transferring each sample, spoonful at a time, into a white enamel pan and rinsing with adequate water to distribute the material. All benthic organisms were isolated and transferred to 6 dram vials containing 70% ethanol. Taxonomic determinations were made according to Pennak (1989), Peckarsky et at. (1990), and Merritt and Cummins (1996). Assistance with the identification of mites was provided by Lanciani (1996) and of weevils by Johnson (1997). Organisms were enumerated and weighed by taxa. Wet weight was determined by removing the organisms from their vials, setting on blotting paper for 15 minutes to remove excess alcohol, and weighing to the nearest 0.1 mg on an electronic balance (Wheat, 1994). No attempt was made to count Oligochaetes, as they tended to fragment during processing. Values indicating numbers of organisms and weights per sample represent composited triplicate (benthic) or quadruplicate (vegetative) samples. For benthic sites, where sample size was more standardized, data were converted to units per meter 2 RESULTS AND DSCUSSON A description of each sample site, including sample type, sampling method, substrate characterization, and dominant macrophytes, is summarized in Table 1 A and B (refer to Figures 2 and 3 for site locations). A total of 81 taxa were collected in this survey, with 61 and 68 taken from Waneta and Lamoka, respectively (Table 2). The 16 September 1996 survey revealed a total of 58 taxa; 44 were collected from Waneta Lake and 45 from Lamoka. On 12 May 1997,63 taxa were taken, with 61 from Waneta and 68 from Lamoka. Generally, diversity was greater in Lamoka, where the number of taxa per site averaged 28.7, compared to 19.4 taxa per site found in Waneta. The southernmost reaches of Lamoka Lake (sites L6-L9) exhibited the greatest diversity. Here, 52 taxa were discovered, with each site averaging This area is relatively shallow and macrophytes were likewise diverse. The Order Trichoptera (caddis flies) showed the greatest species richness, with 14 genera representing 4 families encountered. The comparatively large diversity of leptocerid and phryganeid caddisflies collected in Lamoka Lake is undoubtedly due to the marshy character of that biotope. Representatives of these families are typical of dense, but diverse submergent plant communities. Tables 3-20 describe the macrobenthic invertebrates for each site visited, including numbers and wet weights of each taxa found in both lakes. For benthic samples, abundance and biomass have been projected to units/meter 2. Some sites, where vegetative samples were collected in the first survey, benthic samples were collected in the second due to inadequate macrophyte densities in the spring. Because of this, data from some sites are not easily compared. A preliminary comparison of these data with those included in Curatolo (1991) suggest a marked
10 257 A B Site Sample Type Dominant Vegetation Substrate Characterization Waneta W Sub., 3 small dredges Myriophyllum spicatum organic clay W2 Sub., 3 small dredges M. spicatum organic clay W3 Veg. 4X5 sweeps M. spicatum organ ic clay W4 Sub., 3 large dredges none fine silty clay W5 Veg. 4X5 sweeps M. spicatllm organic clay W6 Sub., 3 small dredges M. spicatum organic detritus W7 Sub., quadrangle none stones (eu littoral) W8 Veg. 4X5 sweeps Ceratophyllul11 de/llersum organic clay W9 Veg. 4X5 sweeps Nuphar variegatu/l, Vallisneria americana organic mud Lamoka L Sub., 3 large dredges none organ ic mud (anox ic) L2 Sub., 3 small dredges none co 111 pact sand L3 Veg. 4X5 sweeps M. spicatul11 organ ic mud L4 Veg. 4X5 sweeps M. spicatuljl peaty organic mud L5 Sub., 3 small dredges Ai spicatulll organic mud L6 Veg. 4X5 sweeps M spicatuljl organic mud L7 Veg. 4X5 sweeps N. variegat/ll organic mud L8 Veg. 4X5 sweeps M. spicatum organic mud L9 Veg. 4X5 sweeps Heterallthera dubia, C dcmersum, V. americana organ ic mud Waneta W Sub., 3 small dredges C demersul11"pota!l1ogetull crisplls organic clay W2 Sub.,3 small dredges P. crispus organic clay W3 Sub., 3 small dredges P. crispus organic clay W4 Sub., 3 large dredges none fine silty clay W5 Sub., 3 large dredges M. spicatulll, P, crispus organic clay W6 Sub., 3 small dredges M. spicatum organic detritus W7 Sub., J quadrangle none stones (eulittoral) W8 Veg. 4X5 sweeps Ceratophylluln demersulll organic clay W9 Veg. 4X5 sweeps Nuphar variegatum, Vallisneria americana organic mud Lamoka L Sub., 3 large dredges none organic mud (anoxic) L2 Sub., 3 small dredges none compact sand L3 Veg. 4X5 sweeps M. spicatum organic mud L4 Veg. 4X5 sweeps M. spicatum peaty organic mud L5 Sub., 3 small dredges M. spicatum organic mud L6 Veg. 4X5 sweeps M. spicatum organic mud L7 Veg. 4X5 sweeps N. variegatm organic mud L8 Veg. 4X5 sweeps M. spicatum organic mud L9 Veg. 4X5 sweeps Heteranthera dllbia, C demersum, V americana organic llud Table 1. Description of macrobenthic invertebrate sampling sites, Waneta and Lamoka Lakes, 16 September 1996 (A) and 12 May 1997 (B). Sub.== substrate sample, Veg.== vegetative sample, small dredge==.0232 m 2, large dredge=.0523 m 2, quadrangle=.0523 m 2.
11 258 TAXA l-'latyhelmlnthes Turbellaria Tricladida Planariidae Nemotoda Annelida Oligochaeta Haplotaxida Naididae Tubificidae Lumbricidae Lumbriculida Lumbriculidae Hirudinea Pharyngobdellida Erpobdellidae Erpobdella Dina pana Alboglossiphonia heteroclita Rhynchobdellida Glossiphoniidae Helobdella Helobdella fusca Helobdella stagnalis Batracobdella Placobdella Glossiphonia complanata Piscicolidae Myzobdella lugubris Mollusca Bivalvia Paleoheterodonta Unionidae Lampsilis radiata (shells) Elliptio complanatus (shells) Veneroida Sphaeriidae Sphaerium Pisidium Waneta 09/16/96 05/12/97 Lamoka 09/16/96 05/12/97 Table 2. Summary ofmacrobenthic invertebrates collected from Waneta and Lamoka Lakes, 16 September 1996 and 12 May 1997.
12 259 Waneta Lamoka TAXA 09/16/96 05/12/97 09/16/96 05/12/97 Gastropoda Basommatrophora Lymnaeidae Lymnaea colume/la Planorbidae Gyraulus parvus Gyraulus hirsutus Promentus exacuous Physidae Physa integra Physa sayii Ancylidae ~ Ferrisia tarda Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnico/a imosa Arthropoda Arachnida Acariformes Hydrodromidae Hydrodroma Limnesiidae Pionidae Arrenuridae Arrenurus Sperconidae Spercon Crustacea Ostracoda Copepoda Harpacticoida sopoda Asellidae Caecidotea Amphipoda Gammaridae Gammarus ~ Talitridae Hyalel/a azteca Table 2 (cont.). Summary ofmacrobenthic invertebrates collected from Waneta and Lamoka Lakes, 16 September 1996 and 12 May 1997.
13 260 Waneta Lamoka TAXA 09/16/96 05/12/97 09/16/96 05/12/97 nsecta Ephemeroptera Baetidae Paracloeodes Callibaetis Caenidae Caenis Heptageniidae Stenacron Odonata (Anisoptera) Libellulidae Erythemis Corduliidae Epitheca Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Lestidae Lestes Hemiptera Pleidae Neoplea Mesoveliidae Mesovelia Lepidoptera Nepticulidae Pyralidae Acentria ephemerella Trichoptera Polycentropodidae Cernotina Leptoceridae Oecetis Ylodes Leptocerus Setodes Nectopsyche Ceraclea Phryganeidae Oligotricha Phryganea Table 2 (cant). Summary ofmacrobenthic invertebrates collected from Waneta and Lamoka Lakes, 16 September 1996 and 12 May 1997.
14 261 Waneta Lamoka TAXA 09/16/96 05/12/97 09/16/96 05/12/97 Hydroptilidae Orthatrichia Oxythira Hydoptilla Mayatrichia Agraylea Coleoptera Curculionidae Euhrychiopsis Dytisicidae Chrysomelidae Pyrrhalta Elmidae Dubiraphia Psephenidae Psephenus Diptera Muscidae Empididae Tabanidae Ceratopogonidae Sphaeromias Probezzia Dasyhelea Bezzia or Palpomyia Culicoides Chaoboridae Chaoborus Chironomidae Table 2 (cont.). Summary ofmacrobenthic invertebrates collected from Waneta and Lamoka Lakes, 16 September 1996 and 12 May 1997.
