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N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

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Page 1: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

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"

"

!(

Reaville

Ringoes

Neshanic River

FIBI023FIBI023

£¤202

!(12

!(31

!(179!(31

Neshanic River - FIBI023

IBI Ratings!( Excellent!( Good!( Fair!( Poor

0 2 41 Miles ±!( FIBI Sampling Location

Small Streams (1st and 2nd Order)Large Streams (3rd Order and Larger)

! !

Page 2: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

SUMMARY OF RESULTS – FIBI023

1. Stream Name: Neshanic River2. Sampling Date: 7/13/20063. Sampling Location: Along Kuhl Road4. Municipality Raritan Twp.5. County: Hunterdon6. Watershed Management Area: 87. Contributing Drainage Area (Sq. Mi.): 23.18. Electrofishing Gear: Barge9. FIBI Score and Rating: Round 1* Fair (36); Round 2 Fair (34)

10. Habitat Score and Rating: Round 1 Sub-Optimal (130); Round 2 Sub-Optimal (134)11. Fishable Species Present: Yes12. Relevant AMNET1 Station Data:

Proximity of FIBI station to AMNET station: 1.0mi upstream AN0333AMNET Rating: 1994 – Moderate; 1999 – Moderate; 2004 – Moderate

13. Stream Chemistries:Dissolved Oxygen (mg/l) 8.03Temperature 0C. 22.63pH 7.06Conductivity (μmhos/cm) 272

14. Length of Stream Sampled: 150m15. Water Clarity: Slightly Turbid16. Average Open Forest Canopy: 18%17. Discharge: 13.1 cfs18. Substrate: 20% Gravel/Sand, 20% Cobble, 40% Boulder, 20% Bedrock19. Habitat: 50% Riffle, 30% Run, 20% Pool20. Snags: Yes21. Periphyton: Heavy22. Submerged Aquatic Vegetation: No23. Outfalls: 224. Number of Fish Species Identified: 2025. Total Number of Fish Collected: 1,14226. Number of Fish With Anomalies: 627. Other Observations: Severe bank erosion between 50-100 meters.

1 AMNET is the acronym for the DEP’s ambient benthic macroinvertebrate monitoring network – a series of 820 monitoring stationslocated throughout the state’s waterways that collects data on the health of bottom dwelling stream fauna which in turn is used toassess general water quality* Round 1 data was scored prior to the FIBI metric recalibration.

Page 3: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

!

!!A

!A

® Kuhl Road

FIBI023NESHANIC RIVERALONG KUHL ROADRARITAN TWP., HUNTERDON COUNTY

County GolfCourse

& 0 50 100 150Meters

Legend

! Finish! Start

!A Outfall

Severe Bank Erosion

® Directionof FlowFIBI Reach

Page 4: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

FIBI023-Neshanic River @ Kuhl Road Excellent Good Fair PoorDate Sampled - 7/13/2006

Score# of Fish Species 5

# of Benthic Insectivorous Species (BI) 5(excluding White Suckers and Bullheads)

# of Trout and Centrarchid Species 5(excluding Green Sunfish and Bluegill)

# of Intolerant Species (IS) 3

Proportion of Tolerant Individuals 1

Proportion of Individuals as Generalists 1

Proportion of Individuals as Insectivorous Cyprinids 1

Proportion of Individuals as Trout *whichever gives better scoreORProportion of Individuals as Piscivores (excluding American Eel)* 3

# of Individuals in Sample 5(excluding Tolerant Species)

Proportion of Individuals w/disease/anomalies 5(excluding blackspot)

Total 34

45-50 Excellent37-44 Good29-36 Fair10-28 Poor

Stream Rating

Page 5: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

HABITAT ASSESSMENT FOR HIGH GRADIENT STREAMS Neshanic River (FIBI023) – 7/13/06 Condition Category

Optimal Suboptimal Marginal Poor 1. Epifaunal Substrate

/Available Cover

Greater than 70% of substrate favorable for epifaunal colonization and fish cover; mix of snags, submerged logs, undercut banks, cobble or other stable habitat and at stage to allow full colonization potential (i.e., logs/snags that are not new fall and not transient).

