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Watershed Conservation Plan - Destination Erie

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Table 6.2. Pennsylvania Vertebrate Animal Species of Special Concern with Documented Occurrences in<br />

the Ohio Portion of Conneaut Creek, West of the Study Area<br />

Rank State Status Pennsylvania Data a<br />

Scientific Name<br />

Common Name<br />

Global<br />

State<br />

Current<br />

Proposed<br />

Present<br />

Listed<br />

Listed Streams<br />

Ameiurus melas black bullhead G5 S1 PE PE yes no Elk<br />

Amia calva bowfin G5 S2S3 PC CR no yes —<br />

Clemmys guttata spotted turtle G5 S3 — — — no —<br />

Culaea inconstans brook stickleback G5 S3 PC C yes no Elk<br />

Ichthyomyzon fossor northern brook lamprey G4 S1 PE PE — no —<br />

Ichthyomyzon unicuspis silver lamprey G5 SNR — PX yes yes —<br />

Ictiobus bubalus smallmouth buffalo G5 S2S3 PT PT no yes —<br />

Lampetra appendix American brook lamprey G4 S3 PC CR yes no Walnut<br />

Lepisosteus osseus longnose gar G5 S3 PC CR no yes —<br />

Lythrurus umbratilis redfin shiner G5 S1 PE PE — no —<br />

Noturus miurus brindled madtom G5 S2 PT PT yes no —<br />

Phoxinus erythrogaster southern redbelly dace G5 S1 PT PT no no —<br />

Thamnophis sauritus eastern ribbon snake G5 S3S4 — — — no —<br />

Umbra limi central mudminnow G5 S3 PC C — no —<br />

Note: (1) data for the Pennsylvania portion of the Conneaut Creek subwatershed.<br />

streams (see Figure 6.2b). Most of the fish community surveys of study area streams have not employed<br />

sufficient sampling frequency and intensity to adequately represent all fish species likely to be present.<br />

The ACOE (1979) fish sampling data for Raccoon, Turkey, and Conneaut Creeks (see Figure 6.2c)<br />

indicates that much greater fish species richness is detected with sampling over several seasons (1977)<br />

than with single-season sampling (1978). Comparing the data values reported in Figure 6.2c to those in<br />

Figures 6.2a and 6.2b for Raccoon and Conneaut Creeks suggests that most of the study area's past<br />

inventories of fish communities have probably overlooked some rare species that may have been present.<br />

The foregoing analysis indicates that a comprehensive modern survey is warranted for the fish<br />

communities in the study area's biologically diverse western streams, to clarify the status of PNHP-listed<br />

species.<br />

The study area's streams have recognized importance as spawning areas for Lake <strong>Erie</strong> fishes (Table<br />

6.3, Figure 6.3). Streams east of the City of <strong>Erie</strong> were known to support relatively few species of<br />

spawning fishes, and the larger streams on the west side appear to support the greatest variety of<br />

spawning fishes (see Figure 6.3). The utilization of smaller streams—Raccoon and Turkey Creeks—near<br />

the Pennsylvania–Ohio line by a great variety of spawning fish species (see Figure 6.3) has been<br />

attributed to the fact that these streams meet the lake in a low gradient "lacustuary" protected from wave<br />

action by a sand/gravel bar feature at their mouths (Roger Kenyon, Lake <strong>Erie</strong> Research Unit,<br />

Pennsylvania Fish & Boat Commission, Fairview, Pennsylvania, personal communication December 2,<br />

2006). Spawning activity by fishes is likely different now than at the time Goodyear et al.'s (1982)<br />

spawning atlas was published; for example, Table 6.3 includes species that are currently considered<br />

extirpated in Pennsylvania waters (see Table 6.1). Furthermore, the near-shore ecology of Lake <strong>Erie</strong> has<br />

105

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