Z
                ARKANSAS
       WATER QUALITY STANDARDS
                 SUMMARY
                  Revised April 1972
NITED STATES ENVIRONMENTAL
ROTECTION AGENCY
ARKANSAS DEPARTMENT OF POLLUTION
       CONTROL AND ECOLOGY

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                           PREFACE
The information contained herein has been condensed from Water Quality
Criteria and  Plan for Implementation, State of Arkansas, prepared by the
Arkansas Department of Pollution Control and Ecology,* and approved by
the Administrator of the Environmental Protection Agency,** This summary
is intended for all who have an interest in the quality of water in the State.

A  summarization of this type, of necessity, omits many pertinent details.
For more detailed information, consult the Arkansas Department of Pollu-
tion Control and Ecology or the complete  text.
 *Prior to July 1, 1971, the Arkansas Pollution Control Commission.
**Prior to December 2,  1970, the Secretary of the Interior.

                          Revised April 1972

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                          CONTENTS

                                                               Page
Introduction                                                        1
Water Uses                                                         3
Water Quality Criteria                                                 7
Implementation Plan                                                  15
Explanation of Terms                                                 19
State and Federal Agency Addresses                                       21
                             TABLES
 I.  Water Use Designations by Basin                                     5
II.  Water Quality Criteria by Basin                                      14
                            FIGURES
I.   Arkansas Major Streams

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SUMMARY  OF  WATER QUALITY STANDARDS

                                FOR

  THE  INTERSTATE WATERS  OF ARKANSAS
  INTRODUCTION
  In the Water Quality  Act of 1965, Congress authorized the establishment of
  water quality standards for interstate waters. The purpose of these standards
  is to protect the public health and welfare and enhance the quality of the
  Nation's interstate waters to serve a variety of beneficial uses, such as public
  water supply, recreation, protection of aquatic life, industrial, and agricul-
  tural uses. This publication summarizes the standards for the general informa-
  tion of the  public and Federal, State and local officials as to the uses and
  associated requirements for interstate water-ways in the State of Arkansas.

  The Act, which amended the Federal Water Pollution Control Act, provided
  for the States to establish standards for their interstate waters, which were
  then subject to review and  approval by  the Secretary  of the Interior.* All
  States, and  the District of Columbia and the Territories of Guam,  Puerto
  Rico and the Virgin Islands participated in this landmark effort to set stand-
  ards. In the course of establishing the standards, public hearings were held
  by the States and other jurisdictions noted above to give the public  an op-
  portunity to participate.

  Arkansas adopted standards for its interstate waters on May 26, 1967, which
  were then submitted  to the Department  of the Interior. Subsequently, cer-
  tain revisions were made by  the State  in the original standards, and the
  Secretary  of the Interior approved the standards, as revised, on August 7,
  1967. At  the request  of the Secretary of the Interior, Arkansas adopted a
  policy to  protect its  high quality waters. The approved standards are thus
  both State  and Federal Standards, enforceable under the Arkansas water
  pollution  control statutes and the Federal Water Pollution Control Act, as
  amended (Section 10).
  *After December 2, 1970, the Administrator of the Environmental Protec-
  tion Agency.

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The interstate waters for which standards were adopted are listed below and
depicted in  Figure I.

The water quality criteria established by Arkansas apply to the following
interstate streams:

UPPER WHITE, NEOSHO, GRAND BASINS

Illinois River, Spavinaw Creek, Barren Fork, Elk River,  White River (above
Newport), Black River,  Current  River,  Eleven  Point  River, Spring  River,
English Creek, and King's River.

LOWER WHITE BASIN

White River (Newport to Mississippi River) and Cache River.

ST. FRANCIS BASIN

Pemiscot Bayou, Buffalo Creek and St. Francis River.

ARKANSAS BASIN

Arkansas River and Poteau River.

UPPER OUACHITA BASIN

Upper Ouachita River down  to and including mouth of Little Missouri River.

LOWER OUACHITA BASIN

Bayou Macon. Boeuf River,  Bayou Bartholomew, Overflow Creek,  Chemin-
a-Haut Creek, Ouachita  River (Mouth of Little  Missouri to Louisiana line),
Bayou Loutre, Little Cornie Bayou, Three Creeks, Cornie Bayou, and Big
Cornie Creek.

