Lost Creek Fillmore
Fish Session #849
- Sample Date
- 7/6/2023
- Timeframe
- 0900-1500
- Reach Size
- 1500 ft
- Method
- Standard Wadeable
- Sample Quality
- Good
- Last Update
- 12/28/2023 1:32:29 PM
This site is on public land, such as a county park, state park, or state-managed wildlife area.
Warm Water
Poor
Kirby, Winn & Link. Sample sites include: 1, 2 & 3. Sites located within Whitewater Canyon owned and managed by the Jones County Conservation Board.
- Identity verification status for this species
- Morphometrics: Length/Weight measurements of individual specimens
- Taxa excluded from species count metrics.
- Click on species name for more information about that species
| Species | Catch | |
|---|---|---|
|
Longnose Dace
Latin: Rhinichthys cataractae
Family: Leuciscidae Tolerance: Sensitive Trophic: Benthic Invertivore Is Exotic: False Is LithoSpawner: False Is Hybrid: False |
68 | |
|
White Sucker
Latin: Catostomus commersonii
Family: Catostomidae Tolerance: Intermediate Trophic: Omnivore Is Exotic: False Is LithoSpawner: False Is Hybrid: False |
42 | |
|
Western Blacknose Dace
Latin: Rhinichthys obtusus
Family: Leuciscidae Tolerance: Intermediate Trophic: Insectivore Is Exotic: False Is LithoSpawner: False Is Hybrid: False |
15 | |
|
Brook Stickleback
Latin: Culaea inconstans
Family: Gasterosteidae Tolerance: Sensitive Trophic: Insectivore Is Exotic: False Is LithoSpawner: False Is Hybrid: False |
13 | |
|
Johnny Darter
Latin: Etheostoma nigrum
Family: Percidae Tolerance: Intermediate Trophic: Benthic Invertivore Is Exotic: False Is LithoSpawner: False Is Hybrid: False |
6 | |
|
Southern Redbelly Dace
Latin: Chrosomus erythrogaster
Family: Leuciscidae Tolerance: Sensitive Trophic: Herbivore Is Exotic: False Is LithoSpawner: False Is Hybrid: False |
3 | |
|
Sand Shiner
Latin: Miniellus stramineus
Family: Leuciscidae Tolerance: Intermediate Trophic: Insectivore Is Exotic: False Is LithoSpawner: False Is Hybrid: False |
1 | |
FIBI Calculation Factors
| Factor | Value |
|---|---|
| Drainage area (mi2) | 8.7300 |
| Log(DA) | 0.9410 |
| Total Fish | 148 |
| Fish per 500 ft | 49 |
| Total Species | 7 |
| # Excluded Species | 0 |
| # Exotic Species | 0 |
| # LMB-BG | 0 |
| Calculation Last Updated | 10/10/2025 10:21:03 AM |
Fish Index of Biotic Integrity
| Metric Name | Value | Score |
|---|---|---|
| Native Species | 7 | 4.46 |
| Sucker Species | 1 | 3.26 |
| Sensitive Species | 3 | 5.58 |
| Benthic Invertivore Species | 2 | 3.54 |
| Top 3 Abundance Percentage | 84.46 | 2.5 |
| Benthic Invertivore Percentage | 50 | 2.5 |
| Omnivore Percentage | 28.38 | 2.5 |
| Top Carnivore Percentage | 0 | 0 |
| Lithophilous Spawner Percentage | 0 | 0 |
| Tolerance Index | 2.16 | 2.5 |
| Adjusted Catch per Unit Effort | 9.87 | 0.99 |
| DELT Percentage Adjustment | 0 | 0 |
FIBI Score Explained
Sites that score between 0 - 25 are considered poor. Fish abundance is usually lower than normal or, if fish are abundant, the collection is dominated by a few tolerant species. The number of native fish species present is low. Sensitive species and habitat specialists are absent or extremely rare. The population is dominated by just a few ubiquitous species that are tolerant of wide-ranging water quality and habitat conditions. Pioneering, introduced and/or short-lived fish species are typically the most abundant types of fish. Fish collected at poor sites often have a higher than normal occurrence of external physical anomalies.
This location has been classified as a survey site. Survey sites are compared to reference sites within the same ecoregion. A reference site represents natural stream qualities that are least disturbed by human activities within the watershed. Reference sites are grouped by ecoregion to establish a benchmark against which these survey streams are compared.
EcoRegion Comparison
Scores for a sampling session are compared against reference sites within the same ecoregion:
| Max | 83 |
| 75th Percentile | 59 |
| Median | 48 |
| 25th Percentile | 38 |
| Min | 10 |
| This Session's Score | 25 |
| Total Reference Site Samples | 105 |
| Mean | 49.02 |
| Standard Deviation | 14.97 |