40-70% mix of stable habitat; well-suited for full colonization potential; adequate habitat for maintenance of populations; presence of additional substrate in the form of newfall, but not yet prepared for colonization (may rate at high end of scale).

20-40% mix of stable habitat; habitat availability less than desirable; substrate frequently disturbed or removed.

Less than 20% stable habitat; lack of habitat is obvious; substrate unstable or lacking.

SCORE 16 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 2. Embeddedness

Gravel, cobble, and boulder particles are 0-25% surrounded by fine sediment. Layering of cobble provides diversity of niche space

Gravel, cobble, and boulder particles are 25-50% surrounded by fine sediment.

Gravel, cobble, and boulder particles are 50-75% surrounded by fine sediment.

Gravel, cobble, and boulder particles are more than 75% surrounded by fine sediment.

SCORE 11 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 3. Velocity/Depth Regimes

All 4 velocity/depth regimes present (slow-deep, slow-shallow, fast-deep, fast-shallow). (slow is <0.3 m/s, deep is >0.5 m)

Only 3 of the 4 regimes present (if fast-shallow is missing, score lower than if missing other regimes).

Only 2 of the 4 habitat regimes present (if fast-shallow or slow-shallow are missing, score low).

Dominated by 1 velocity / depth regime (usually slow-deep).

SCORE 20 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 4. Sediment Deposition

Little or no enlargement of islands or point bars and less than 5% (<20% for low-gradient streams) of the bottom affected by sediment deposition.

Some new increase in bar formation, mostly from gravel, sand or fine sediment; 5-30% (20-50% for low-gradient) of the bottom affected; slight deposition in pools.

Moderate deposition of new gravel, sand or fine sediment on old and new bars; 30-50% (50-80% for low-gradient) of the bottom affected; sediment deposits at obstructions, constrictions, and bends; moderate deposition of pools prevalent.

Heavy deposits of fine material, increased bar development; more than 50% (80% for low-gradient) of the bottom changing frequently; pools almost absent due to substantial sediment deposition.

SCORE 8 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 5. Channel Flow Status

Water reaches base of both lower banks, and minimal amount of channel substrate is exposed.

Water fills >75% of the available channel; or <25% of channel substrate is exposed.

Water fills 25-75% of the available channel, and/or riffle substrates are mostly exposed.

Very little water in channel and mostly present as standing pools.

SCORE 19 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 6. Channel Alteration

Channelization or dredging absent or minimal; stream with normal pattern.

Some channelization present, usually in areas of bridge abutments; evidence of past channelization, i.e., dredging, (greater than past 20 yr) may be present, but recent channelization is not present.

Channelization may be extensive; embankments or shoring structures present on both banks; and 40 to 80% of stream reach channelized and disrupted.

Banks shored with gabion or cement; over 80% of the stream reach channelized and disrupted. In stream habitat greatly altered or removed entirely.

SCORE 16 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 7. Frequency of Riffles (or

bends)

Occurrence of riffles relatively frequent; ratio of distance between riffles divided by width of the stream <7:1 (generally 5 to 7); variety of habitat is key. In streams where riffles are continuous, placement of boulders or other large, natural obstruction is important.

Occurrence of riffles infrequent; distance between riffles divided by the width of the stream is between 7 to 15.

Occasional riffle or bend; bottom contours provide some habitat; distance between riffles divided by the width of the stream is between 15 to 25.

Generally all flat water or shallow riffles; poor habitat; distance between riffles divided by the width of the stream is a ratio of >25.

SCORE 11 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 8. Bank Stability (score

each bank) Note: determine left or right side by facing downstream.

Banks stable; evidence of erosion or bank failure absent or minimal; little potential for future problems. <5% of bank affected.

Moderately stable; infrequent, small areas of erosion mostly healed over. 5-30% of bank in reach has areas of erosion.

Moderately unstable; 30-60% of bank in reach has areas of erosion; high erosion potential during floods.

Unstable; many eroded areas; "raw" areas frequent along straight sections and bends; obvious bank sloughing; 60-100% of bank has erosional scars.

