I LLINOI
P~LLOT::
C~
C( NT?~OL BOARD
:rrne
1~
~9~2
IN
THE
MATTER
OF
AMENDMENTS
TO
TITLE
35:
ENVIRONMENTAL
PROTECTION
R
81~
23
SUBTITLE C:
WATER
POLLUTION,
CHAPTER
1:
POLLUTION
CONTROL
BOARD
(Aismonia
Nitro-~en)
~p~edRulG
Eeoc ad
Mothc s.
OPINION
AND
ORDEP
OF
TEE
BOARD
(hv
T~D~
Dumelie):
On
February
4,
i,
12
~
~.
Rc~rd
:ssued
a
Proposed
Opinion
and
Order
in
this
matter
baseC
i~r~n
ire~,
~1nqniry~
hearings
which
had
been
held
in
response
Lo
tNe
Department
of
Energy
and
Natural
Resources
having
submitted
its
review
of
existing
Rule
203(f)
of
Chapter
3:
Water
Poli~tion
as
it
relates
to
ammonia
nitrogen
(Doc.
8:L/23)~
On March 19, 191~ :hs 303rd
entered
a
Proposed
Rule/First
Notice
Order.
First~Notce was published
in
the
Illinois
Register on April
3Q, i912~ Thereafter,
two
additional
hearings
were held to consider the 13oard~sproposal.
The first
was held April
30,
1981 at the Board Meeting Room in
Chicago.
The other
was held May
4
~98
at the Peoria
Public
Library.
The Board s
comment period and 8th First
Notice
period
both
expired
on
June
14,
1912~
As
noted
in
the
Febrvavy
4,
1982
Proposed
Opiniori~
the
Board
has
codified
Chapter
3
during
the
pendancy
of
this proceeding.
Since
the
Board
expects
State
Library
certification
of
that
Codi-
fication
prior to the close ml the Jecond
Notice
period,
all
references
in this Order ~J
me to Lao codified rules.
The
following
table
is
provided
to
aid
in
referencing
old
Board
rule
numbers
to
section
numbers
pursuant
to
codification:
Chapter
3:
Water
35 111,
Admin.
Rule
Name
pollution
Rule
Number
Code Number
*
203(f)
302~2O8
General Use WQS—
Chemical
Constituents
402
3O4~i35
Violation of WQS
402~l
304 .~3O1
Temporary Effluent
Standards
406
304.122
General
Effluent
Standards
-
Nitrogen
409
304.140
Delayá
in
Upgrading
*WQS
=
Water Quality Standards
47-293
—2—
RESPONSE TO COMMENTS
On April
21, 1982 the Agency filed a “recommendation”
which was entered as Exhibit 12 at the April
30,
1982 hearing.
Final
Agency
comments were filed on June 14,
1982 which reiterated
the Agency’s position presented in the recommendation:
first,
that the termination date for the Section 304.301(d) exemption
be extended to July 1,
1988 rather than July
1,
1986 and, second,
that the un—ionized ammonia alternative water quality standard
be removed or at least that an upper limit be set on the ammonia
nitrogen standard regardless of the calculated un—ionized level.
The Agency’s rationale for extending the termination date
to 1988 is based upon the
“Municipal Wastewater Treatment Con-
struction Grant Amendments
of
1981” which extended the compliance
date for municipalities to meet secondary treatment requirements
or more stringent state requirements from July 1, 1983 to July
1,
1988.
Therefore,
municipalities required
to meet ammonia limits
could be issued NPDES permits
which
expire July 1,
1988 if the
Board’s termination date were set
in
accordance with the federal
date.
The shorter term permits allowed by the Board’s proposed
1986 date are argued to cause increased costs to the applicant
and the Agency due
to
an increase in permit renewals, review and
issuance.
Part of the Agencyus rationale for deletion of the un-
ionized ammonia alternative water quality standard is the diffi-
culty of monitoring since
there
is not yet any reliable, easily
accomplished method of direct measurement of un—ionized ammonia
concentrations.
Further,
the Agency argues that mathematical
conversion of ammonia nitrogen concentrations to un—ionized
ammonia nitrogen concentrations using pH and temperature fails
to take into consideration other significant factors that affect
the conversion.
