Bootstrap review report — d7_wd31_los_pinos_river_basin
Generated 2026-08-16 09:02 UTC for Division 7 / Water District 31.
This is a review checklist, not a finished config. Everything below is a suggestion from live DWR data — confirm or correct each section in config.yaml before running this basin for real.
1. Stream-name patterns
Assumed mainstem pattern: LOS PINOS RIVER (highest-count waterSource value). Candidates below by structure count — decide which are real tributaries worth their own centerline vs. noise, and add them to longitudinal.tributary_stream_patterns in priority order (more-specific names, e.g. "WEST FORK X", must precede substrings of themselves, e.g. "X").
| waterSource | structure count |
|---|---|
| LOS PINOS RIVER (assumed mainstem) | 92 |
| BEAVER CREEK | 19 |
| VALLECITO CREEK | 16 |
| GRIMES CREEK | 13 |
| DRY CREEK | 12 |
| TEXAS CREEK | 11 |
| TIFFANY DRAW | 9 |
| NORTH FORK TEXAS CREEK | 8 |
| IGNACIO CREEK | 7 |
| ROCK CREEK | 7 |
| UNDEFINED | 7 |
| LOST CREEK | 6 |
| CARLSON ARROYO | 6 |
| UTE CREEK | 5 |
| BEAR CREEK | 4 |
| SPRING CREEK | 4 |
| WALLACE GULCH | 4 |
| CROWBAR CREEK | 4 |
| BRINKS DRAW | 3 |
| BERRI CREEK | 3 |
| FREEMAN CREEK | 3 |
2. Diversion / return classification
Auto-classified from structureType + name patterns: 217 diversions, 35 returns, 91 unclassified (neither pattern matched — these render as neither on the schematic unless added to return_flow_wdids/force_diversion_wdids or a type is added to the diversion/return type lists).
This layer needs the least manual work — it's the same heuristic the engine uses at runtime. Spot-check a sample rather than reviewing every row; if you have a water-year accounting spreadsheet for this basin, cross-reference it against the 'other' bucket specifically (that's where a real augmentation return with an unusual DWR structureType will hide).
2b. Cross-checked against decreed water rights (CDSS)
47 structure(s) have a decreed water right (CDSS waterrights/netamount) that disagrees with the structureType/name-pattern classification above. Same-agency evidence (DWR/HydroBase), not independent of DWR the way the NLDI topology check is — worth a glance, not an automatic correction.
| wdid | structure | currently | decreed uses suggest | decreed uses |
|---|---|---|---|---|
| 3100651 | VALLECITO VALLEY PMP STA | other | diversion | Commercial, Domestic |
| 3100844 | VALLECITO HYDROELECTRIC | other | diversion | Power Generation |
| 3105000 | WESTERN CONST & DEV CO W | other | diversion | Commercial, Domestic |
| 3105004 | CURRIE WELL | other | diversion | Domestic, Irrigation |
| 3105008 | BISHOP BROTHERS WELL | other | diversion | Commercial, Domestic |
| 3105009 | MARRS AND DOYLE WELL | other | diversion | Domestic |
| 3105022 | SCHROEDER WELL NO 2 | other | diversion | Domestic |
| 3105023 | BEUTEN WELL NO 60708 | other | diversion | Domestic, Stock |
| 3105025 | PINE RIVER IRR DIST WELL | other | diversion | Domestic, Fire |
| 3105028 | NORRIS WELL | other | diversion | Domestic |
| 3105029 | RUSSELL WELL | other | diversion | Commercial, Domestic |
| 3105030 | JOE FORD WELL NO 2 | other | diversion | Domestic |