15 262 Waneta Lake Site 1 (benthic) 9/16/96 5/12/97 TAXA #/m"2 g/m"2 #/m"2 g/m"2 Platyhelminthes Turbellaria Tricladida Planariidae Nemotoda Annelida Oligochaeta Haplotaxida Naididae NA Tubificidae NA Lumbricidae NA Lumbriculida Lumbriculidae NA NA Hirudinea Rhynchobdellida Glossiphoniidae Helobdella stagnalis Batracobdella Placobdella Mollusca Gastropoda Basommatrophora Planorbidae Gyraulus parvus Gyraulus hirsutus Promentus exacuous Physidae Physa sp Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnico/a limosa Arthropoda Crustacea sopoda Asellidae Caecidotea Amphipoda Gammaridae Gammarus Talitridae Hyalella azteca Table 3. Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #1,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2.
16 263 Waneta lake Site 1 (benthic) 9/16/96 5/12/97 TAXA #/m A 2 g/m A 2 #/m A 2 g/m A 2 nsecta Ephemeroptera Caenidae Caenis Odonata (Zygoptera) Coenagrionidae Coenagrion or Ena//agma Trichoptera leptoceridae Ylodes 14 0,0603 Hydroptilidae Hydoptilla 14 <.0014 Diptera Ceratopogonidae Sphaeromias Bezzia or Palpomyia Culicoides 43 <.0014 Chaoboridae Chaoborus Chironomidae Table 3 (cont.). Summary of macrobenthic invertebrates collected from Waneta Lake, Site #1, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2.
17 264 Waneta Lake Site 2 (benthic) 9/16/96 5/12/97 TAXA #/m l 2 g/m ll 2 #/m l 2 g/m ll 2 Platyhelminthes Turbellaria Tricladida Planariidae Nematoda <.0014 Annelida Oligochaeta Lumbriculidae NA NA Hirudinea Rhynchobdellida Glossiphoniidae Helobdella stagnalis Mollusca Gastropoda Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnicola limosa Arthropoda Crustacea sopoda Asellidae Caecidotea Amphipoda Talitridae Hyalella azteca nsecta Ephemeroptera Caenidae Caenis Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Trichoptera Hydroptilidae Orthotrichia Diptera Muscidae Ceratopogonidae Sphaeromias Bezzia or Palpomyia Culicoides 29 <.0014 Chaoboridae Chaoborus Chironomidae Table 4. Summary of macrobenthic invertebrates collected from Waneta Lake, Site #2, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2.
18 265 Waneta Lake Site 3 (vegetative 9/15, benthic 5/12) TAXA Platyhelminthes Turbellaria 9/16/96 #/samp g/samp 5/12/97 #/m!l2 g/m!l2 Tricladida Planarlidae Nemotoda Annelida Oligochaeta Haplotaxida Naididae NA NA Lumbriculida Lumbriculidae NA Hirudinea Rhynchobdellida Glossiphoniidae Helobdella Mollusca Bivalvia Veneroida Sphaeriidae Pisidium Gastropoda Basommatrophora Planorbidae Gyraulus parvus Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnico/a limosa Arthropoda Arachnida Acariformes Hydrodromidae Hydrodroma Crustacea sopoda Asellidae Caecidotea Amphipoda Gammaridae Gammarus Talitridae Hyalella azteca Table 5. Summary of macrobenthic invertebrates collected from Waneta Lake, Site #3, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps (9/16/96) and per meter2 (5/12/97).
19 266 Waneta Lake Site 3 (vegetative 9/15, benthic 5/12) TAXA nsecta Ephemeroptera Caenidae Caenis Trichoptera Leptoceridae Oecetis 9/16/96 #/samp g/samp /12/97 #/m l 2 g/m ll Hydroptilidae Orthotrichia Diptera Ceratopogonidae Culicoides Chironomidae < Table 5 (cont.). Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #3, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps (9/16/96) and per meter 2 (5/12/97).
20 267 Waneta Lake Site 4 (benthic) 9/16/96 5/12/97 TAXA #/m l 2 g/m"2 #/m l 2 g/m ll 2! Platyhelminthes Turbellaria Tricladida Planariidae 72 <.0014 Annelida Oligochaeta Haplotaxida Naididae NA Lumbriculida Lumbriculidae NA Mollusca Gastropoda Mesogastropoda Hydrobiidae Amnico/a limosa Arthropoda Arachnida Acarjformes Limnesiidae 14 <.0014 Crustacea Ostracoda Amphipoda Talitridae Hyalella azteca 14 <.0014 nsecta Trichoptera Hydroptilidae Mayatrichia 14 <.0014 Diptera Chaoboridae Chaoborus Chironomidae Table 6. Summary of macrobenthic invertebrates collected from Waneta Lake, Site #4, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter.
21 268 Waneta Lake Site 5 (vegetative 9/16, benthic 5/12) 9/16/96 5/12/97 TAXA #/samp g/samp #/mf\2 g/mf\2 Platyhelminthes Turbellaria Tricladida Planariidae Nemotoda 14 <.0014 Annelida Oligochaeta Haplotaxida Naididae NA Tubificidae NA Lumbricidae \JA Lumbriculida Lumbriculidae NA Mollusca Gastropoda Basommatrophora Planorbidae Gyraulus parvus Physidae Physa sp Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnico/a /imosa Arthropoda Arachnida Acariformes Limnesiidae 14 <.0014 Crustacea Amphipoda Talitridae Hyale/la azteca nsecta Ephemeroptera Baetidae Paracloeodes Caenidae Caenis Odonata (Zygoptera) Coenagrionidae Coenagrion or Ena/lagma Lepidoptera Nepticulidae Table 7. Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #5,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps (9/16/96) and per meter2 (5/12/97).
22 269 Waneta Lake Site 5 (vegetative 9/16, benthic 5/12) 9/16/96 5/12/97 TAXA #/samp g/samp #/m fl 2 g/m fl 2 nchoptera Hydroptilidae Orthotrichia Oxythira Hydoptilla Coleoptera Curculionidae Euhrychiopsis Diptera Ceratopogonidae Bezzia or Palpomyia Chaoboridae Chaoborus Chironomidae Table 7 (cont.). Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #5, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps (9/16/96) and per metei" (5/12/97).
23 270 Waneta Lake Site 6 (benthic) 9/16/96 5/12/97 TAXA #/m l 2 g/m ll 2 #/m l 2 g/m ll 2 Platyhelminthes Turbellaria Tricladida Planariidae Nemotoda Annelida Oligochaeta Haplotaxida Naididae NA NA Tubificidae NA NA Lumbriculida Lumbriculidae NA NA Hirudinea Rhynchobdellida Glossiphoniidae Helobdella stagnalis Mollusca Gastropoda Basommatrophora Planorbidae Gyraulus parvus Mesogastropoda Hydrobiidae Amnicola limosa Arthropoda Arachnida Acariformes Hydrodromidae Hydrodroma 14 <.0014 Limnesiidae 14 < Crustacea Amphipoda Talitridae Hyalella azteca nsecta Ephemeroptera Caenidae Caenis Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Lepidoptera Nepticulidae Table 8. Summary of macrobenthic invertebrates collected from Waneta Lake, Site #6, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
24 271 Waneta Lake Site 6 (benthic) 9/16/96 5/12/97 TAXA #/mf\2 g/mf\2 #/mf\2 g/mf\2 Tnchoptera Hydroptilidae Oxythira Agraylea 14 <.0014 Coleoptera Dytisicidae Diptera Ceratopogonidae Probezzia Bezzia or Palpomyia <.0014 Culicoides Chaoboridae Chaoborus Chironomidae Table 8 (cont.). Summary ofmacfobenthic invertebrates collected from Waneta Lake, Site #6, 9/16/96 and 5/12/97 (see Figure 2 fof site locations). Densities and biomass presented per 20 vegetative sweeps.