Also,
fluctuations of pH can be sufficiently
large and difficult to predict that the discharger would generally
have to overcontrol to assure compliance with the water quality
standard such that the discharger would not be able to rely on
the proposed, relaxed alternative standard.
The Agency finally argues that the Board’s proposed standard
would allow ammonia nitrogen levels at least as high as 325 mg/i
to be discharged and that such discharges could lead to unaccept-
able oxygen depletion and fish toxicity.
Based on this the
Agency recommends that at a minimum the Board impose an upper
limit on the ammonia nitrogen discharge regardless of the un-
ionized ammonia concentration.
Linda Huff of Huff & Huff,
Inc., an environmental consulting
firm, testified that the proposed un-ionized ammonia standard is
a
positive step “to prioritize the pollution expenditures and reduce
the cost of providing acceptable
levels of wastewater treatment,”
despite the more complex determination of compliance
(R.393-394).
47-294
—3—
She
also testified that some treatment works may be able to
eliminate nitrificatiori,
and therefore reduce costs under the
Board’s proposal on a sophisticated site—specific basis
(R.394—
395),
Finally, she supported the Agency~srecommendation of an
upper limit on ammonia nitrogen levels,
although she was
uncertain as to what that level should be (R,395).
Drs,
Muchmore
and Heidinger,
authors of the economic impact
study
in this matter,
commented on June 14,
1982,
that they
supported the alternative standard with a 10 mg/i ammonia nitrogen
concentration limitation and that they saw little real difficulty
with the mathematical conversion method of monitoring un—ionized
ammonia
concentrations.
Also, on June
14,
1982,
Borg-Warner
commented
that the Board’s
proposal “would make the existing water quality standard more
reasonable” and that it
is fully supported by the
record,
However,
Borg—Warner contends that the same rationale for the water quality
standard supports the deletion of the effluent standards of
Section
304,122 which are applicable to dischargers to the Illinois River,
Des Plaines River, Chicago River System,
and the Calumet River
System.
The
Galesburg Sanitary District filed comments on June
15,
1982,
a
day after the close of the comment period, but the Board
will
consider them,
The District generally supports the Board’s
proposal
as cost saving while adequately protecting the
environment.
However,
it supports a higher un—ionized ammonia standard for
those streams which support a low variety of fish, perhaps up
to
0,07 to 0,10 mg/i.
In effect
it supports an even more site—
specific
approach to this regulatory
scheme.
The City of Lockport also filed
late comments on June 16,
1982
which will be considered,
The City
is supportive
of
the
Board’s
proposal,
citing
potential
cost
savings
of
$800,000
in
construction
costs for the upgrading of its facility.
BOARD ACTION
Based upon the hearings and the comments during the First
Notice
period,
the
Board
has
determined
that
an
upper
limit
should be placed upon the ammonia nitrogen concentration,
The
Board will
set that upper limit at 15 mg/I
as part of new
Section
302,212,
The Board will also modify the language establishing
the alternative standard for nurposes of clarity
(Section
302,212(a),
(b) and
(c),
inc’ude an equation for the mathematical
conversion of ammonia nitrogen concentrations to un—ionized
ammonia
concentrations
(Section
302,212(d),
and
include
a
table
of acceptable
levels of ammonia nitrogen under various pH and temperature
conditions
(Section 302,212(e).
The Board has also extended the
Section 304.301 compliance date until July 1,
1988.
Otherwise,
the Board’s
proposal
remains
unchanged.
47-295
—4—
JUSTIFICATION
The Board
has followed the Agency’s
recommendation that
the compliance
date of Section 304.301
be extended to July 1,
1988.
The
Agency states that there
is
considerable pressure
upon it from regulations
other than
Section 304.301 to insure
that appropriate
ammonia control will
be required at the earliest
possible time.
The Board has extended
the date with the under-
standing that
stream studies under R79—6
will proceed as expedi-
tiously as possible.
The Board has declined
to follow
the suggestion of the City
of Galesburg to raise
the proposed
un—ionized ammonia alternative
standard.