| 3105032 | COOL WATER INC WELL | other | diversion | Commercial, Domestic |
| 3105035 | SAFLEY WELL | other | diversion | Commercial |
| 3105039 | VALLECITO RESORT W NO 1 | other | diversion | Commercial |
| 3105045 | VALLECITO RESORT W NO 2 | other | diversion | Commercial |
| 3105061 | C WHEAT WELL #1 | other | diversion | Commercial, Domestic, Municipal |
| 3105066 | VAN DEN BERG SUBDIV WELL | other | diversion | Commercial, Domestic |
| 3105067 | POOLE WELL | other | diversion | Commercial, Irrigation |
| 3105075 | WILDERNESS CLUB WELL 1 | other | diversion | Commercial, Domestic, Fishery, Irrigation |
| 3105076 | WILDERNESS CLUB WELL 3 | other | diversion | Commercial, Domestic, Fishery, Irrigation |
| 3105077 | WILDERNESS CLUB WELL 4 | other | diversion | Commercial, Domestic, Fishery, Irrigation |
| 3105079 | SAFARI LODGE WELL | other | diversion | Commercial, Domestic |
| 3105082 | PONDEROSA WELL NO 2 | other | diversion | Commercial, Domestic |
| 3105087 | FIVE BRANCHES WELL | other | diversion | Commercial |
| 3105088 | SILVER STREAMS WELL NO 1 | other | diversion | Commercial, Domestic |
| 3105090 | WITS END WELL NO 1 | other | diversion | Commercial, Domestic, Recreation |
| 3105091 | JONES WELL | other | diversion | Municipal |
| 3105092 | SILVER SPRUCE WELL | other | diversion | Commercial, Domestic |
| 3105095 | PEAKE WELL A | other | diversion | Domestic |
| 3105097 | BLUE SPRUCE WELL | other | diversion | Commercial, Domestic |
| 3105099 | RESTHAVEN WELL | other | diversion | Commercial, Domestic |
| 3105100 | RIBAUDO WELL | other | diversion | Commercial |
| 3105101 | PACK WELL | other | diversion | Domestic |
| 3105103 | DUSTIN WELL | other | diversion | Domestic |
| 3105104 | CAVIGGIA WELL | other | diversion | Commercial, Domestic |
| 3105105 | HILL WELL | other | diversion | Domestic |
| 3105107 | PETERSON WELL #117379 | other | diversion | Domestic |
| 3105108 | BRIGGS WELL #2 | other | diversion | Domestic |
| 3105109 | BARNHART WELL | other | diversion | Commercial, Domestic |
| 3105110 | TUTHILL WELL #2 | other | diversion | Municipal |
| 3105112 | FOREST LAKES WELL #1 | other | diversion | Domestic, Fire, Municipal |
| 3105113 | EIGHT CORNERS REPL WELL | other | diversion | Commercial, Domestic |
| 3105115 | POFFENBERGER WELL | other | diversion | Domestic |
| 3105116 | SCHMIDT WELL | other | diversion | Domestic |
| 3105118 | SWIER WELL #2 | other | diversion | Domestic |
| 3105119 | WILBOURN WELL #1 | other | diversion | Domestic, Stock |
3. Suspected nested tributaries
11 flag(s) confirmed connected by USGS NLDI — real surveyed stream-network topology, not a distance guess (see VERIFICATION-PLAN.md). This confirms the two candidates' channels really do merge (ruling out a coincidental-proximity false flag) but NOT auto-applied to tributary_parent_overrides — NLDI's overlap test can't reliably tell which side is upstream once two streams have already merged near DWR's own recorded structures, only that they connect. Confirm the direction (which one is the tributary, which is the parent) from local knowledge or the evidence below, then set it yourself.