25 272 Waneta Lake Site 7 (benthic) 9/16/96 5/12/97 TAXA #/m\2 g/ml\2 #/m\2 g/ml\2 Platyhelminthes Turbellaria Tricladida Planariidae Annelida Oligochaeta Haplotaxida Naididae NA Tubificidae NA Lumbriculida Lumbriculidae NA Hirudinea Pharyngobdellida Erpobdellidae Erpobde//a Arthropoda Crustacea Amphipoda Gammaridae Gammarus nsecta Diptera Ceratopogonidae Bezzia or Palpomyia Chironomidae Table 9. Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #7,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2
26 273 Waneta Lake Site 8 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Platyhelminthes Turbellaria Tricladida Planariidae Nemotoda Annelida Oligochaeta Haplotaxida Naididae NA NA Hirudinea Pharyngobdellida Erpobdellidae Dina parva Rhynchobdellida Glossiphoniidae Helobdella stagnalis Piscicolidae h1yzobdellalugubris Mollusca Bivalvia Veneroida Sphaeriidae Sphaerium Pisidium Gastropoda Basommatrophora Planorbidae Gyraulus parvus Promentus exacuous Physidae Physa integra Physa sayii Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnicola limosa Table 10. Summary of macrobenthic invertebrates collected from Waneta Lake, Site #8, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
27 274 Waneta Lake Site 8 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Arthropoda Arachnida Acariformes Limnesiidae Pionidae Crustacea Amphipoda Talitridae Hyalella azteca nsecta Ephemeroptera Caenidae Caenis Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Lepidoptera Nepticulidae Diptera Ceratopogonidae Bezzia or Palpomyia <.0001 Chaoboridae Chaoborus Chironomidae Table 10 (cont.). Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #8, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
28 275 Waneta Lake Site 9 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Platyhelminthes Turbellaria Tricladida Planariidae Nemotoda 1 <.0001 Annelida Oligochaeta Haplotaxida Naididae NA Tubificidae NA Lumbriculida Lumbriculidae NA Hirudinea Pharyngobdellida Erpobdellidae Alboglossiphonia heteroclita Mollusca Bivalvia Veneroida Sphaeriidae Sphaerium Pisidium Gastropoda Basommatrophora Lymnaeidae Lymnaea columella Planorbidae Gyraulus parvus Gyraulus hirsutus Physidae Physa sayii Mesogastropoda Hydrobiidae Amnico/a limosa Arthropoda Crustacea sopoda Asellidae Caecidotea <.0001 Table 11. Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #9,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
29 276 Waneta Lake Site 9 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Amphlpoda Gammaridae Gammarus Talitridae Hyalella azteca nsecta Ephemeroptera Caenidae Caenis Odonata (Anisoptera) Libellulidae Erythemis Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Hemiptera Mesoveliidae Mesovelia Lepidoptera Nepticulidae Pyralidae Acentria ephemerella Trichoptera Leptoceridae Leptocerus Coleoptera Curculionidae Euhrychiopsis Chrysomelidae Pyrrhalta Diptera Ceratopogonidae Bezzia or Palpomyia Culicoides Chironomidae Table 11 (cont.). Summary ofmacrobenthic invertebrates collected from Waneta Lake, Site #9, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
30 277 Lamoka Lake Site 1 (benthic) TAXA Annelida Oligochaeta Haplotaxida Naididae Tubificidae Lumbriculida 9/16/96 #/mf\2 g/mf\2 NA /12/97 #/mf\2 g/mf\2 ~ Lumbriculidae NA Arthropoda Crustacea Amphipoda Talitridae Hyalella azteca nsecta Diptera Chaoboridae Chaoborus Chironomidae Table 12. Summary of macrobenthic invertebrates collected from Lamoka Lake, Site #1,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2
31 Lamoka Lake Site 2 (benthic) 9/16/96 5/12/97 TAXA #/m\2 g/ml\2 #/m\2 g/ml\2 Platyhelminthes Turbellaria Tricladida Planariidae Nemotoda Annelida Oligochaeta Haplotaxida Naididae NA NA Tubificidae NA Lumbriculida Lumbriculidae NA Hirudinea Rhynchobdellida Glossiphoniidae Helobdella stagnalis i >---'1 Glossiphonia complanata ! -i Mollusca Bivalvia Paleoheterodonta Unionidae Lampsilis radiata (shells only Elliptio complanatus (shells only 278 Veneroida, Sphaeriidae i Sphaerium Pisidium Gastropoda Basommatrophora, Planorbidae Gyraulus parvus Promentus exacuous Physidae Physa integra Mesogastropoda Hydrobiidae Amnicola limosa Table 13. Summary of macrobenthic invertebrates collected from Lamoka Lake, Site #2, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2.
32 279 Lamoka Lake Site 2 (benthic) 9/16/96 5/12/97 TAXA #/m"2 g/m"2 #/m"2 g/m"2 Arthropoda Arachnida, Acariformes Limnesiidae 29 <.0014 Crustacea Copepoda Harpacticoida 29 <.0014 sopoda Asellidae Caecidotea Amphipoda Talitridae Hyalella azteca, nsecta Ephemeroptera Baetidae Callibaetis Caenidae ~ Caenis Odonata (Anisoptera) Corduliidae Epitheca Odonata (Zygoptera) Coenag rion idae Coenagrion or Enallagma Lepidoptera Pyralidae Acentria ephemerella Trichoptera Leptoceridae Leptocerus Setodes Phryganeidae Oligotricha Hydroptilidae Orthotrichia Oxythira Hydoptilla 14 <.0014 Diptera Tabanidae Ceratopogonidae Probezzia Bezzia or Palpomyia Chaoboridae Chaoborus Chironomidae Table 13 (cont.). Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #2, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter2.
33 280 Lamoka Lake Site 3 (vegetative) TAXA Platyhelminthes Turbellaria Tricladida Planariidae Annelida Oligochaeta Haplotaxida Naididae Lumbriculida Lumbriculidae Hirudinea Pharyngobdellida Erpobdellidae Alboglossiphonia heteroclita Rhynchobdellida Glossiphoniidae Helobdella stagnalis Batracobdella Placobdella Mollusca Bivalvia Veneroida Sphaeriidae Sphaerium Gastropoda Basommatrophora Planorbidae Gyraulus parvus Promentus exacuous Physidae Physa sayii Mesogastropoda Valvatidae Valvata tricarinata f 116/96 #/sari) g/samp 3 '.,, i 5/12/97 #/samp g/samp NA NA NA Hydrobiidae Amnicola limosa Table 14. Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #3,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
34 281 Lamoka Lake Site 3 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Arthropoda Arachnida Acariformes Limnesiidae 2 <.0001 Crustacea sopoda Asellidae Caecidotea <.0001 Amphipoda Gammaridae nsecta Ephemeroptera Gammarus Talitridae Hyalella azteca Caenidae Caenis 1 <.0001 Heptageniidae ~1 Stenacron Odonata (Anisoptera) Corduliidae Epitheca Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Trichoptera Leptoceridae Leptocerus Coleoptera Psephenidae Psephenus Diptera Ceratopogonidae Bezzia or Palpomyia Chironomidae Table 14 (cont.). Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #3, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
35 282 Lamoka Lake Site 4 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Platyhelminthes Turbellaria Tricladida Planariidae Annelida Oligochaeta Haplotaxida Naididae NA Tubificidae NA Lumbriculida Lumbriculidae NA Hirudinea Pharyngobdellida Erpobdellidae Erpobdella Alboglossiphonia heteroclita Rhynchobdellida Glossiphoniidae Helobdella stagnalis Mollusca Bivalvia Veneroida Sphaeriidae Pisidium Gastropoda Basommatrophora Planorbidae Gyraulus panus Gyraulus hirsutus Promentus exacuous Physidae Physa integra Physa sayii Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnicola limosa Arthropoda Arachnida Acariformes Hydrodromidae Hydrodroma Limnesiidae Table 15. Summary of macrobenthic invertebrates collected from Lamoka Lake, Site #4, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
36 283 Lamoka Lake Site 4 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Crustacea Copepoda Harpacticoida sopoda Asellidae Caecidotea Amphipoda Gammaridae Gammarus Talitridae Hyalella azteca nsecta Ephemeroptera Caenidae Caenis Odonata (Anisoptera) Corduliidae Epitheca Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Trichoptera Polycentropodidae Cemotina Leptoceridae Oecetis Leptocerus Nectopsyche Phryganeidae Phryganea Hydroptilidae Agraylea Coleoptera Elmidae Oubiraphia Diptera Ceratopogonidae Bezzia or Pa/pomyia Culicoides Chironomidae 4 < < Table 15 (cont.). Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #4, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
37 284 Lamaka Lake Site 5 (benthic) 9/16/96 5/12/97 TAXA #/m/l2 g/m/l2 #/m/l2 g/m/l2 Platyhelminthes Turbellaria Tricladida Planariidae Nematoda 29 <.0014 Annelida Oligochaeta Haplotaxida Naididae NA Lumbricidae NA Hirudinea Pharyngobdellida Erpobdellidae A/boglossiphonia heteroclita Rhynchobdellida Glossiphoniidae Batracobdel/a Mollusca Bivalvia Veneroida Sphaeriidae Sphaerium Gastropoda Basommatrophara Planorbidae Gyraulus parvus Gyraulus hirsutus Promentus exacuous Physidae Physa integra Mesogastrapoda Hydrobiidae Amnico/a limosa Arthropoda Arachnida Acariformes Hydrodromidae Hydrodroma Limnesiidae Sperconidae Spercon 14 <.0014 Table 16. Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #5,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2
