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Trinchera Creek

Division 3 · Water District 35
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Trinchera Creek on the ground — the ditches, wells, reservoirs and gages of Water District 35 · clicktap anything for its record

Snowpack — no snow on the ground at 3 SNOTEL sites — normal for the date; the snow year begins in October and typically peaks around March 9. Runoff outlook — Trinchera Ck ab Turners Ranch: even odds of at least 1 kAF over 06-01 to 09-30 — 21% of a normal season, per NRCS, issued 2026-06-01 — the season’s final; new forecasts begin in January. Runoff outlook — Sangre de Cristo Ck : even odds of at least 1 kAF over 06-01 to 09-30 — 27% of a normal season, per NRCS, issued 2026-06-01 — the season’s final; new forecasts begin in January. Runoff outlook — Ute Ck nr Fort Garland: even odds of at least 2 kAF over 06-01 to 09-30 — 25% of a normal season, per NRCS, issued 2026-06-01 — the season’s final; new forecasts begin in January. Full snow & runoff picture — charts, forecast history and how the forecasts have verified →

Sites, exceedance bands and sources
SNOTEL siteElev (ft)SWE (in)Median (in)% of medianTypical peak
Medano Pass9650 0.00.0 March 9 (7.4 in)
Trinchera10860 0.10.0 April 5 (11.2 in)
Ute Creek10720 0.00.0 April 4 (12.4 in)

Trinchera Ck ab Turners Ranch — 06-01 to 09-30 volume, thousand acre-feet (chance the volume is AT LEAST this):

90%70%50%30%10%Normal
01122 6

Sangre de Cristo Ck — 06-01 to 09-30 volume, thousand acre-feet (chance the volume is AT LEAST this):

90%70%50%30%10%Normal
01123 4

Ute Ck nr Fort Garland — 06-01 to 09-30 volume, thousand acre-feet (chance the volume is AT LEAST this):

90%70%50%30%10%Normal
01234 7

Snow-water equivalent and medians (1991–2020) from NRCS SNOTEL; seasonal volume forecasts from the NRCS National Water and Climate Center. Sites and forecast points are assigned to the district whose boundary contains them — snowpack that feeds this district can also sit in a neighboring headwater district. Toggle the Snow chip on the map above to see the sites.

Topology cross-check: 11 parent disagreements (vs DWR's route framework — under review)

This flow network was built mechanically; DWR's Source Water Route Framework disagrees with it in the places below. Each row is a question a human reviewer has not yet answered — not an error verdict. Checked 18 streams, 7 agree. Know this water? Tell us →

StreamThis site routes it toDWR routes it to
Sand Creek the mainstem Arena Creek
Big Spring Creek the mainstem nan
Medano Creek the mainstem nan
North Zapata Creek the mainstem nan
South Zapata Creek the mainstem nan
Urraca Creek the mainstem nan
Pioneer Creek the mainstem nan
Blanca Creek the mainstem nan

Full diagnostic snapshot pending — this district's weekly-style report (system status, active calls, hydrographs, anomaly flags) is produced by the nightly rotation and appears here after its first run. The tabs above are live now.

Groundwater

29,262 water-level measurements across 324 monitored well(s) — 174 alluvial, 54 bedrock — plus 3 administered well(s) reporting metered pumping.

What is being counted

Observation wells and pumping wells are different populations and are never conflated: water levels come from monitored observation wells, and metered pumping comes from administered wells reporting through diversion records. Click any well to chart its own record.

Well map

3D aquifer x-ray

Every aquifer unit as its own head surface, animated through time.

How the surfaces are built, and what they are not

Alluvial water table on top, Denver Basin members (Dawson, Denver, Arapahoe, Laramie–Fox Hills) stacked beneath where measured, interpolated from measured water levels. Units are never mixed; a surface exists only inside its own unit's well coverage, with no extrapolation; thin epochs are suppressed and say why. Vertical scale is exaggerated for readability and z is head elevation in feet. These are measured heads, not a calibrated groundwater model.

Water-table trends

Of 92 well(s) with enough record for a trend test: 55 declining, 7 rising.

Fastest-declining wellsSettingft / decadeSpanp
CC03107214CAA unknown -11.12 45 yr 0.0
CC03107209BAA unknown -8.33 45 yr 0.0
CC03107210BCD unknown -8.0 34 yr 0.0061
CC03107514AD unknown -7.34 16 yr 0.012
NA03801234BDD1 EW-27U alluvial -6.38 23 yr 0.0002
CC03107207DDA unknown -6.04 81 yr 0.0
CC03007302BAD alluvial -5.27 34 yr 0.0
NA03801234BDD2 EW-27C alluvial -4.52 23 yr 0.0001

Stream corridors — the surface connection

Where a reach's gain or loss has shifted, the wells within two miles of its anchoring gage and what their water table did over the same era.

How the corridor is assembled

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.

SANGRE DE CRISTO CREEK NEAR FORT GARLAND, CO.: 2 alluvial well(s) nearby; pooled water table -17678.2 ft (1991–2025, no_trend, p=0.3202)

UTE CREEK NEAR FORT GARLAND, 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.