SCORE 7 (LB) Left 10 9 8 7 6 5 4 3 2 1 0 SCORE 5 (RB) Right 10 9 8 7 6 5 4 3 2 1 0 9. Bank Vegetative

Protection (score each bank)

More than 90% of the streambank surfaces and immediate riparian zone covered by native vegetation, including trees, under story shrubs, or nonwoody macrophytes; vegetative disruption through grazing or mowing minimal or not evident; almost all plants allowed to grow naturally.

70-90% of the streambank surfaces covered by native vegetation, but one class of plants is not well-represented; disruption evident but not affecting full plant growth potential to any great extent; more than one-half of the potential plant stubble height remaining.

50-70% of the streambank surfaces covered by vegetation; disruption obvious; patches of bare soil or closely cropped vegetation common; less than one-half of the potential plant stubble height remaining.

Less than 50% of the streambank surfaces covered by vegetation; disruption of streambank vegetation is very high; vegetation has been removed to 5 centimeters or less in average stubble height.

SCORE 6 (LB) Left 10 9 8 7 6 5 4 3 2 1 0 SCORE 7 (RB) Right 10 9 8 7 6 5 4 3 2 1 0 10. Riparian Vegetative

Zone Width (score each bank riparian zone)

Width of riparian zone >18 meters; human activities (i.e., parking lots, roadbeds, clear-cuts, lawns, or crops) have not impacted zone.

Width of riparian zone 12-18 meters; human activities have impacted zone only minimally.

Width of riparian zone 6-12 meters; human activities have impacted zone a great deal.

Width of riparian zone <6 meters: little or no riparian vegetation due to human activities.

SCORE 3 (LB) Left 10 9 8 7 6 5 4 3 2 1 0 SCORE 5 (RB) Right 10 9 8 7 6 5 4 3 2 1 0

HABITAT SCORES VALUE

OPTIMAL 160 − 200

SUB-OPTIMAL 110 − 159

MARGINAL 60 − 109

POOR < 60

HABITAT SCORE

134

Page 6: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

FIBI023-R2 Neshanic River 07/13/2006

Common Name Scientific Name Abundance Size Range (inches) White Sucker Catostomus commersoni 288 - Banded Killifish Fundulus diaphanus 167 - Redbreast Sunfish Lepomis auritus 108 2.4 - 6.3 Tessellated Darter Etheostoma olmstedi 89 - Green Sunfish Lepomis cyanellus 88 2.0 - 5.0 Bluegill Lepomis macrochirus 86 2.2 - 3.7 Spotfin Shiner Cyprinella spiloptera 82 - Common Shiner Luxilus cornutus 59 - Pumpkinseed Lepomis gibbosus 58 2.7 - 4.0 Rock Bass Ambloplites rupestris 33 2.4 - 6.7 American Eel Anguilla rostrata 33 - Largemouth Bass Micropterus salmoides 12 2.0 - 2.6 Longnose Dace Rhinichthys cataractae 8 - Yellow Bullhead Ameiurus natalis 8 4.8 - 7.3 Blacknose Dace Rhinichthys atratulus 7 - Smallmouth Bass Micropterus dolomieu 7 5.0 - 8.5 Margined Madtom Noturus insignis 4 - Spottail Shiner Notropis hudsonius 3 - Satinfin Shiner Cyprinella analostana 1 - Golden Shiner Notemigonus crysoleucas 1 -

Page 7: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

Species Identified at Neshanic River (FIBI023)(Not to Scale)

White Sucker

Satinfin Shiner

Blacknose Dace

Yellow BullheadTessellated Darter

Redbreast Sunfish

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Species Identified at Neshanic River (FIBI023)(Not to Scale)

Rockbass

Common Shiner

Green Sunfish

Banded Killifish Longnose Dace

Margined Madtom

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Species Identified at Neshanic River (FIBI023)(Not to Scale)

American EelPumpkinseed

Spottail Shiner Bluegill

Smallmouth Bass Largemouth Bass

Page 10: N eshan ic R v r - F IB 023 · R eavi l Ringoes N eshan ic R v r FFI IBBI002233 £¤ 20!(12!(31!(179!(31N eshan ic R v r - F IB 023 IB Ratings!(Exc el nt!(G od!(Fair!(P or 0 1 2 4

Spotfin Shiner

Species Identified at Neshanic River (FIBI023)(Not to Scale)

Golden Shiner


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