The
proposed standard
is
an interim standard pending
the completion of studies which
may
allow for ammonia standards
on a stream—specific
basis,
which
is
essentially what Galesburg
is suggesting be
done
in this
proceeding
for streams which do
not support a
high variety of fish.
In setting the 0.04 mg/l
standard the
Board
has loosened the
ammonia limitations as much
as is supportable
generally
throughout the State.
The present
record is inadequate to
support greater
specificity in terms of
stream use.
The
Board expects that to
be accomplished sometime
prior to 1986.
The Board
has further declined to follow
Borg-Warner’s
suggestion that
the Section 304,122
standards be deleted.
As
noted by other
commenters,
the
alternative standard proposed
allows considerably
higher ammonia
nitrogen discharges which
could have an
effect upon the
dissolved oxygen levels down-
stream of the discharge.
When the Board adopted
old
Rule 406
(Section 304.122),
the Board in fact found that
the
river systems covered suffered
from a unique dissolved
oxygen problem.
Deletion of that Section
could, therefore,
exacerbate
an
existing problem.
Borg—Warner
itself acknowledges that no testimony in this record is directed
specifically at these river systems
to show that there has been
significant enough improvement in dissolved oxygen levels to
warrant such deletion,
If
such evidence exists,
or if an alter-
native strategy for dissolved oxygen control can be shown to
remedy that problem, e.g.
through the
use of in—stream aeration,
that evidence could be presented
in
a future regulatory proceed-
ing directed at Section
304.122,
This record, however,
fails
to support such deletion.
The Board has also declined
to follow the Agency’s recom-
mendation that the un—ionized ammonia alternative standard be
dropped.
The Agency’s concerns over
the
difficulty of monitoring,
possible problems
with
dissolved oxygen levels and ammonia nitrogen
toxicity, and a lack
of cost savings have not been adequately
supported.
47-296
—5—
The
Agency
was the only participant
at the hearing to ques-
tion the
mathematical conversion technique
to
determine
the
un—ionized ammonia
concentration, citing
interference factors
of turbidity and
heavy metals
(R.387-388),
However, neither
interference could
be quantified,
and the heavy metal inter-
ference is offset
by the fact that
ammonia complexed with heavy
metals is less toxic
than the un-ionized
form
(R.388—389).
Further, several
conversion tables
exist and are
in close
agreement,
and Drs,
Muchrnore and
Heidinger did not feel that
the conversion
suffered from significant
infirmities.
The
Board has determined
that the table
generated by the Agency
and appearing
in Exhibit 12 is in general
agreement with other
tables, as
is the
equation on which
it
is based
see
Emerson,
Kenneth;
R.C.
Russo;
R.E.
Lund; and
R.V,
Thurston;
“Aqueous
Ammonia Equalibrium
Calculations:
Effects of pH and Temperature,”
Journal Fisheries
Research Board of
Canada, Vol.
32,
No,
12,
pp. 2379—2383
(1~75),
The Board has
included both the equation
and a table
in
Section 302,212 to give both an
easy reference
to the water
quality standard at typical
pH and temperature
levels and a means
for calculating
values which do not appear
in the table.
The
only
evidence presented regarding
ammonia nitrogen
toxicity is based
upon a 1962 study by
Tabata and a 1978 study
by Armstrong,
et al.
(R61-362),
However,
the applicability of
these studies to
Illinois fish is
undetermined and the conclu-
sions are quite
general.
Further, the
imposition of an upper
limit on ammonia
nitrogen should help
avoid any potential problems
and the economic
impact study
(Ex,1)
clearly indicates that the
focus of the
regulation should be on
un—ionized ammonia toxicity
rather than on
ammonia nitrogen.
The
Agency itself admitted
that there
“is very
limited information
on the toxicity of
combined forms of
ammonia”
(R,374).
Finally,
the Board is modifying its
proposal to establish
an upper
limit on the
ammonia
nitrogen concentration regardless
of the un—ionized ammonia concentration.