RED RIVER BASIN

Little River, Dorcheat B^you, Bodcaw Creek, Lelly Bayou, McKinney Bayou,
Sulphur River, and Red River.

MISSISSIPPI RIVER

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The standards  consist of three  major components: designation of the uses
which the waters are to serve, specification of narrative and numerical criteria
to protect and enhance water quality, and specification of a plan of imple-
mentation and enforcement, which includes treatment and control require-
ments for municipal, industrial and other wastes discharged to or affecting
the waters. These components  are  discussed in the  following sections; all
three are  essential  to a complete standards  program.

The standards are now being implemented. However, there will be continu-
ing research on water quality requirements for various beneficial uses and for
improved  collection and  evaluation of water quality data. As more informa-
tion becomes available and experience with implementing the standards is
gained,  the standards will be refined and improved  to reflect this new know-
ledge.

Should more detailed information be required on any aspect of the standards,
it may be obtained from the Arkansas Department of Pollution Control and
Ecology,  Little Rock, Arkansas, or the Environmental Protection Agency
Regional  Office in Dallas,  Texas. On March  26, 1971, Arkansas established
water quality standards for its intrastate waters. Information on these stand-
ards may  also be obtained  from the Arkansas Department of Pollution Con-
trol and Ecology. The addresses of these offices are given on page 21.

WATER USES

The designation by the State of Arkansas of specific uses in all river basins is
to protect present uses, recognize practicable future uses, provide where pos-
sible  for  a  variety of uses, and to assure compatibility of standards with
Federal, State and local resource planning. With few exceptions, the streams
of Arkansas contain waters of a quality suitable for all legitimate uses without
the necessity of unreasonable water treatment. Where man-made pollution
exists, substantial progress has been and is being made  in abatement.

It is the purpose of. these criteria to preserve and enhance the quality  of this
water so that it shall  be reasonably available for all beneficial uses and thus
promote the social welfare and economic well-being of the people  of the
State. To  satisfy the intent of the Federal Water Pollution Control Act to en-
hance water quality, the  standards specifically provide that no  interstate
waters may be used solely or primarily for waste assimilation. The waters must
be aesthetically pleasing, and this  quality  is protected by narrative criteria
preventing unsightly  or  obnoxious conditions,  such  as floating debris, oil
slicks, unpleasant  odors, and colors.

Specific use designations for all waters covered by the  standards are provided
in Table I.

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WATER QUALITY CRITERIA


The  protection  of water quality and  uses requires the establishment  01
numerical and narrative limits  on pollutants which damage these uses. The
water quality criteria in this section reflect the  best scientific judgment avail-
able  as to the water quality requirements for the assigned uses. Numerical
criteria are used wherever it is reasonable to do so. However, narrative cri-
teria are  also necessary  in some cases, particularly with respect to aesthetic
considerations.

Some waters have  a higher quality than the minimum levels assigned for pro-
tection of water uses, and the  standards seek  to protect this higher quality
as much  as possible in  the  face of increasing  social and economic develop-
ments. Scientific knowledge about the exact water  quality requirements for
every use is limited, and by preventing degradation of high quality waters, the
standards seek to  assure optimum, not marginal, conditions to protect the
uses  associated  with clean waters. The water quality criteria to protect the
designated uses in  each  river basin is shown below under general and specific
criteria and in Table 11. Also included is a statement on controlling degrada-
tion of high quality waters, by the Arkansas Department of Pollution Control
and Ecology.
GENERAL CRITERIA

     1.   Methods  —  The  methods  of  sample  collection,  preservation,
         measurements and analyses shall be in accordance with the latest
         edition of "Standard Methods For The Examination of Water and
         Wastewater" or other proven methods acceptable to the Depart-
         ment.

     2.   Location  — The effect of wastes on the receiving stream shall  be
         determined  after the wastes have been thoroughly mixed with the
         stream  water, but consideration may also be given to the quality
         of the  waste effluent in determining the adequacy of treatment.

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     3.   Ephemeral Streams — Where  there are streams with intermittent
         flow, the treatment of waste discharged  thereto shall be no less
         than conventional secondary or equivalent if reasonably required
         to protect present and projected future downstream uses.

