Industrial stormwater facility
4 19I021497 · Notice of Intent · Culver City, Los Angeles
Official
Hydrologic
Official facility coordinate plotted against the official 2026 impaired-water geometry.
303(d) context
Grouped by derived geographic association class.
River & Stream · Integrated Report category 5 · TMDL required
Listed pollutants / stressors (22) Aluminum, Bifenthrin, Chlordane, Copper, Cyanide, Cyfluthrin +16 more
Wetland, Tidal · Integrated Report category 4a · TMDL approved by USEPA
Listed pollutants / stressors (4) Exotic Vegetation, Habitat alterations, Reduced Tidal Flushing, Trash
River & Stream · Integrated Report category 5 · TMDL required
Listed pollutants / stressors (4) Copper, Indicator Bacteria, Lead, Zinc
Lake & Reservoir · Integrated Report category 4a · TMDL approved by USEPA
Listed pollutants / stressors (8) Algae, Chlordane, Dieldrin, Eutrophic, Odor, PCBs (Polychlorinated biphenyls) +2 more
Bay & Harbor · Integrated Report category 5 · TMDL required
Listed pollutants / stressors (11) alpha-Endosulfan (Endosulfan 1), Chlordane, Copper, DDT (Dichlorodiphenyltrichloroethane), Dieldrin, Indicator Bacteria +5 more
River & Stream · Integrated Report category 4a · TMDL approved by USEPA
Listed pollutants / stressors (5) Copper, Indicator Bacteria, Lead, Selenium, Zinc
Associations are calculated from official facility coordinates, USGS HUC12 boundaries, and official 2026 impaired-water geometry. They do not establish a discharge connection or causation.
Water Board-stated TMDL waste load allocations applied to this industrial permit in SMARTS.
No SMARTS TMDL requirement is recorded for this WDID. In the statewide TMDL export only permits in Regions 4, 8 and 9 currently carry industrial TMDL requirements, so an absence here is not a statement that the facility discharges to an unimpaired water.
Official monitoring
Self-reported industrial stormwater sampling results as submitted by the discharger to SMARTS.
Loading reported results…
| Sample date | Location | Parameter | Result | Units | Event |
|---|---|---|---|---|---|
| 2026-02-16 | Earplugs | Copper, Dissolved | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Copper, Dissolved | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Copper, Dissolved | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Lead | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Lead | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Lead | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Oil and Grease | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Oil and Grease | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Oil and Grease | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | pH | 7.7 | SU | Qualifying Storm Event |
| 2026-02-16 | Earplugs | pH | 7.7 | SU | Qualifying Storm Event |
| 2026-02-16 | Earplugs | pH | 7.7 | SU | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Total Suspended Solids (TSS) | 4.3 | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Total Suspended Solids (TSS) | 4.3 | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Total Suspended Solids (TSS) | 4.3 | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Zinc, Dissolved | .031 | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Zinc, Dissolved | .031 | mg/L | Qualifying Storm Event |
| 2026-02-16 | Earplugs | Zinc, Dissolved | .031 | mg/L | Qualifying Storm Event |
| 2026-02-16 | Extrusion | Copper, Dissolved | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Extrusion | Copper, Dissolved | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Extrusion | Copper, Dissolved | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Extrusion | Lead | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Extrusion | Lead | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Extrusion | Lead | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
| 2026-02-16 | Extrusion | Oil and Grease | ND —(non-detect / est.) | mg/L | Qualifying Storm Event |
Monitoring rows are official self-reported SMARTS submissions, joined to this facility by WDID. California Stormwater Intelligence does not restate, correct, average or evaluate reported values, and no benchmark comparison or violation determination is made.
YDOS-derived
Reported SMARTS analytical results compared against the Numeric Action Levels of the Industrial General Permit version in effect for each reporting year (July 1 – June 30).
| Parameter | NAL type | Calculated value | NAL | Result | Samples used | Method |
|---|---|---|---|---|---|---|
Oil and Grease oil_grease | Instantaneous maximum | —0 samples above | 25 mg/L | At or below NALNo eligible result in this reporting year was outside the instantaneous maximum NAL. | 27 eligible24 non-detect as zero | count of eligible effluent results outside the instantaneous maximum NAL within the July 1 - June 30 reporting year |
pH ph | Instantaneous maximum | —0 samples above | 6 – 9 pH units | Within NAL rangeNo eligible result in this reporting year was outside the instantaneous maximum NAL. | 27 eligible | count of eligible effluent results outside the instantaneous maximum NAL within the July 1 - June 30 reporting year |
Total Suspended Solids (TSS) tss | Instantaneous maximum | —0 samples above | 400 mg/L | At or below NALNo eligible result in this reporting year was outside the instantaneous maximum NAL. | 27 eligible | count of eligible effluent results outside the instantaneous maximum NAL within the July 1 - June 30 reporting year |
YDOS-derived overlap
Parameters where this facility has an NAL exceedance in at least one reporting year and the geographically associated waterbody carries a 303(d) listing for the same pollutant.
pHMonitoringAbove NAL303(d) impairmentBallona Creek
4 reporting years above the instantaneous maximum NAL, most recently RY 2021 · 1 303(d) listing · association: derived receiving water (medium confidence)
pHMonitoringAbove NAL303(d) impairmentEcho Park Lake
4 reporting years above the instantaneous maximum NAL, most recently RY 2021 · 1 303(d) listing · association: derived watershed association (low confidence)
ZincMonitoringAbove NAL303(d) impairmentBallona Creek
1 reporting year above the annual NAL, most recently RY 2021 · 1 303(d) listing · association: derived receiving water (medium confidence)
ZincMonitoringAbove NAL303(d) impairmentCentinela Creek
1 reporting year above the annual NAL, most recently RY 2021 · 1 303(d) listing · association: derived watershed association (low confidence)
ZincMonitoringAbove NAL303(d) impairmentMarina del Rey Harbor
1 reporting year above the annual NAL, most recently RY 2021 · 1 303(d) listing · association: derived watershed association (low confidence)
ZincMonitoringAbove NAL303(d) impairmentSepulveda Canyon
1 reporting year above the annual NAL, most recently RY 2021 · 1 303(d) listing · association: derived watershed association (low confidence)
Overlap is informational co-occurrence between a derived NAL comparison and an official 303(d) listing. It is not evidence that this facility caused or contributed to the impairment.
An NAL exceedance is a permit-defined condition that triggers Exceedance Response Actions under the Industrial General Permit. It is not a violation, an enforcement action, or a Water Board compliance determination. Annual values use the arithmetic average of eligible results with non-detects treated as zero; instantaneous maximum NALs (total suspended solids, oil and grease, pH) are exceeded when two or more eligible results in a reporting year fall outside the level. Rules transcribed from 2014-0057-DWQ as amended by 2015-0122-DWQ ↗ (effective 2015-07-01, superseded 2020-06-30); 2014-0057-DWQ as amended by 2018-0028-DWQ ↗ (effective 2020-07-01).
Provenance