The Board has set that
limit at 15 mg/i, which
is higher
than the 10 mg/i limitation
recommended by the
Agency and supported
by Drs. Heidinger and
Muchmore, but somewhat
less than the
normal influent loading
to municipal treatment
plants.
The Board
has set that level
in
order to relieve municipal-
ities from the burden
of ammonia control
where such control does
not appear necessary
to protect the
environment.
James Park,
Manager of Technical
Standar~.s,
Division of Water Pollution
Control for the Agency,
testified that
some municipal plants
without ammonia controls
may discharge
up
to 30 mg/i of ammonia
nitrogen, but that
most fail
in the 15—20
mg/I range
(R.377).
In its comments Galesburg
states that
20 mg/i
is “generally
acceptable”
as the concentration found
in untreated wastewater
of domestic origin.
47-297
—6—
Setting
an upper
limit at this time is somewhat
difficult.
If the
Board were to rely on the Tabata data which
indicates
that ammonia
nitrogen is somewhat less than one—fiftieth
as toxic
to fish
as un—ionized ammonia, the upper limit would be set at
somewhat higher
than 2,0 mg/l,
If,
however, the Board were to
conclude
that the present state of
knowledge regarding ammonia
nitrogen toxicity
is insufficient to
necessitate control,
a
standard of
30 mg/i would be
appropriate
to allow most,
if not
all, municipal plants
to be uncontrolled,
Given the burdensome costs associated with
controls to
reach the lower end
of
that
range
and
the sparse evidence of
toxicity, a standard
as
low
as
2.0
mg/i
is
unjustifiable at this
time.
On the other
hand, allowing a total
absence of control
in
light of suspected
environmental harm is
equally unsupportable.
The Board has,
therefore,
concluded that
a middle ground of 15
mg/i
is
appropriate at this time.
Since
most municipal plants
are exempted
under Section 304.301,
in
any case,
this standard
is currently
one more of form than of substance.
Only after
July 1,
1988 would
it have general
applicability.
During the
interim studies can proceed
and data can be
collected to estab-
lish a more
meaningful standard,
If future
studies show that
ammonia
nitrogen toxicity at that level
is
a real problem or that
the 15 mg/i
standard can be raised without
causing significant
toxicity
problems, that can be addressed in
future regulatory
proceedings.
Based
on the record in this
proceeding a 15 mg/i
limitation seems adequate
to protect
the environment.
ORDER
The Board
hereby directs the Clerk to
proceed to Second
Notice in this matter,
and proposes the
following amendments
to Title
35:
Environmental Protection;
Subtitle C:
Water
Pollution; Chapter
I:
Pollution Control
Board (deleted
language is lined through;
added language is
underlined):
Section 302.208
Chemical Constituents
The following levels
of chemical constituents
shall not be
exceeded:
STORET
CONCENTRATION
CONSTITUENT
NUMBER
(mg/i)
AMMeI~4~
N~foge~(e~
N)
~98~Q
Arsenic
(totai)
01002
1.0
Barium
(total)
01007
5.0
Boron
(total)
01022
1.0
Cadmium
(total)
01027
0.05
Chloride
00940
500.
Chromium
(total hexavalent)
01032
0.05
Chromium (total trivalent)
01033
1.0
Copper
(total)
01042
0.02
47-298
—7—
STORET
CONCENTRATION
CONSTITUENT
NUMBER
(mg/i)
Cyanide
00720
0.025
Fluoride
00951
1.4
Iron (total)
01045
1.0
Lead (total)
01051
0.1
Manganese
(total)
01055
1.0
Mercury
(total)
71900
0.0005
Nickel
(total)
01067
1.0
Phenols
32730
0.1
Selenium
(total)
01147
1.0
Silver
01077
0.005
Sulfate
00945
500.
Total Dissolved
Solids
70300
1000.