| pair | NLDI evidence |
|---|---|
| DRY CREEK <-> BRINKS DRAW | tributary's downstream NHD trace (comid 17034443) first overlaps BRINKS DRAW's own downstream trace at index 1 (next-nearest candidate: ('MAINSTEM', 2)) |
| LOST CREEK <-> GRIMES CREEK | tributary's downstream NHD trace (comid 17034221) first overlaps GRIMES CREEK's own downstream trace at index 2 (next-nearest candidate: ('MAINSTEM', 14)) |
| GRIMES CREEK <-> VALLECITO CREEK | tributary's downstream NHD trace (comid 17034217) first overlaps VALLECITO CREEK's own downstream trace at index 3 (next-nearest candidate: ('MAINSTEM', 14)) |
| VALLECITO CREEK <-> GRIMES CREEK | tributary's downstream NHD trace (comid 17034217) first overlaps GRIMES CREEK's own downstream trace at index 0 (next-nearest candidate: ('MAINSTEM', 14)) |
| TIFFANY DRAW <-> CARLSON ARROYO | tributary's downstream NHD trace (comid 17034649) first overlaps CARLSON ARROYO's own downstream trace at index 0 (next-nearest candidate: ('MAINSTEM', 2)) |
| CARLSON ARROYO <-> TIFFANY DRAW | tributary's downstream NHD trace (comid 17034649) first overlaps TIFFANY DRAW's own downstream trace at index 0 (next-nearest candidate: ('MAINSTEM', 2)) |
| SPRING CREEK <-> TIFFANY DRAW | tributary's downstream NHD trace (comid 17034641) first overlaps TIFFANY DRAW's own downstream trace at index 1 (next-nearest candidate: ('MAINSTEM', 2)) |
| BRINKS DRAW <-> DRY CREEK | tributary's downstream NHD trace (comid 17034445) first overlaps DRY CREEK's own downstream trace at index 1 (next-nearest candidate: ('MAINSTEM', 2)) |
| WALLACE GULCH <-> MAINSTEM | tributary's downstream NHD trace (comid 17034321) first overlaps MAINSTEM's own downstream trace at index 1 (next-nearest candidate: ('DRY CREEK', 9)) |
| CROWBAR CREEK <-> BEAVER CREEK | tributary's downstream NHD trace (comid 17034349) first overlaps BEAVER CREEK's own downstream trace at index 3 (next-nearest candidate: ('MAINSTEM', 5)) |
| UTE CREEK <-> MAINSTEM | tributary's downstream NHD trace (comid 17034551) first overlaps MAINSTEM's own downstream trace at index 2 (next-nearest candidate: ('SPRING CREEK', 7)) |
Still need a human decision — these tributary pairs are comparably close to EACH OTHER as to the mainstem — one may actually join the other rather than the mainstem directly (like Leavenworth Creek -> South Clear Creek in the Clear Creek basin). NLDI couldn't resolve these (no nearby flowline, or ambiguous/no downstream overlap within range) — if you know the real topology, set it in longitudinal.tributary_parent_overrides.
| tributary | possible parent | dist to possible parent (mi) | dist to mainstem (mi) | NLDI result |
|---|---|---|---|---|
| IGNACIO CREEK | DRY CREEK | 1.15 | 1.15 | ambiguous -- tied earliest overlap at index 5: ['DRY CREEK', 'MAINSTEM'] |
4. Gage placement risk
None — every gage with a resolvable position is within the placement cutoff.
8 more gage(s) pass but are within 2x the cutoff distance — worth a glance if the structure dataset changes later.
Next steps
- Fill in
tributary_stream_patternsfrom section 1. - Resolve section 3's flags (or confirm none apply).
- Resolve section 4's at-risk gages.
- Cross-reference
return_flow_wdids/force_diversion_wdidsagainst any local accounting source you have for this basin. - Review the rendered schematic for this district before relying on it.
Evolution of the network
Computed 2026-08-20 09:36 from 8 gage(s) with cached period-of-record data. Statistical tests (Mann-Kendall trend, Pettitt changepoint) require at least 8 years spanning at least 10 years of record -- gages below that report no signal, not "no change."
Data provenance & quality
Where these numbers come from and how far they can be trusted. Grade C (3/6 points) — the components below are the finding; the letter alone is not. Sources: DWR HydroBase snapshot HydroBase_CO_20260707 (imported 2026-08-19) for history, plus the CDSS REST API for current conditions.
| Check | State | What was measured |
|---|---|---|
| gage freshness | stale | newest gage reading is 45 day(s) old (target 7) |
| diversion record | expected-lag | newest diversion record is 293 day(s) old (DWR publishes ~1 year in arrears) |
| structure coverage | sparse | 10% of schematic structures have data |
Independent check: PASS — 100.0000% agreement across 626,697 stored values re-checked against DWR's authoritative record (HydroBase_CO_20260707), over 20 structures. 0 disagreement(s) beyond a 0.01 cfs tolerance. Checked 2026-08-19; a rotating sample covers the whole basin across successive runs, and the structures this report cites are checked every time.