     4.   Stream  Flows  — These criteria  are based upon the assumption
         that existing flow conditions in  interstate streams shall  continue
         without  material change. The minimum weekly flow that occurs
         on  the  average once in 10 years will be used in applying these
         criteria.

     5.   The quality  of streams tributary to the interstate streams shall
         be  controlled  so that  the quality of the interstate streams will
         not be lowered beyond the  criteria set herein.


SPECIFIC CRITERIA

     1.   Temperature — The maximum temperature shall not be elevated
         above 68° F. in trout streams, 86° F. in small-mouth bass streams,
         and 95° F. in other streams. The temperature of a stream as deter-
         mined by  natural conditions  shall  not be increased or decreased
         more than 5° F. by discharges thereto.

     2.   Color —  True color shall not be increased to the extent that it will
         interfere with present usage and projected future use of the stream.

     3.   Turbidity — There shall be no distinctly visible increase in  turbidity
         due to waste  discharges to the stream.

     4.   Taste and Odor —  Taste and odor producing substances shall  be
         limited  to concentrations in the stream that will not  interfere
         with the  production  of potable  water by reasonable water treat-
         ment processes, or impart unpalatable flavor to food fish, or  re-
         sult  in  offensive  odors arising  from  the  stream, or  otherwise
         interfere  with  the  reasonable  use  of the water.

     5.   Solids, Floating Material, and Deposits — The stream shall have  no
         distinctly visible solids, scum or foam of a persistent nature, nor

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         shall there be any formation of slimes, bottom deposits or sludge
         banks, attributable to waste discharges.

     6.  Oil and Grease - The stream shall be essentially free of the relative-
         ly nonvolatile liquid components that contribute to the formation
         of oil films, deposits and emulsions.

     7.  pH — The pH of water in the stream must not fluctuate in excess
         of  1.0 pH unit, within the range of 6.0 -  9.0, over a  period of
         24 hours. The pH shall not be below 6.0 or above 9.0 due to wastes
         discharged to the receiving stream.

     8.  Dissolved Oxygen (D.O.) - The dissolved oxygen in the stream
         shall not be less than 4 ppm, and this  shall  be the critical deficit
         point of the dissolved oxygen profile. The only exception will be
         when periodic lower  values are of  natural  origin and  therefore
         beyond  control of  the water  user. For trout stream waters the
         minimum dissolved oxygen content shall not  be  less  than 5.0
         mg/1. The dissolved oxygen sample  shall  be taken at  mid-depth
         and the middle of  the stream on  the  smaller streams and rivers.
         On  the larger rivers the dissolved oxygen  shall be determined by
         the average of concentrations in samples collected at quarter points
         across the river,  and at two-tenths and eight-tenths of the depth
         at each point.

     9.  Radioactivity -  The  Rules and  Regulations for the Control of
         Sources of Ionizing Radiation,  of the Division  of Radiological
         Health,  Arkansas Department of Health,*  shall  apply  as to the
         limits established for radiation levels in uncontrolled areas.

    10.  Bacteria  —  The Arkansas Department of Health  has the responsi-
         bility of approving  or disapproving surface  waters for swimming
         and drinking water  supply, and it has issued rules and regulations
         pertaining to  such  uses.  The regulation  of the Department of
         Pollution Control and  Ecology states that the  coliform group
         shall not exceed  1000/100 milliliters as a monthly average  value
         (either most probable  number  or  membrane  filter count)  for
*Priorto July 1, 1971, the Arkansas State Board of Health.

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         waters  substantially used for body contact aquatic sports; nor
         exceed  this number in more  than twenty percent of the samples
         examined during any one month; nor exceed 2,400/100 milliliters
         on any day except during periods of storm water runoff; provided,
         however, that  no fecal contamination is known to be present. In
         other waters, the  coliform bacteria group shall not exceed 5,000/
         100 milliliters  as  a  monthly average value (either Most  Probable
         Number or  membrane filter  count); nor  exceed  this number in
         more than  twenty percent  of the samples examined  during  any
         month;  nor exceed 20,000/100 milliliters in more  than 57< of
         such samples.  Arithmetic averages  will be  used.

