Each scenario screens the Ottawa River's low-flow capacity against the
campus's consumptive cooling draw: live flow minus consumptive loss against
the 7Q10 design low flow, and the assimilative headroom that remains. Live
gauge and permit figures are grounded; scenario draws are
labelled assumptions.
A written walk-through of this screen — including the newly document-sourced
sanitary figures — is in the
water-balance assimilative screen memo.
Bullet · draw vs design low flowAt the 7Q10 design low flow, the buildout cooling draw dwarfs the river
scale · cubic feet per second
Consumptive draw · buildout
[inference]
4.85 cfs
Ottawa River 7Q10 design low flow
[verified]
0.2 cfs
The modeled buildout cooling draw (5 cfs) is about 24× the Ottawa River's 7Q10 design low flow (0 cfs) — the drought flow Ohio writes discharge permits at. This is a basin-scale worst-case bound, not a river withdrawal: Lima draws treated water from five off-stream reservoirs (~15 BG) filled from the Auglaize and Ottawa at high flow, so the operating constraint is reservoir drawdown, not instantaneous river depletion.
The screen above is the surface-water constraint. Its groundwater peer — the
area well concerns: the hypothetical drawdown cone, the documented
construction-dewatering wellfield and the domestic wells it drew down, and a screen of
the river record for where that pumped water went — has its own page.
The screen above weighs the cooling load's volume. The same load also carries
heat: cooling water leaves a plant warm, and Ohio writes a numeric
temperature standard the Ottawa River has only 5.4 °C
of headroom against at design low flow. The thermal screen reads the modeled campus heat
load and the corridor's own reported effluent temperatures against it, framed as
CWA §316(a) — 3 of 7 screened dischargers clear the criterion , and 2 permits already report an effluent temperature over it
.
Assimilative screen · 4 of 4 receiving reaches fail the dilution
band at design low flow (Shawnee II WWTP chronic 0.04:1, acute 0.00:1 (6.21:1 effluent-credited) · American Bath WWTP chronic 0.01:1, acute 0.01:1 · American II WWTP chronic 0.42:1, acute 0.32:1 · Lima WWTP chronic 0.01:1, acute 0.00:1 (0.17:1 effluent-credited)). The design flow is matched to the criterion type — chronic aquatic-life
dilution at the 7Q10, acute at the sharper 1Q10; the effluent-credited ratio counts the
permitted effluent already in the reach. A screening band, not a permit determination.
Tier-0 water balance · 5 nodes · modeling caveats:
BOSC routing via theorized-fm3-shawnee-ii to watch-shawnee-ii-wwtp is THEORIZED (unconfirmed) — excluded from the balance; Shawnee II has no known BOSC routing.
buildout
Data-center campus cooling draw (evaporative_tower) on the municipal supply.
The IT load is inferred from the facility's [verified] air-permit
backup capacity (N+1), then carried through the cooling archetype's water math — one
derivation, not two headlines. The disclosed MW range widens the consumptive bracket.
the load and the grid →
Assimilative screen · 4 of 4 receiving reaches fail the dilution
band at design low flow (Shawnee II WWTP chronic 0.04:1, acute 0.00:1 (6.21:1 effluent-credited) · American Bath WWTP chronic 0.01:1, acute 0.01:1 · American II WWTP chronic 0.42:1, acute 0.32:1 · Lima WWTP chronic 0.01:1, acute 0.00:1 (0.17:1 effluent-credited)). The design flow is matched to the criterion type — chronic aquatic-life
dilution at the 7Q10, acute at the sharper 1Q10; the effluent-credited ratio counts the
permitted effluent already in the reach. A screening band, not a permit determination.
Tier-0 water balance · 5 nodes · modeling caveats:
BOSC routing via theorized-fm3-shawnee-ii to watch-shawnee-ii-wwtp is THEORIZED (unconfirmed) — excluded from the balance; Shawnee II has no known BOSC routing.
BOSC campus consumptive cooling is a derived central estimate (~4.9 cfs; 2.85-4.18 MGD evaporative range) from the air-permit power figure x WUE — not a metered or permitted value.