Federal cross-check: PASS — 99.12% day-level agreement with USGS's own published records for the same gages, across 6 co-listed station(s) and 107,336 overlapping days (within max(2%, 0.5 cfs) daily). Pre-1950 records at some gages carry known between-agency day-stamp and transcription differences — scored at each year's best ±1-day alignment; residual disagreement is real historical divergence, flagged for review.
8 gage(s) / 126,408 daily values (1927-10-01–2026-07-06); 204 structure(s) with diversion records; 1037 with decreed rights. Methodology has not yet had independent expert review — treat every figure as an advisory screen, not an administrative or legal conclusion.
Read this first: the measurement network itself evolved
This basin was not always measured the way it is today — the API-era record is dense and recent, the early record sparse. 6 gage(s) and 36 structure(s) report in 2026, but structure reporting only reached half its modern level around ~1967. Every historical claim below is checked against this: long-term shifts that co-move with the growth of the network carry an explicit measurement-evolution caution, and abandonment screens whose idleness begins before the modern reporting era are flagged †.
| Decade | Gages with data (median yr) | Structures reporting (median yr) |
|---|---|---|
| 1920s | 1 | 0 |
| 1930s | 1 | 0 |
| 1940s | 1 | 0 |
| 1950s | 3 | 49 |
| 1960s | 4 | 24 |
| 1970s | 4 | 100 |
| 1980s | 4 | 115 |
| 1990s | 4 | 124 |
| 2000s | 5 | 120 |
| 2010s | 5 | 92 |
| 2020s | 6 | 32 |
Gage flow trend & changepoints
Every located gage with a period of record — dot size scales with the strength of its flow trend (|Sen slope| in %/decade, the same statistic as the table below), color with direction. An amber ring marks a detected Pettitt changepoint. Click a gage to chart its trend and shift.
| Gage | Trend | Change / decade | Significance | Years | Changepoint |
|---|---|---|---|---|---|
|
▸
PINE RIVER BELOW VALLECITO RESERVOIR NEAR BAYFIELD PINBVACO |
↓ decreasing | -22.7% | p=0.009 | 41 | ~2008 |
7 other gage(s) show no significant trend or changepoint (not shown).
Mass-balance (network closure) trend
Structure divrec-history backfill coverage as of the last check: 10% of 508 schematic-relevant structures. 0 year(s) clear the 30% coverage gate so far -- the trend activates automatically once qualifying years span a full decade. No action needed; the nightly backfill keeps extending the record.
Reach gain/loss shifts (1951–2026)
Mass-balance kinks computed for every summer month back to 1951 (746 reach-snapshots) — which reaches gain or lose water, and how that has shifted across decades. Each shift is cross-checked against the observation record above: as more diversions became metered, "unaccounted" water shrinks mechanically, which can masquerade as a hydrologic shift.
- LOS PINOS RIVER NEAR IGNACIO, CO: reach shifted from -544 cfs to -180 cfs summer mean (more gaining, p=0.020, 27 yr) [sedimentary plains/foothills: moderate groundwater connectivity -- gain/loss shifts can be real aquifer response; corroborate with nearby well records] [measurement-evolution caution: this shift co-moves with the growth of the gage/metering network (rho=-0.61) -- part of it may be unaccounted water becoming accounted, not hydrologic change]
- SPRING CREEK AT LA BOCA, CO: reach shifted from -587 cfs to -12 cfs summer mean (more gaining, p=0.046, 61 yr) [sedimentary plains/foothills: moderate groundwater connectivity -- gain/loss shifts can be real aquifer response; corroborate with nearby well records]
Groundwater now has its own tab: 120 monitored well(s), water-table trends, stream corridors, and the advisory depletion screen.
Reservoirs now has its own tab: 30 reservoir(s), end-of-year storage back to 1951, click-to-chart histories.