38 285 Lamoka Lake Site 5 (benthic) 9/16/96 5/12/97 TAXA #/m"2 g/m"2 #/m"2 g/m"2 Crustacea Copepoda Harpacticoida sopoda Asellidae Caecidotea Amphipoda Gammaridae Gammarus Talitridae Hyalella azteca nsecta Ephemeroptera Caenidae Caenis Odonata (Anisoptera) Corduliidae Epitheca Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Trichoptera Polycentropodidae Cernotina Leptoceridae Oecetis Ylodes Leptocerus Nectopsyche Hydroptilidae Agraylea Diptera Empididae Ceratopogonidae Sphaeromias Bezzia or Palpomyia Chaoboridae Chaoborus Chironomidae ~ Table 16 (cont.). Summary of macrobenthic invertebrates collected from Lamoka Lake, Site #5, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per meter 2
39 286 Lamoka Lake Site 6 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Platyhelminthes Turbellaria Tricladida Planariidae Nemotoda Annelida Oligochaeta Haplotaxida Naididae Hirudinea Rhynchobdellida Glossiphoniidae He/obdella fusca Mollusca Bivalvia Veneroida Sphaeriidae Sphaerium Pisidium Gastropoda Basommatrophora Planorbidae Gyraulus parvus Gyraulus hirsutus Promentus exacuous Physidae Physa integra Physa sayii Ancylidae Ferrisia tarda Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnico/a limosa Arthropoda Arachnida Acariformes Hydrodromidae Hydrodroma Sperconidae Spercon NA NA <.0001 Table 17. Summary of macrobenthic invertebrates collected from Lamoka Lake, Site #6,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
40 287 Lamoka Lake Site 6 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp Crustacea Copepoda Harpacticoida 1 <.0001 sopoda Asellidae Caecidotea Amphipoda Talitridae Hyalella azteca nsecta Ephemeroptera Baetidae Paracloeodes Caenidae Caenis Odonata (Anisoptera) Corduliidae Epitheca Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Hemiptera Pleidae Neoplea Trichoptera Polycentropod idae Cernotina Leptoceridae Oecetis Leptocerus Ceraclea Hydroptilidae Oxythira Diptera Ceratopogonidae Sphaeromias Bezzia or Palpomyia CUlicoides Chaoboridae Chaoborus Chironomidae Table 17 (cont.). Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #6, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
41 Lamoka Lake Site 7 (vegetative) TAXA Platyhelminthes Turbellaria 9/16/96 #/samp g/samp 5/12/97 #/samp g/samp Tricladida Planariidae Annelida Oligochaeta Lumbriculida Lumbriculidae NA Hirudinea Rhynchobdellida Glossiphoniidae He/obde/la stagnalis Batracobde/la Mollusca Bivalvia Veneroida Sphaeriidae Sphaerium Pisidium Gastropoda Basommatrophora Planorbidae Gyraulus parvus Gyraulus hirsutus Promentus exacuous Physidae Physa Mesogastropoda Hydrobiidae Amnicola limosa Arthropoda Arachnida Acariformes Hyd rod romidae Hydrodroma Crustacea, sopoda Asellidae Caecidotea Amphipoda Talitridae Hyale/la azteca Table 18. Summary of macrobenthic invertebrates collected from Lamoka Lake, Site #7, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
42 289 Lamoka Lake Site 7 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp nsecta Ephemeroptera Baetidae Parae/oeodes Caenidae Caenis Odonata (Anisoptera) Libellulidae Erythemis Corduliidae Epitheca Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Hemiptera Pleidae Neoplea Mesoveliidae Mesovelia Trichoptera Polycentropodidae Cernotina Leptoceridae Ylodes Leptocerus Diptera Ceratopogonidae Sphaeromias 1 <.0001 Oasyhelea Bezzia or Palpomyia Chironomidae Table 18 (cont.). Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #7, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
43 290 Lamoka Lake Site 8 (vegetative) TAXA Platyhelminthes Turbellaria 9/16/96 #/samp g/samp 5/12/97 #/samp g/samp Tricladida Planariidae Nematoda 1 <.0001 Annelida Oligochaeta Haplotaxida Naididae NA NA Hirudinea Rhynchobdellida Mollusca Glossiphoniidae Glossiphonia complanata Bivalvia Veneroida Sphaeriidae Pisidium Gastropoda Basommatrophora Arthropoda Arachnida Planorbidae Gyraulus parvus Promentus exacuous Physidae Physa sayii Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnicola limosa Acariformes Limnesiidae 2 <.0001 Arrenuridae Arrenurus Crustacea Ostracoda 1 <.0001 Copepoda Harpacticoida 1 <.0001 Table 19. Summary of macrobenthic invertebrates collected from Lamoka Lake, Site #8,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
44 291 Lamoka Lake Site 8 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp sopoda Asellidae Caeeidotea Amphipoda Talitridae Hya/e//a azteea nsecta Ephemeroptera Baetidae Parae/oeodes Caenidae Caenis Odonata (Anisoptera) Corduliidae Epitheea Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Lepidoptera Nepticulidae Pyralidae Aeentria ephemere//a Trichoptera Polycentropodidae Cernotina Leptoceridae Oeeetis Y/odes Leptocerus Hydroptilidae Orthotrichia Oxythira Diptera Ceratopogonidae Sphaeromias Dasyhe/ea Bezzia or Pa/pomyia Cu/ieoides Chaoboridae Chaoborus Chironomidae Table 19 (cont.). Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #8, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
45 Lamoka Lake Site 9 (vegetative) TAXA Platyhelminthes Turbellaria 9/16/96 #/samp g/samp 5/12/97 #/samp g/samp Tricladida Planariidae Annelida Oligochaeta Haplotaxida Naididae Tubificidae NA NA Lumbriculida Lumbriculidae NA Hirudinea Rhynchobdellida Glossiphoniidae He/obdella Helobdella fusca Batracobdella Mollusca Bivalvia Veneroida Sphaeriidae Sphaerium Pisidium Gastropoda Basommatrophora Planorbidae Gyraulus parvus Promentus exacuous Physidae Physa sayii Mesogastropoda Valvatidae Valvata tricarinata Hydrobiidae Amnico/a limosa Crustacea Amphipoda Talitridae Hyalella azteca Table 20. Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #9,9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
46 293 Lamoka Lake Site 9 (vegetative) 9/16/96 5/12/97 TAXA #/samp g/samp #/samp g/samp nsecta Ephemeroptera Caenidae Caenis Odonata (Anisoptera) Corduliidae Epitheca Odonata (Zygoptera) Coenagrionidae Coenagrion or Enallagma Lestidae Lestes Lepidoptera Nepticulidae Trichoptera Polycentropodidae Cernotina Leptoceridae Oecetis Ylodes Leptocerus Hydroptilidae Orthotrichia Coleoptera Curculionidae EUhrychiopsis Diptera Ceratopogonidae Dasyhelea Bezzia or Palpomyia Culicoides Chaoboridae Chaoborus Chironomidae Table 20 (cont). Summary ofmacrobenthic invertebrates collected from Lamoka Lake, Site #9, 9/16/96 and 5/12/97 (see Figure 2 for site locations). Densities and biomass presented per 20 vegetative sweeps.
47 294 increase in benthic biodiversity. However, this is likely due to extraneous factors, such as differences in sampling and processing techniques and the taxonomic level to which some groups were determined. Acentria ephemerella, a larval aquatic moth, and Euhrychiopsis lecontei, an aquatic weevil, were collected in this survey. These organisms are known to feed consistently upon Myriophyllum spicatum (Eurasion watermilfoil). Recent research on E. lecontei suggests that this beetle has the potential to serve as an effective tool in managing milfoil (Sheldon, 1997). Neither of these insects was found in significant numbers; however, harvesting milfoil may have limited their populations. These animals tend to live in the upper portion of milfoil beds, feeding primarily on apical meristems of plants. Mechanical plant harvesting, therefore, has severe negative impacts on the populations of these animals (Sheldon, 1997; Harman et at., 1997). Limiting or discontinuing harvesting may result in a long term, self sustaining means of controlling milfoil. Waneta and Lamoka Lakes seem likely candidates for zebra mussel colonization. Calcium concentrations of approximately 18 mg/l, coupled with ph values of encountered in the Lakes, provide for conditions suitable for these organisms. Given the proximity of these Lakes to infested waters, including Seneca and Cayuga Lakes, and the readily available access afforded by convenient boat launching facilities, a protocol for preventing the introduction of these organisms would seem appropriate. REFERENCES APHA, AWWA, WPCF Standard methods for the examination of water and wastewater, 17 th ed. American Public Health Association. Washington, DC. Butts, W.L Personal communication. Biological Field Station, Cooperstown, NY. Curatolo, Final Report. The aquatic vegetation control program in Schuyler County, p. Schuyler County Soil and Water Conservation District, Montour Falls, NY. Harman, W.N., L.P. Sohacki, M.F. Albright, and D.L. Rosen The state of Otsego Lake, Occasional Paper #30, SUNY Oneonta Bio. Fld. Sta., SUNY Oneonta. Hydrolab Corporation Scout operating manual. Hydrolab Corp. Austin, TX. Johnson, R Personal communication. Cornell University. thaca, NY. Lanciani, C Personal communication. University of Florida. Gainesville, FL. Merritt, R.W., and K.W Cummins (eds.) Aquatic insects of North America. Kendall/Hunt Publishing Company. Dubuque, A.
