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                  <text>C O L O R A D O

P A R K S

&amp;

W I L D L I F E

Experiments Show Iron Pollution
Limits Fail To Protect Aquatic Species

April 2020

Experiments conducted by Colorado Parks and Wildlife (CPW) suggest the current water quality
standard for iron (Fe) is two to four times higher than it should be to protect Colorado’s aquatic life.

Are Colorado’s iron water quality standards protective of fish?

For many decades, state and national water quality standards have
considered 1,000 µg/L of iron to be acceptable to allow fish and
aquatic life to survive. Unlike most toxicants, Fe does not stay in
solution. It precipitates out and settles on the floor of streams and
lakes (Figure 1). Over time, even low concentrations of Fe have
potential to heavily accumulate and smother habitat of fish, and the
aquatic insects and algae that fish eat. Colorado Parks and Wildlife
has long noticed that Fe can overburden aquatic ecosystems, even
when below the standard of 1,000 µg/L. To address this concern, a
series
of experiments
Figure 2 - Iron oxides smother a Colorado
a.
stream affected by legacy mines
were conducted by
CPW’s Aquatic Toxicology Laboratory and by Colorado State
University’s (CSU) Ecotoxicology Laboratory.

Laboratory studies - We exposed Mountain Whitefish, Boreal Toads,
Rainbow Trout, Brown Trout, Mayflies, as well as Planarian and
Lumbriculus worms to increasing level levels of iron. We then used the
standardized US Environmental Protection Agency methods to derive
water quality standards incorporating our results and the results of
other published studies. The calculated safe water quality standard was
found to be 499 µg/L total Fe. This is less than half the current
acceptable level of Fe pollution.
Mesocosm studies – CPW and CSU researchers feared the reason the
scientific community failed to consider Fe a threat to ecosystems was
related to the way experiments were conducted. CSU and CPW
incorporated more ecologically relevant methodologies to examine
effects of iron pollution on aquatic insects, the primary food source for
most of Colorado’s sport fish. Communities of aquatic macroinvertebrates were allowed to colonize substrate in the field (Figure
2a). Assemblages were then transported to experimental streams
(Figure 2b). Eighteen streams were assigned various concentrations of
Fe. After ten days insect survival was assessed. When these mesocosm
results were applied to the derivation, the final proposed chronic

b.

Figure 1- (a) Aquatic benthic communities
colonized substrate for 30 days prior to use in
mesocosm experiments. (b) Experimental
streams allow for a more ecologically relevant
exposure of benthic communities.

COLORADO PARKS &amp; WILDLIFE • 317 W Prospect Rd, Fort Collins, CO 80526 • (970) 472-4332 • cpw.state.co.us

�criterion for iron was found to be 251 µg/L total Fe. This is 25% of the current state and national limit for Fe.

Synergistic interactions with other metals - Water quality standards often assume the stress from one toxicant does
not reduce an organism’s resiliance against another toxicant. This is especially true for Fe. Studies from the late
20th century suggested that Fe has a protective effect against other metals. However, when we exposed algae to
copper (Cu) and zinc (Zn) in the presence and absence of Fe, we observed tissue concentrations of these toxicants
to be higher when Fe was present (Figure 4). Given algae is the base of most aquatic food chains, Fe can indirectly
increase dietary exposure to other metals.

How did CPW and CSU find effects well below the existing standard?

We conducted ecologically sound research rather than simply following standardized methods to the minimal level
of compliance.
●We included benthic (bottom dwelling) organisms that were
smothered by Fe, not just pelagic (free swimming) organisms.
●By using naturally colonized substrate we included small and
rare species, not just laboratory cultures (i.e. Water Fleas).
●Standardized methods allow static renewal, or infrequent
replenishment of toxicants. We used continous flow systems that
better simulate nature.
●Standardized methods require scientists to record only survival
as an appropriate endpoint. The most sensitive endpoints in our
laboratory trials were endpoints such as growth and reproductive
success.
●Standardized methods are perhaps fitting for direct toxicity of
some chemicals through gills. But these methods fail to include
dietary exposure as well as the indirect toxicity observed when Fe
smothers habitat or retards ecosystem processes. Mesocosm
studies incorporate indirect effects.

What is next?

Figure 3 - Zinc (Zn) and copper (Cu) accumulation in algae in low metal (ML) and high
metal (MH) treatments was greater when Fe
(red) was present. Different letters represent
statistical difference. DW=dry weight

Each water quality standard is ostensibly reviewed by federal
(USEPA) and state (Colorado Dept. of Public Health and
Environment) regulatory agencies every three years. CPW’s calculation followed the guidance of CDPHE and
USEPA experts and incorporated all supporting details. Revised iron standards have potential to align closely to
our derivation of 251 µg/L. This will improve conditions for aquatic life in Colorado streams affected by Fe
pollution. To read more, see these recent publications:

Cadmus, P., Guasch, H., Herdrich, A.T., Bonet, B., Urrea, G. and Clements, W.H. (2018) Structural and functional responses of
periphyton and macroinvertebrate communities to ferric Fe, Cu, and Zn in stream mesocosms. Environmental
Toxicology and Chemistry. 37: 1320-1329. https://doi.org/10.1002/etc.4070

Cadmus, P., Brinkman, S.F. &amp; May, M.K. (2018) Chronic Toxicity of Ferric Iron for North American Aquatic Organisms:
Derivation of a Chronic Water Quality Criterion Using Single Species and Mesocosm Data. Archive of Environmental
Contamination and Toxicology. 74: 605–615. https://doi.org/10.1007/s00244-018-0505-2
Kotalik, C. J., Cadmus, P. and Clements, W.H. (2019) Indirect Effects of Iron Oxide on Stream Benthic Communities:
Capturing Ecological Complexity with Controlled Mesocosm Experiments. Environmental Science &amp; Technology
53:11532-11540. https://doi.org/10.1021/acs.est.9b04236

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