Cross-gage pattern fingerprint
Over the 27-year window with full coverage (2000–2026), the dominant shared pattern across 3 gage(s) explains 90% of year-to-year variance (almost certainly a basin-wide climate/snowpack driver).
All gages in this window move with the shared pattern -- no localized outlier.
The basin's aquifer story, from 179 water-level measurements across 120 monitored well(s) (86 alluvial, 0 bedrock, rest unclassified) — plus 4 administered well(s) reporting metered pumping through diversion records. Observation wells and pumping wells are different populations and are never conflated. Click a well to chart its record.
Well map
Every monitored well with a location — hover for identity, click to chart its water-level record below. ● alluvial ● bedrock / confined (Denver Basin, High Plains, etc. — one-way, no human-timescale recharge) ● unclassified — marker size scales with the strength of the well's water-level trend (|Sen slope| in ft/decade — the same Mann-Kendall/Sen statistic as the trends table below); the smallest, faintest dots have too little record to test.
3D aquifer x-ray
Every aquifer unit as its own 3D head surface — alluvial water table on top, Denver Basin members (Dawson, Denver, Arapahoe, Laramie–Fox Hills) stacked beneath where measured — interpolated from measured water levels and animated through time. Units are never mixed; surfaces exist only inside each unit's well coverage (no extrapolation); thin epochs are suppressed with their reason shown. Vertical scale exaggerated for readability; z is head elevation in feet. Advisory — measured heads, not a calibrated model.
Water-table trends
Of 1 well(s) with enough record for a trend test: 0 declining, 0 rising.
Stream corridors — the surface connection
For each reach whose gain/loss has shifted (Trends tab), the wells within 2 miles of its anchoring gage, their pooled water-table history over the same era, and an advisory Glover screen of lagged stream depletion from nearby metered pumping. v1 proximity = distance to the reach's anchoring gage; segment-based reach join is a flagged upgrade.
LOS PINOS RIVER NEAR IGNACIO, CO: 23 alluvial well(s) nearby. Glover screen: 0.1 cfs of nearby metered alluvial pumping → est. lagged depletion 0.0–0.1 cfs (uncalibrated T/S ranges; flagged for SPDSS calibration, AWAS cross-check, and expert review — DWR's AWAS is the authority).
SPRING CREEK AT LA BOCA, CO: 1 alluvial well(s) nearby
Wells labeled by administrative world before anything else is said about them: tributary alluvium participates in the priority system; designated-basin and Denver Basin bedrock aquifers are governed differently and are excluded from stream-connection reasoning. Read bedrock declines differently too: deep bedrock aquifers recharge negligibly on human timescales, so a falling bedrock level is storage mining — effectively permanent — not a drought response that a wet year undoes. All screens advisory.
30 reservoir(s) with 2,048 storage measurement(s), 1951–2012. Basin storage as of 2011-10-19 (the record's own end — reservoir records publish ~annually): 58,940 AF across 2 reservoir(s). Storage change is real water the mass balance must credit — a losing reach beside a filling reservoir isn't losing water, it's banking it.
Reservoir map — how full is each vessel?
Each reservoir drawn as a vessel: bubble size ∝ its record-high storage, fill level = last recorded storage as a share of its surveyed capacity (USACE National Inventory of Dams) where a confident NID match exists — the tooltip names the matched dam — and of its own record high otherwise (a wrong capacity would be worse than an honest record high, so only confident joins upgrade). Hover for numbers, click to chart its history below the map. A dashed teal ring marks reservoirs reporting live DWR telemetry — their fill reflects yesterday's storage, drawn as a dotted tail on charts and treated as provisional until the next verified HydroBase snapshot supersedes it. ● <25% ● 25–60% ● 60–90% ● >90%
Basin storage, end of each water year
End-of-water-year totals; per-year reservoir counts shown because reporting coverage varies -- a total is only comparable to years with similar counts.