48 295 New York State Dept. OfEnvir. Cons., New York State water quality, Bureau of Monitoring and Assessment. Division of Water. NYSDEC. Albany, NY. Peckarsky, B.L., P.R. Fraissinet, M.A. Penton, and OJ. Conklin, Jr Freshwater macroinvertebrates ofnortheastern J\Jorth America. Cornell University Press. thaca, NY. Pennak, R.W Freshwater invertebrates of the United States, 3rd Ed. John Wiley and Sons, nc. New Yark. Wheat, E A study of the macrobenthos of the eulittoral zone of Otsego Lake. /n 26 th Ann. Rept., Pp SUNY Oneonta Bio. Fld. Sta., SUNY Oneonta.
Macrobenthic invertebrate survey of Waneta and Lamoka Lakes, Schuyler County, New York, September, 1996.
133 Macrobenthic invertebrate survey of Waneta and Lamoka Lakes, Schuyler County, New York, September, 1996. Matthew Albright Willard N. Harman INTRODUCTION Schuyler County encompasses 331 square miles
More informationAn inventory ofmeroplankton associated with Myriophyllum spicatum, focusing on Acentria ephemerella, in Otsego Lake, summer 1997
80 REPORTS: An inventory ofmeroplankton associated with Myriophyllum spicatum, focusing on Acentria ephemerella, in Otsego Lake, summer 1997 Mary Miner INTRODUCTION Myriophyllum spicatum, commonly known
More informationAquatic invertebrate surveys of two ponds in Greenwoods Conservancy, one on and the other off the Volney-Marcy South Right of Way
Aquatic invertebrate surveys of two ponds in Greenwoods Conservancy, one on and the other off the Volney-Marcy South Right of Way Bekka S. Brodie 1 INTRODUCTION Greenwoods Conservancy, in Burlington, NY,
More informationAPPENDIX B THREE RIVERS SECOND NATURE RESULTS OF RAPID INVERTEBRATE BIOLOGICAL ASSESSMENT SAMPLING PHASE 2 APRIL 2002 A-19
APPENDIX B THREE RIVERS SECOND NATURE RESULTS OF RAPID INVERTEBRATE BIOLOGICAL ASSESSMENT SAMPLING PHASE 2 APRIL 2002 A-19 Shades Run Squaw Run Sandy Quigley Indian Powers Run Phylum Arthropoda Insecta
More informationMacroinvertebrate Response to a Gradient of Hydrologic Connectivity within the Lower Mississippi River and Its Floodplain
Macroinvertebrate Response to a Gradient of Hydrologic Connectivity within the Lower Mississippi River and Its Floodplain AUDREY B HARRISON, CLIFFORD A OCHS, WILLIAM T SLACK, K JACK KILLGORE, CATHERINE
More informationContinued observations of Moe Pond after the unauthorized stocking of smallmouth and largemouth bass
Continued observations of Moe Pond after the unauthorized stocking of smallmouth and largemouth bass Rebecca J. Hamway 1 INTRODUCTION Moe Pond (Figure 1) is located in Otsego County, New York and is a
More informationCurrent Status of Dreissena polymorpha and Biodiversity of Littoral Macroinvertebrates in Geneva Lake, Wisconsin
Current Status of Dreissena polymorpha and Biodiversity of Littoral Macroinvertebrates in Geneva Lake, Wisconsin Cassie Taplin (UW-Superior) Geneva Lake Environmental Agency December 2016 1 Introduction
More informationAquatic Plant Point-Intercept Survey for Pike Lake, Scott County, Minnesota
Campers on Pike Lake, Scott County, Minnesota, 2015 Aquatic Plant Point-Intercept Survey for Pike Lake, Scott County, Minnesota [Plant Survey Conducted August 24, 2015] Prepared for: Prior Lake/Spring
More informationChateaugay Lakes Milfoil Control Program
Chateaugay Lakes Milfoil Control Program Summary of Activities and Findings for June August 29 Prepared By: Daniel L. Kelting Executive Director Adirondack Watershed Institute Paul Smith's College P.O.
More informationKilkenny Central Access Scheme. Follow-up Aquatic Ecological Report
Kilkenny Central Access Scheme Follow-up Aquatic Ecological Report 6 th October 2014 Prepared on behalf of John Craddock Ltd. Tait Business Centre, Dominic Street, Limerick City, Ireland. t. +353 61 419477,
More informationWater Quality and Habitat in Shingle Creek
Water Quality and Habitat in Shingle Creek Definitions Habitat Meander Riffle Pool Cobble Substrate Buffer Stream Invertebrates Much of the aquatic life in streams is composed of benthic macroinvertebrates.
More informationA Survey of the Metrics Utilized to Determine Macroinvertebrate Indices in Eight Southeastern States
A Survey of the Metrics Utilized to Determine Macroinvertebrate Indices in Eight Southeastern States Don Lane, MS Senior Environmental Scientist Doss Engineering, Inc. dlane@dei-wv.com or laneds@suddenlink.net
More informationMismer. St. Martin s Duck
Pine River Mismer Mackinac Golf Course Mckay Cedarville Port Dolomite St. Martin s Duck 10 km Lake Huron Voight Peck Prentiss Almeda Wigwam Saginaw Bay Cotter Road Vanderbilt Park 25 km Wildfowl Bay/ Maisou
More informationRECREATIONAL PONDS AND LAKES
RECREATIONAL PONDS AND LAKES POND ECOLOGY AQUATIC PLANTS & FISH F.S. Conte Department of Animal Science University of California Davis Photos By Flickr AQUATIC PLANTS POND HEALTH Chemical Recycling Oxygen
More informationFish Survey Report and Stocking Advice for Loch Milton. (Loch a Mhuilinn), May 2011
Fish Survey Report and Stocking Advice for Loch Milton (Loch a Mhuilinn), May 2011 Jonah Tosney Freshwater Fisheries Biologist Wester Ross Fisheries Trust 1 Loch Milton (Loch a Mhuilinn) Fish Survey Report
More informationMud Bay SLELO-PRISM Water Chestnut & Hydrilla Surveillance 2012
St. Lawrence Eastern Lake Ontario Partnership for Regional Invasive Species Management Mud Bay Water Chestnut & Hydrilla Surveillance 2012 June 27 th (Water Chestnut) & August 2 (Hydrilla), 2012 Figure
More informationAquatic Plant Point-Intercept Survey for Cates Lake, Scott County, Minnesota
American Lotus in Cates Lake, Scott County, Minnesota, 2016 Aquatic Plant Point-Intercept Survey for Cates Lake, Scott County, Minnesota [Plant Survey Conducted August 29, 2016] Prepared for: Prior Lake-Spring
More informationAquatic Plants of the Three Lakes
Aquatic Plants of the Three Lakes Chris Doyle, CLM Senior Aquatic Biologist/Water Quality Program Supervisor Allied Biological, Inc. 580 Rockport Road Hackettstown, NJ 07840 Phone: 908-850-0303 E-mail:
More informationContinued monitoring of fish community dynamics and abiotic factors influencing Moe Pond, summer 2006
Continued monitoring of fish community dynamics and abiotic factors influencing, summer 26 Erika Reinicke 1 Georgette M. Walters 1 INTRODUCTION (Figure 1) is a eutrophic water body located on the Upper
More informationOrange County Water Authority
Orange County Water Authority Orange County, NY Water Quality Biomonitoring Project Report for year 00 Sample Dates: July - September 0, 00 Report Date: January 0 Prepared for ORANGE COUNTY WATER AUTHORITY
More informationASSESSMENT OF BALANCED AND INDIGENOUS POPULATIONS IN THE YADKIN RIVER AND HIGH ROCK LAKE NEAR BUCK STEAM STATION NC
ASSESSMENT OF BALANCED AND INDIGENOUS POPULATIONS IN THE YADKIN RIVER AND HIGH ROCK LAKE NEAR BUCK STEAM STATION NC0004774 Principal Investigators: Michael A. Abney James J. Hall Josh R. Quinn DUKE ENERGY
More informationTaxonomy. An Introduction to the Taxonomy and Ecology of EPT Families
An Introduction to the Taxonomy and Ecology of EPT Families Prepared by Dave Penrose North Carolina State University Biological and Agricultural Engineering Department Soil & Water Environmental Technology
More informationCHAPTER 2 AQUATIC INVERTEBRATES
CHAPTER 2 AQUATIC Draft June 17, 2009 10 Chapter 2 AQUATIC 2 AQUATIC Aquatic invertebrates can be found in nearly any habitat from small temporary pools to large lakes and small springs to large rivers.