Zinc
01092
1,0
Source:
6
Ill,
Reg,
,
effective
Section
302,212
Ammonia Nitrogen and Un-ionized Ammonia
a)
Ammonia
nitrogen
(as
N:
Storet Number 31616)
shall
in
no
case
exceed
15
mg/i.
b)
If ammonia nitrogen is less than 15 mg/i
and greater
than or equal
to 1.5 mg/I, then un—ionized
ammonia
(as N) shall not exceed 0,04 mg/i.
c)
Ammonia nitrogen concentrations
of
less than 1.5 mg/i
are lawful regardless of un—ionized
ammonia concentration.
d)
For
purposes of this section the concentration
of
un—ionized ammonia shall be computed
according to the
£01lowing equation:
N
where:
12 (1+
10
)+
0. 05 59
X
=
0.09018
+
2729.92
—
pH
(T
+
273,16)
U
=
Concentration of un—ionized ammonia
as
N
in
mg/l
N
=
Concentration
of
ammonia
nitrogen
as
N
in
mg/i
T
=
Temperature in
degrees
Celsius
e)
The following table indicates the maximum
ammonia
nitrogen concentrations allowable for
certain
combinations of pH and temperature:
47-299
—8—
AMMONIA NITROGEN
WATER QUALITY STANDARD
(mg/l)
TEMP.
pH
°C(°F)
6.0
6.5
7.0
7.5
8.0
8.5
9.0
5
(41)
15
15
15
9.6
3.1
1.5
1.5
10
(50)
15
15
15
6.5
2.1
1.5
1.5
15
(59)
15
15
13.9
4.4
1.5
1,5
1.5
20
(68)
15
15
9,6
3.1
1.5
1.5
1.5
25
(77)
15
15
6.7
2.1
1.5
1.5
1.5
30
(86)
15
14.9
4.7
1,5
1.5
1,5
1.5
35
(95)
15
10.7
3.4
1,5
1.5
1.5
1.5
Source:
6 Iii.
Reg.
,
effective
SUBPART
(C);
TEMPORARY
EFFLUENT STANDARDS
Section 304.301
Exception
for
Ammonia Nitrogen Water Quality
Violations
a.
Section 304.105
shall not apply to
a~-pe~~on-e~
Section 302.212
~
for any effluent from a source in existence on April
1,
1977, having an
untreated ammonia
infiuent loading not
exceeding 60 pounds per day and not otherwise needing
upgrading to meet the requirements of this chapter.
b.
Section 304.105 shall not apply to tha~-pef~oft-o?Section
302.212 ~O
~9~-~ea
g-te-ammo~a-~~fe~en
for any
source during the months
of
November through March;
except
that during the months
of
November through March no source
not exempt under paragraph
(a)
shall discharge an effluent
containing a concentration of ammonia nitrogen greater than
4.0 mg/i
if the discharge, alone or in combination with
other discharges, causes
or
contributes to a violation of
that portion of Section ~
302.121 pef~a~n4~g—~e
ae~a—n~~ege~.
c.
Compliance with the provisions of paragraph
(b)
shall be
achieved by March 31, 1979,
or such other date as required
by NPDES permit,
or as ordered by the Board under Title
VIII or Title IX of the Environmental Protection Act.
d.
After July 1,
1988, the exemptions provided in this section
shall terminate,
Source:
6 Iii. Reg.
,
effective
47-300
—9—
Section 304.140
Delays
in Upgrading
a.
All effluent
standards required to be met on December 31,
1973 or December 31,
1974 and in response to Section
304.301 shall be met unless:
1.
The discharger
is eligible for a construction grant
under Section 201(g)
of the Clean Water Act;
and,
2.
The discharger has filed an application for a construction
grant on or before December 31, 1975;
and,
3.
The discharger has timely taken all necessary pre—grant
and post-grant actions appropriate to the specific
grant step for which the discharger is then eligible.
4.
The exemption provided in
(a)
(1),
(a) (2) and
(a) (3)
above shall terminate upon completion of construction
under the grant provided and compliance with the
provisions of this Section shall thereafter be required.
Source:
6 Ill. Reg.
,
effective
IT IS SO ORDERED.
I, Christan L.
Moffett,
Clerk of the Illinois Pollution
Control Board,
hereby ~ertify that the above Opinion and Order
was adopted on the
/~1~ day of ~
,
1982 by a
vote of
~-O
Christan L. MofW~’)Clerk
Illinois PoliutidT1’’Control Board
47-301