Largest reservoirs on record
Click a reservoir to chart its full storage history.
| Reservoir | Last recorded storage (AF) | As of |
|---|---|---|
| ▸ VALLECITO RESERVOIR (3103518) | 58,751 | 2010-10-31 |
| ▸ VALLECITO RESERVOIR (3103529) | 350 | 1980-08-07 |
| ▸ EMERALD LAKE RESERVOIR (3103516) | 220 | 1951-09-01 |
| ▸ WOMMER RESERVOIR NO 1 (3103517) | 189 | 2011-10-19 |
| ▸ VALLECITO RESERVOIR (3103532) | 90 | 1980-07-10 |
| ▸ BELLFLOWER RETENTION RES (3103520) | 60 | 1990-10-31 |
| ▸ GOSNEY GRAVEL PIT NO. 1 (3103805) | 47 | 2003-10-31 |
| ▸ VALLECITO RESERVOIR (3103531) | 37 | 1980-08-07 |
Decrees, seniority, and administrative calls connected to this basin's flow network. Advisory reading aids on public DWR data — not administrative or legal conclusions. Rights on file: 1122 across 1037 structure(s); 44 structure(s) carry 1 court-case references.
Abandonment radar (25 screens)
Absolute rights with 10+ years of no recorded diversions. Screens only — storage, alternate points, and plan operations can explain nonuse lawfully. And diversion REPORTING itself only reached its modern level ~1967 — idleness that begins before then may be unreported use, not nonuse (flagged † below).
- EMERALD LAKE RESERVOIR (3103516) (1976-05-12, 0.0 cfs decreed): last active 1951 — 74 years idle † predates modern reporting era — last recorded activity predates this basin's modern reporting era (~1967) -- early absence of record is weak evidence of nonuse
- LEIGH PIPELINE (3100738) (1973-06-01, 0.1 cfs decreed): last active 1969 — 56 years idle
- COUCH D NO 1 & PUMP PLT (3100602) (1969-03-01, 1.0 cfs decreed): last active 1972 — 53 years idle
- GEORGE B JONES DITCH (3100565) (1911-05-01, 2.5 cfs decreed): last active 1973 — 52 years idle
- COUCH D NO 2 & PUMP PLT (3100603) (1969-03-01, 1.0 cfs decreed): last active 1973 — 52 years idle
- MONTGOMERY DITCH (3100610) (1920-04-23, 4.0 cfs decreed): last active 1973 — 52 years idle
- LOWER WOMMER DITCH NO 1 (3100623) (1900-07-31, 3.0 cfs decreed): last active 1973 — 52 years idle
- LOWER WOMMER DITCH NO 2 (3100624) (1900-07-31, 2.0 cfs decreed): last active 1973 — 52 years idle
- CALMETT NO 1 PUMP AND PL (3100631) (1952-12-31, 0.7 cfs decreed): last active 1973 — 52 years idle
- CURRIE-JACK CREEK PL (3100643) (1965-07-06, 0.0 cfs decreed): last active 1973 — 52 years idle
Compliance screens (102 advisory flags)
Screened 139 of 1037 structures with rights (151 have diversion history on file). A flag is a lead for expert review — augmentation plans, exchanges, and free-river conditions can make over-decree diversions lawful and are deliberately not modeled.
- VALLECITO HYDROELECTRIC (3100844): Observed p99 daily rate 725.0 cfs (max 850.0) exceeds total decreed absolute 720.0 cfs across 40124 recorded day(s).
- KING DITCH (3100519): Observed p99 daily rate 116.0 cfs (max 758.6) exceeds total decreed absolute 106.2 cfs across 47452 recorded day(s).
- SCHRODER IRRIGATION DITCH (3100523): Observed p99 daily rate 64.9 cfs (max 82.0) exceeds total decreed absolute 63.5 cfs across 44216 recorded day(s).
- ROBT MORRISON D HEAIR EX (3100645): Observed p99 daily rate 54.0 cfs (max 56.0) exceeds total decreed absolute 2.5 cfs across 7116 recorded day(s).
- THOMPSON-EPPERSON DITCH (3100511): Observed p99 daily rate 45.0 cfs (max 66.0) exceeds total decreed absolute 35.4 cfs across 41129 recorded day(s).