More informationMARTINDALE POND Wayne County 2004 Fish Management Report. Christopher C. Long Assistant Fisheries Biologist
MARTINDALE POND Wayne County 2004 Fish Management Report Christopher C. Long Assistant Fisheries Biologist Fisheries Section Indiana Department of Natural Resources Division of Fish and Wildlife I.G.C.
More information[USP5655] [USP5650] [USP5653] [USP5649] [USP5654] [USP5648] 121 [USP5652] grazers 33. predator grazers 124 [USP5647]
Appendix Author(s): Source: A Rapid Biodiversity Assessment of the Nakauvadra Range, Ra Province, Fiji:-. 0. Published By: Conservation International URL: http://www.bioone.org/doi/full/0.896/0.07.00 BioOne
More informationRat Cove and Brookwood Point littoral fish survey, 2002
Rat Cove and Brookwood Point littoral fish survey, 2 Katie Wayman 1 INTRODUCTION During the summer of 2, efforts to monitor the Otsego Lake littoral fish community continued with trap netting at both Rat
More informationImpacts to Water Quality from Land Use or What is Pollution?
Water Quality Impacts to Water Quality from Land Use or What is Pollution? Pollution is: The addition of excessive carbon to a system The addition of large amounts of materials to water that causes adverse
More informationAquatic Plant Management and Importance to Sport Fisheries
Aquatic Plant Management and Importance to Sport Fisheries Presentation to Michigan Inland Lakes Convention May 2014 Mike Maceina Professor Emeritus School of Fisheries, Aquaculture, and Aquatic Sciences
More informationData Sheet. Macroinvertebrate Assessment. Part II: Water Quality Score. Part I: Color Dots. Color Code & Sensitivity Points. Type of Macroinvertebrate
(Page 1 of 8) Part I: Color Dots (Before assessment) 1. Read Color Code & Sensitivity Points below to understand the water quality conditions represented by the colors green, yellow, and red. Place the
More informationAquatic Insects. Dayton Steelman Northwest Arkansas Master Naturalist
Aquatic Insects Dayton Steelman Northwest Arkansas Master Naturalist Aquatic Habitat Excellent Stream Site Here we find a variety of organisms with very different body shapes and ways of making a living.
More informationSurvey of veliger and adult zebra mussels (Dreissena polymorpha) in Goodyear Lake
Survey of veliger and adult zebra mussels (Dreissena polymorpha) in Goodyear Lake Samantha Armstrong 1 ABSTRACT Zebra mussels, Dreissena polymorpha, which cause numerous ecological and economical damages,
More informationFeeding Selectivity of the American Eel Anguilla rostrata (LeSueur) in the Upper Delaware River
Am. Midl. Nat. 129:301-308 Feeding Selectivity of the American Eel Anguilla rostrata (LeSueur) in the Upper Delaware River CHARLES E. DENONCOURT AND JAY R. STAUFFER, JR. School of Forest Resources, The
More informationMoses Lake Fishery Restoration Project
Moses Lake Fishery Restoration Project Factors Affecting the Recreational Fishery in Moses Lake Washington Annual Report 2002-2003 DOE/BP-00006320-4 November 2003 Field37: This Document should be cited
More informationHydroacoustic surveys of Otsego Lake s pelagic fish community,
Hydroacoustic surveys of Otsego Lake s pelagic fish community, 2010 1 Holly A. Waterfield 2 and Mark Cornwell 3 INTRODUCTION Hydroacoustic surveys were conducted in May and November 2010 to estimate pelagic
More informationStatus of rainbow smelt (Osmerus mordax) in the Mohican Canyon Tributary, May 2014
Status of rainbow smelt (Osmerus mordax) in the Mohican Canyon Tributary, May 2014 Matthew J. Best 1 INTRODUCTION Rainbow smelt (Osmerus mordax) were thought to have been introduced into Otsego Lake in
More informationEnvironmental. Effects of Dredging
Envi~onmental Effects of Dredging Technical Notes THE VALUE OF GRAVEL DISPOSAL MOUNDS IN RIVER SIDE CHANNELS FOR FRESHWATER MUSSELS PURPOSE: This note provides information on the value of gravel disposal
More informationAquatic Macro-invertebrate Sampling at three sites on the Lower Duke of Northumberland s River; October 13 th 2015:
Photos Ilse Steyl Aquatic Macro-invertebrate Sampling at three sites on the Lower Duke of Northumberland s River; October 13 th 2015: WHPT Analysis and Preliminary Species Audit Report V_1.0 Conducted
More informationHaw River Watch. A Citizen Water Quality Project of the Haw River Assembly. Damselflies, Coenagrionidae and Lestidae families.
Haw River Watch A Citizen Water Quality Project of the Haw River Assembly Damselflies, Coenagrionidae and Lestidae families. Part 5: Identifying Macroinvertebrates 5-1 This part of the River Watch presentation
More informationThe Uptake of Mercury and Relationship to Food Habits of Fish in the South River and South Fork Shenandoah River
The Uptake of Mercury and Relationship to Food Habits of Fish in the South River and South Fork Shenandoah River G. W. Murphy, T. J. Newcomb, and D. J. Orth Dept. of Fisheries and Wildlife Sciences Virginia
More informationBioindicators of Water Quality Quick Reference Guide
Purdue Extension -H-9 Bioindicators of Water Quality Quick Reference Guide Authors: Julie Speelman and Natalie Carroll Photographer (unless otherwise noted): Julie Speelman Design and Layout: Jennifer
More informationChecklist (for turning in results)
Bio-monitoring Data Collection Packet tier 2 In collecting samples, sorting, identifying and recording data, please strive to be as meticulous as possible, following the protocols as carefully and completely
More informationCARL BLACKWELL LAKE MANAGEMENT PLAN
CARL BLACKWELL LAKE MANAGEMENT PLAN Background Lake Carl Blackwell impounds Stillwater Creek, 10 miles west of Stillwater in Payne County, Oklahoma (Figure 1). The lake covers 3,370 surface acres and was
More informationSALINITY. It's the amount of dissolved salts the water contains.
AQUATIC ECOSYSTEMS SALINITY The types of organisms in an aquatic ecosystem depend upon the water s Salinity. It's the amount of dissolved salts the water contains. Salinity determines the two main aquatic
More informationMEMORANDUM Comfort Lake-Forest Lake Watershed District
MEMORANDUM Comfort Lake-Forest Lake Watershed District To: Board of Managers Date: December 7, 2016 From: Mike Kinney Subject: 2016 Watercraft Inspections and AIS Report Summaries Watercraft Inspection
More informationConsolidated Data on the river Puyo and Piatua
Consolidated Data on the river Puyo and Piatua Table. Total Macroinvertebrates and percentage in river Puyo and Piatua S.No Name River Puyo % River Piatua % Platyhelminthes-. planarian 23.78 8.6.2 Cestoda.7
More information2014 Threatened and Endangered Fish Survey of. East Loon Lake and West Loon Lake. Lake County, Illinois
2014 Threatened and Endangered Fish Survey of East Loon Lake and West Loon Lake Lake County, Illinois Prepared by Integrated Lakes Management 120 LeBaron St. Waukegan, IL 60085. Chris Ryan Chris Rysso
More informationMaxDepth Aquatics, Inc.
MaxDepth Aquatics, Inc. Hydroacoustic Survey and Point Sampling of Macrophytes In Diamond Lake 2009 A Report to the Partners for Umpqua Rivers Roseburg, OR And the Umpqua National Forest Roseburg, OR By
More informationAquatic Macroinvertebrate ID
Aquatic Macroinvertebrate ID Resources and skills necessary for good invertebrate ID: 1. Solid introduction - Preferably a general or aquatic entomology class, or other training from a reputable source.
