“In 1992 the California State Water Quality Control
Board (SWQCB) proposed that the Klamath River be
listed for both temperature and nutrients, requiring
the development of total maximum daily load (TMDL) limits
and implementation plans.
“The United States Environmental Protection Agency (USEPA)
and the North Coast Regional Water Quality Control
Board accepted this action in 1993. The basis for
listing the Klamath River as impaired was aquatic
habitat degradation due to excessively warm water
temperatures and algae blooms associated with high
nutrient loads, water impoundments, and agricultural
diversions,” states the 2008 California 303 (d) list
of water quality limited segments from the SWQCB.
The list, containing “Category 5” water body
segments, pertains to water segments that are listed
as impaired with a TMDL required, but not yet
completed for one or more of the pollutants listed
for that segment. Five segments of the Klamath
River, as well as both Copco reservoirs and Iron
Gate Reservoir, are listed as Category 5 water
bodies.
For the mainstem Klamath River from Oregon to Iron
Gate, the list cites impairments as cyanobacteria
hepatotoxic microcystins, nutrients, organic
enrichment/low dissolved oxygen and water
temperature. Also listed for other segments is
sedimentation or siltation.
The list contains various potential sources of
pollutants, including agriculture; dam construction;
drainage/filling of wetlands; flow
regulation/modification; habitat modification;
hydromodification; unknown sources; industrial point
sources; municipal point sources; natural sources;
irrigation tailwater; range grazing–riparian and/or
upland; and upstream impoundment, among others.
Other sources, listed as “out–of–state sources,” are
explained in the list. “Klamath Falls (Oregon)
municipal wastewater discharge, industrial
facilities, and United States Bureau of Reclamation
pumped discharge of agricultural waste are
significant sources of nutrient loads to the Klamath
River as it enters California.” The list also states
that these are significant sources of organic
enrichment/low dissolved oxygen.
The stretch of the Klamath awaiting a TMDL – along
with the three reservoirs – may have implications
for the current issue of dam relicensing, with the
listing of dam construction as a potential source of
some of the impairments.
According to Dave Clegern of the SWQCB Office of
Public Affairs, the process of determining TMDLs on
the Klamath stretch is operating independently of
the dam process.
“The SWQCB does not have a seat at settlement
negotiations, and must ultimately await an outcome
of some kind there,” Clegern said, “For that reason,
we are proceeding with our Environmental Impact
Report (EIR) in a way that allows us to continue
gathering material in an open–ended manner.”
Clegern stated that the EIR is targeting the impacts
of pollutants and impediments on specific species in
the river, largely salmon and other fish but also
various other species.
There are a number of different dates for completion
of TMDLs, for example; on the stretch of the Klamath
from Iron Gate Dam to the Scott River, nutrients,
organic enrichment/low dissolved oxygen and
temperature are set to be addressed by next year,
but cyanobacteria and sediment TMDLs do not have to
be completed until 2021 – one year after the target
date for initiation of removal of the dams set forth
in the Agreement in Principle between dam owner
PacifiCorp and various governing agencies.
Other TMDLs share this decade-in-advance completion
date – ranging from 2019 to 2021.
“We’re taking
the EIR one step at a time simply because we don’t
know what will come out of the settlement,” Clegern
said, “we are open–ended right now, but will proceed
with an eye toward having all bases covered in as
timely a manner as possible.”
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