- BEAR CREEK AND PINE RIVER DITCH (3100514): Observed p99 daily rate 22.6 cfs (max 110.0) exceeds total decreed absolute 14.0 cfs across 47111 recorded day(s).
- CEANABOO DITCH (3100502): Observed p99 daily rate 19.5 cfs (max 26.7) exceeds total decreed absolute 9.8 cfs across 34987 recorded day(s).
- LOS PINOS IRRIGATING DITCH (3100512): Observed p99 daily rate 19.0 cfs (max 35.8) exceeds total decreed absolute 11.5 cfs across 73215 recorded day(s). Structure holds an Augmentation-use decree -- diversions above the direct-flow decree can be lawful under plan operations; interpret with care.
- LA BOCA DITCH (3100507): Observed p99 daily rate 18.0 cfs (max 31.7) exceeds total decreed absolute 14.3 cfs across 22127 recorded day(s).
- KIRKPATRICK DITCH (3100535): Observed p99 daily rate 16.5 cfs (max 22.6) exceeds total decreed absolute 6.5 cfs across 10832 recorded day(s).
Seniority (top structures by decreed rate)
| Structure | Senior priority date | Rights | Decreed abs (cfs) | Decreed abs (AF) | Conditional? |
|---|---|---|---|---|---|
| VALLECITO HYDROELECTRIC (3100844) | 1979-06-01 | 1 | 720.0 | 0 | — |
| SPRING CREEK DITCH (3101045) | 1868-07-25 | 9 | 321.2 | 0 | yes |
| ROBERT MORRISON DITCH (3100547) | 1890-10-01 | 6 | 108.5 | 0 | — |
| KING DITCH (3100519) | 1881-05-01 | 4 | 106.2 | 0 | — |
| VALLECITO CREEK INSTREAM FLOW WATER RIGH (3101901) | 2017-03-23 | 1 | 92.0 | 0 | — |
| DR MORRISON DITCH (3101044) | 1868-07-25 | 2 | 72.6 | 0 | yes |
| SCHRODER IRRIGATION DITCH (3100523) | 1881-09-01 | 4 | 63.5 | 0 | — |
| PORTER DITCH (3100583) | 1936-06-15 | 2 | 48.0 | 0 | — |
| WEMINUCHE PASS DITCH (3104637) | 1934-07-28 | 4 | 40.0 | 0 | — |
| THOMPSON-EPPERSON DITCH (3100511) | 1877-12-31 | 6 | 35.4 | 0 | — |
| LOS PINOS RIVER (3101900) | 1984-07-13 | 1 | 32.0 | 0 | — |
| PINE R WEMINUCHE PASS D (3104638) | 1934-10-11 | 3 | 18.0 | 0 | — |
| DRY CREEK DITCH (3100660) | 1900-12-31 | 1 | 15.4 | 0 | — |
| LA BOCA DITCH (3100507) | 1868-07-25 | 1 | 14.3 | 0 | yes |
| BEAR CREEK AND PINE RIVER DITCH (3100514) | 1878-05-01 | 1 | 14.0 | 0 | — |
No inventory or legal-document changes detected since the daily watch began.
If a call were placed at a given seniority, which structures in this basin would be out of priority, and how much of their decreed rate would be curtailed? Computed from this basin's cached decrees.
What this does and doesn't model. Seniority arithmetic only: every right junior to the call is treated as curtailed. It does not model reach applicability — structures downstream of the calling point are not administered by it — and it applies no futile-call judgment. Read it as “who is junior to this date, and by how much,” not as a prediction of what the Division Engineer would actually order.
Pick a calling right
Real decrees from this basin, ordered by administration number — that is, by actual seniority. The years will look out of order, and that is correct: an administration number encodes the adjudication date as well as the appropriation date, so a right appropriated in 1970 can be administered ahead of one from 1950. A senior call curtails almost everything; a junior one curtails almost nothing.
Or enter an administration number directly
DWR administration numbers encode appropriation and adjudication dates; lower is more senior.