More informationCommon Macroinvertebrates in the Clinton River Watershed
Common Macroinvertebrates in the Clinton River Watershed Phylum-Annelida Class- Oligochaeta Aquatic worms Class- Hirudinea Leeches Sediment, leaf pack, vegetation Long, thin, cylindrical, segmented 1 30
More informationSOONER LAKE MANAGEMENT PLAN
SOONER LAKE MANAGEMENT PLAN Background Lake Sooner impounds Greasy Creek, 15 miles south of Ponca City in Noble and Pawnee Counties, Oklahoma (Figure 1). The Grease Creek basin that Sooner Lake impounds
More informationMIDDLE FORK RESERVOIR Wayne County 2004 Fish Management Report. Christopher C. Long Assistant Fisheries Biologist
MIDDLE FORK RESERVOIR Wayne County 2004 Fish Management Report Christopher C. Long Assistant Fisheries Biologist FISHERIES SECTION INDIANA DEPARTMENT OF NATURAL RESOURCES DIVISION OF FISH AND WILDLIFE
More informationOverview of Recreational Pond Management
Overview of Recreational Pond Management extension November 13 th 2013 Forrest Wynne State Extension Specialist for Aquaculture Kentucky State University Ponds are built for some of the following purposes:
More informationAnnual monitoring of Moe Pond in conjunction with bio-manipulation
Annual monitoring of Moe Pond in conjunction with bio-manipulation Zachary R. Diehl 1 and Nicholas J. Muehlbauer 2 Introduction Moe Pond (Figure 1) is a 38 acre man-made polymictic pond located near Cooperstown,
More informationBIG MARINE LAKE, WASHINGTON COUNTY: 2017 AQUATIC VEGETATION REPORT
BIG MARINE LAKE, WASHINGTON COUNTY: 2017 AQUATIC VEGETATION REPORT Report by the Invasive Species Program Division of Ecological and Water Resources Minnesota Department of Natural Resources Lake: Big
More informationEcoLogic Memorandum. TO: Ben Brezell; EDR FROM: Mark Arrigo RE: Possible Impacts of Dredging Snooks Pond DATE: 6/4/07
EcoLogic Memorandum TO: Ben Brezell; EDR FROM: Mark Arrigo RE: Possible Impacts of Dredging Snooks Pond DATE: 6/4/07 Background EDR P.C. (EDR) has been contracted by a landowner to assess the feasibility
More informationShallow Lake Management Strategies. Steve McComas Blue Water Science Shallow Lakes Forum April 2014
Shallow Lake Management Strategies Steve McComas Blue Water Science Shallow Lakes Forum April 2014 Shallow Lakes and Ponds Are Similar Shallow Lake Goal: Clear water and macrophytes. Clear Turbid Aquatic
More informationA Biotic and Hydrologic Assessment of Honeycut Springs
A Biotic and Hydrologic Assessment of Honeycut Springs Description Honeycut springs issue at approximately 1,040 ft asl from a limestone ledge lined with maidenhair fern (Adiantum capillus-veneris) in
More informationNicholas Brown. 31 Bennett Rd Wolfeboro NH Application submitted
Nicholas Brown 31 Bennett Rd Wolfeboro NH 03894 603-856-5454 Nick4634@gmail.com Application submitted 8-12-2017 Description of proposed project A. General Methodology The site located approximately 600
More informationEurasian Water-milfoil Bed Mapping Survey Red Lake (WBIC: ) Douglas County, Wisconsin
Eurasian Water-milfoil Bed Mapping Survey Red Lake (WBIC: 2492100) Douglas County, Wisconsin Red Lake Eurasian water-milfoil with >12 leaflet pairs/limp whorls out of water EWM Beds on Red Lake 10/2/16
More informationCurrent Status and Management Recommendations for the Fishery in the Cloverleaf Chain of Lakes
Current Status and Management Recommendations for the Fishery in the Cloverleaf Chain of Lakes Jason Breeggemann Senior Fisheries Biologist Wisconsin Department of Natural Resources Outline DNR fisheries
More informationFisheries Survey of Saratoga Lake
Fisheries Survey of Saratoga Lake 7- Mark D. Cornwell Kevin Poole State University of New York College of Agriculture & Technology Department of Fisheries & Wildlife Cobleskill, NY ABSTRACT: This survey
More informationThe benthic community of Owasco Lake as an indicator of lake ecosystem health
The benthic community of Owasco Lake as an indicator of lake ecosystem health Jim Watkins, Lars Rudstam, Ed Mills, and Mark Leopold Cornell Biological Field Station, 9 Shackleton Point Road, Bridgeport,
More informationEcological Enhancement of a Constructed Beach using ECOncrete Tide Pools: Preliminary Report
Ecological Enhancement of a Constructed Beach using ECOncrete Tide Pools: Preliminary Report October 2014 Background Man-made coastal defense structures such as breakwaters, revetments, and riprap belts
More informationEFFECTS OF ELECTRIC FISHING ON THE INVERTEBRATE FAUNA OF A NEW ZEALAND STREAM
97] EFFECTS OF ELECTRIC FISHING ON THE INVERTEBRATE FAUNA OF A NEW ZEALAND STREAM CHRIS R. FOWLES* Fisheries Laboratory, Ministry of Agriculture and Fisheries, Christchurch, New Zealand (Received August
More information2015 Macrophyte Survey Results
Invasive Macrophyte Survey Pilot 2015 2015 Macrophyte Survey Results COMPLETED WITH SUPPORT FROM: Acknowledgments The Invasive Plant Monitoring Program was made possible through the support of Alberta
More informationCompilation of alewife (Alosa pseudoharengus) trap net catch in Rat Cove, Otsego Lake,
Compilation of alewife (Alosa pseudoharengus) trap net catch in Rat Cove, Otsego Lake, 1989-22 Michael S. Gray 1 and John R. Foster 2 INTRODUCTION Trap netting in the eulittoral area of Rat Cove began
More informationINDICATOR BENTHIC MACROINVERTEBRATE SPECIES AND THEIR CHARACTERISTICS
Coelenterata (Hydras) Turbellaria (Flatworms) A tube with tentacles Reproduces asexually by budding Movement: sessile, attached or fixed, not free moving Colour: clear to whitish Flattened shape Distinct
More informationMISSISSIPPI MAKEOVER A Plan for Restoration, Just Around the Bend
MISSISSIPPI MAKEOVER A Plan for Restoration, Just Around the Bend Interim Report Card 2013 Project coordinated by the Dakota County Soil and Water Conservation District and sponsored by the Minnesota Pollution
More informationO/<. i4--' ~y~ /1_- / ~igan \ DEER PARK WETLANDS BIOLOGICAL MONITORING PROGRAM Annual Report
DEER PARK WETLANDS BIOLOGICAL MONITORING PROGRAM 1991 Annual Report Submitted to: Pasco County Public Works and Utilities 7536 State Street New Port Richey, FL 34654 Submitted by: Mote Marine laboratory
More informationBig Spring Creek Habitat Enhancement and Fishery Management Plans
Big Spring Creek Habitat Enhancement and Fishery Management Plans November 5, 2012 Big Spring Events and Activities Center Newville, PA Charlie McGarrell Regional Habitat Biologist Pennsylvania Fish and
More informationSize, Age and Growth ofnesting Male Pumpkinseed Sunfish (Lepomis gibbosus) in Rat Cove, Otsego Lake, NY
126 Size, Age and Growth ofnesting Male Pumpkinseed Sunfish (Lepomis gibbosus) in Rat Cove, Otsego Lake, NY John R. O'Connor l, John R. Foster, John Urban 3, and Jim Hakala 4 ABSTRACT Male pumpkinseed
More informationHydroacoustic survey of Otsego Lake, 2004
Hydroacoustic survey of Otsego Lake, 2004 Thomas E. Brooking 1 Mark D. Cornwell 2 INTRODUCTION Fishery managers must often rely on uncertain information regarding abundance and distribution of offshore
More informationDRAFT AMENDMENT 1. Introduction
DRAFT AMENDMENT 1 Aquatic Plant Management Plan, Yahara River and Upper Mud Lake, Lower Rock River Basin, Dane County Wisconsin Approved by the Dane County Lakes and Watershed Commission on and by the
More informationWinter Drawdown Issues of Concern
Winter Drawdown Issues of Concern Wetland Connectivity Amphibians Fisheries Winter Drawdown Wetland Connectivity Wetland complex near Osprey Creek is not responsive to lake level Wetland at upper end of
More informationHabitat Fact Sheets. Rocky habitats are dominated by seaweeds and often mussels, which rely on the rocks for attachment.
Habitat Fact Sheets Habitats in the Gulf of Maine serve many important roles for the environment and for humans as well. These include: cycling nutrients, filtering pollution, trapping sediments, storing
More informationResource Partitioning and Life History Patterns Among Salmonids in the Estuarine Habitat Mosaic
Resource Partitioning and Life History Patterns Among Salmonids in the Estuarine Habitat Mosaic Bethany Craig, Chris Eaton, and Si Simenstad University of Washington May 26, 2010 c/o WA DOE Salmon in the
More information2006 Photographic Atlas Aquatic Macroinvertebrates of Piasa Watershed Creeks and Ponds
2006 Photographic Atlas Aquatic Macroinvertebrates of Piasa Watershed Creeks and Ponds Dr. Patrick J. Dailey Lewis and Clark Community College 1 Table of Contents Phylum Annelida Page 3 Phylum Arthropoda
More informationGRASS CARP SPAWNING IN LAKE ERIE TRIBUTARIES: WHEN AND WHERE?
GRASS CARP SPAWNING IN LAKE ERIE TRIBUTARIES: WHEN AND WHERE? Nicole R. King 1, Patrick M. Kocovsky 2, Christine M. Mayer, 1 Song S. Qian 1 1. University of Toledo Dept. Environmental Sciences and Lake
More informationTrait characteristics determine pyrethroid sensitivity in non-standard test species of freshwater
Supporting Information Trait characteristics determine pyrethroid sensitivity in non-standard test species of freshwater macroinvertebrates A reality check Peter Wiberg-Larsen, Daniel Graeber, Esben Astrup
More informationTwo types of physical and biological standards are used to judge the performance of the Wheeler North Reef 1) Absolute standards are measured against
1 Two types of physical and biological standards are used to judge the performance of the Wheeler North Reef 1) Absolute standards are measured against fixed value at Wheeler North Reef only 2) Relative
More informationCrooked Lake Oakland County (T4N, R9E, Sections 3, 4, 9) Surveyed May James T. Francis
Michigan Department of Natural Resources Status of the Fishery Resource Report No. 2004-1, 2004 Crooked Lake Oakland County (T4N, R9E, Sections 3, 4, 9) Surveyed May 2002 James T. Francis Environment Crooked
More informationSOCIETAL GOALS TO DETERMINE ECOSYSTEM HEALTH: A FISHERIES CASE STUDY IN GALVESTON BAY SYSTEM, TEXAS
SOCIETAL GOALS TO DETERMINE ECOSYSTEM HEALTH: A FISHERIES CASE STUDY IN GALVESTON BAY SYSTEM, TEXAS Anthony S. Pait, NOAA, National Centers for Coastal Ocean Science Thomas P. O Connor, David R. Whitall,
More informationOsoyoos Lake Aquatic Plant Mapping
Osoyoos Lake Aquatic Plant Mapping AquaTechnex, LLC Presented to Okanogan County NWCB by PO Box 30824 Bellingham WA, 98228 www.aquatechnex.com Introductions Myriophyllum spicatum or Eurasian Milfoil has
More informationFish, Benthic-Macroinvertebrate, and Stream- Habitat Data From Two Estuaries Near Galveston Bay, Texas,
In cooperation with the Houston-Galveston Area Council Fish, Benthic-Macroinvertebrate, and Stream- Habitat Data From Two Estuaries Near Galveston Bay, Texas, 2 21 Open-File Report 2 24 U.S. Department
More informationManual of Fisheries Survey Methods II: with periodic updates. Chapter 22: Guidelines for Sampling Warmwater Rivers with Rotenone
Manual of Fisheries Survey Methods II: with periodic updates : Guidelines for Sampling Warmwater Rivers with Rotenone P. W. Seelbach, G. L. Towns, and D. D. Nelson Suggested citation: Seelbach, Paul W.,
More informationFACT SHEET MCGREGOR LAKE RESTORATION HABITAT PROJECT POOL 10, UPPER MISSISSIPPI RIVER, WISCONSIN ENVIRONMENTAL MANAGEMENT PROGRAM
FACT SHEET MCGREGOR LAKE RESTORATION HABITAT PROJECT POOL 10, UPPER MISSISSIPPI RIVER, WISCONSIN ENVIRONMENTAL MANAGEMENT PROGRAM LOCATION McGregor Lake is located within a mid-river island in Pool 10
More informationINLAND LAKE MANAGEMENT REPORT FY Spring 2008
INLAND LAKE MANAGEMENT REPORT FY 2008 Spring 2008 Prepared by Robert O. Andress District Fisheries Biologist E. Daniel Catchings District Fisheries Supervisor Kevin W. Baswell District Biologist Aide Department
More informationJason Blackburn, Paul Hvenegaard, Dave Jackson, Tyler Johns, Chad Judd, Scott Seward and Juanna Thompson
Alberta Conservation Association (ACA) Date: 2014-2015 Project Name: Owl River Walleye and Aquatic Habitat Assessment Fisheries Program Manager: Peter Aku Project Leader: Tyler Johns Primary ACA staff
More informationlocated Let s go fishing Hydrilla
Our Lake of the Month for November is Lake August (set your GPS to 27.2750-81.4136). The elevation of Lake August is 102.5. Lake August is a 52 acre dredge hole lake (man-made from a former wetland; see
More informationMichigan Department of Natural Resources Status of the Fishery Resource Report Page 1
Michigan Department of Natural Resources 2007-33 Status of the Fishery Resource Report Page 1 Grand Sable Lake Alger County, T49N, R14W, Sec. Many Lake Superior watershed, last year surveyed 2004 James
More informationEscaped Rainbow Trout (Onchorhyncus mykiss) Management 2018 Operational Plan
Escaped Rainbow Trout (Onchorhyncus mykiss) Management 2018 Operational Plan Internal Document Last updated 9 th May 2018 INTRODUCTION Following the escape of a significant number of rainbow trout (Onchorhyncus
More informationEurasian water-milfoil (Myriophyllum spicatum) SCUBA Dive Monitoring Survey Sand Bar Lake WBIC: Bayfield County, Wisconsin
Eurasian water-milfoil (Myriophyllum spicatum) SCUBA Dive Monitoring Survey Sand Bar Lake WBIC: 2494900 Bayfield County, Wisconsin 6ft EWM Towers with Rooted Branch Preparing to Fall Off (Berg 2016) EWM
More informationFrom Phosphorus to Fish: Beneficial Use of Excess Nutrients
FLOATINGISLANDINTERNATIONAL From Phosphorus to Fish: Beneficial Use of Excess Nutrients Project Location: Shepherd, Montana Fishing can be the primary method for transitioning excess nonpoint source nutrients
More informationRecent changes in invasive zebra mussel abundance in Gull Lake. Jeffrey D. White GLQO Annual Meeting 12 August 2014
Recent changes in invasive zebra mussel abundance in Gull Lake Jeffrey D. White GLQO Annual Meeting 12 August 2014 Zebra mussels: background Introduced: 1980s from Europe/Asia Transported: ballast water
More informationThe Fish Fauna of Cranberry Bog, Town of Burlington, Otsego County, N.Y.
80 The Fish Fauna of Cranberry Bog, Town of Burlington, Otsego County, N.Y. Steven M. Foster* ABSTRACT In June 1995 a baseline fish survey of Cranberry Bog was conducted in order to identify the species
More informationMonitoring the Moe Pond ecosystem and population estimates of largemouth bass (Micropterus salmoides) post unauthorized introduction
Monitoring the Moe Pond ecosystem and population estimates of largemouth bass (Micropterus salmoides) post unauthorized introduction Stephen G. Stowell 1 ABSTRACT A study of Moe Pond, located in Otsego
More informationAquatic Plant Surveys in Donner Lake State Park, California: Report to California State Parks. Final Draft
Aquatic Plant Surveys in Donner Lake State Park, California: 2017 Report to California State Parks Final Draft Brant Allen, Katie Senft, and Brandon Berry UC Davis Tahoe Environmental Research Center February
More informationNURSERY POND Fish Management Report. Jason C. Doll Assistant Fisheries Biologist
NURSERY POND 2004 Fish Management Report Jason C. Doll Assistant Fisheries Biologist FISHERIES SECTION INDIANA DEPARTMENT OF NATURAL RESOURCES DIVISION OF FISH AND WILDLIFE I.G.C. South, Room W273 402
More informationHudson River Food Webs
Name Date Part 1: Introduction to the In part one, you will learn about food chains in one of the major environments in the Hudson River: marsh, brackish channel, freshwater channel, or freshwater shallows.
More informationATTACHMENT F. Minnesota Department of Natural Resources. Marsh Lake Ecosystem Restoration Project
ATTACHMENT F Minnesota Department of Natural Resources Marsh Lake Ecosystem Restoration Project Mussel Rescue and Translocation Plan for Pomme de Terre River Restoration (Prepared June, 2016) Attachment
More information