    11.  Toxic Substances — Toxic materials, organic or inoganic,  shall
         not be  present in such quantities  as to cause the waters to be
         toxic to human, animal, plant or aquatic life or to interfere with
         the normal propagation of aquatic life. For aquatic life and using
         bioassay techniques, the level  of toxic materials in the stream shall
         not exceed one-tenth  (0.1) of the  forty-eight (48) hour Median
         Tolerance  Limit.

    12.  Mineral Quality — Waste discharges shall not affect existing mineral
         quality so as to  interfere with other beneficial uses.  Recognizing
         that the present water quality of the Arkansas and Red Rivers is
         less than  desirable  from  natural  as  well as  manmade  sources,
         additional mineral discharges  will  be limited  with the  intent of
         improving the quality as  plans  for removing majoi natural salt
         sources  are implemented. In the lower Ouachita River Basin  it is
         recognized  that water quality is low due primarily to manmade
         sources, but constantly improving under existing controls. Numeri-
         cal  mineral criteria  will be set and  implemented within the next
         five years* as  existing quality and results of the present controls
         are evaluated.
*By August 2, 1972.
                                  10

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ARKANSAS NON-DEGRADATION RESOLUTION

WHEREAS,  the Arkansas  Pollution Control Commission*  has heretofore
promulgated Regulation  No. 2, establishing water quality criteria for inter-
state  streams within the State of Arkansas, pursuant to the provisions of
Section 3 of the Arkansas Water and Air Pollution Control Act (Act 472 of
the Acts of Arkansas for 1949, as amended; Ark. Stats., §82-1904), and
in compliance with the requirements of the Federal Water  Quality Act of
of 1965  (Public Law 89-234, 33 U.S.C.A., §466g); and

WHEREAS, said Regulation provides that "The criteria are designed to en-
hance  the quality, value, and beneficial uses of the water resources of the
State of Arkansas and  to aid the prevention,  control, and abatement of
water pollution"; and

WHEREAS, said Regulation further provides that "It is the purpose of these
criteria to preserve and enhance the quality of this water so that is shall be
reasonably available for all beneficial uses and thus promote the social  wel-
fare and economic well-being of the people of the State"; and

WHEREAS,  said  Regulation further  provides for a clear and  unequivocal
non-degradation policy, to-wit:

     "3.  The water quality  criteria herein contained shall not be construed
     as permitting any waste  amenable to treatment  or control to be dis-
     charged into any water of the State of Arkansas  without reasonable
     treatment  or control.  The Arkansas Water and Air Pollution Control
     Act provides, among  other  things, that it shall be unlawful for any
     person to  discharge any waste into any waters of the State without hav-
     ing  first obtained a written  permit from the Commission. A disposal
     permit may not be issued unless there is submitted to the Commission
     plans and  specifications for a disposal system adequate  to treat or  con-
     trol the wastes so as not to cause  water pollution as defined in the  Act.
     Such treatment or  control must be consistent with the  state of the art
*After July 1, 1971, the Arkansas Department of Pollution  Control  and
 Ecology.
                                  11

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     and best practicable industry standards, the minimum requirements be-
     ing secondary treatment or equivalent, giving due regard to quality and
     flow of the receiving waters, the present, future and potential uses of
     such waters, economic feasibility, and other relevant factors".
and
WHEREAS, the Water Quality Standards for Interstate Streams adopted by
the Commission, of which Regulation No.2 is an integral part,  were approved
without exception  by the Secretary  of Interior on  August 7, 1967; and

WHEREAS, subsequent to such approval the Secretary  of the Interior and the
Federal Water Pollution Control Administration* articulated a non-degrada-
tion  policy,  which has been  authoritatively construed and explained by
responsible officials of the Department of the Interior as set forth in a Com-
pendium dated August, 1968; and

WHEREAS, the  non-degradation policy  incorporated in  Regulation  No.  2,
making clear  that waters of existing quality  higher than the established
standards  may not  be degraded by untreated waste discharges even though
the resulting water quality might comply with the standards and  that a waste
disposal permit,  as  required by  law, will not be issued by the Commission
unless  the  treatment  or control is consistent with the stale of the art and
best practicable industry standards (the minimum requirements being second-
ary treatment or equivalent), is at least as strong as that subsequently adopt-
ed by  the  Secretary of the  Interior and is fully  consistent  therewith; and

WHEREAS, the  Commission wishes to assure  the  Secretary of the Interior
and Federal Water  Pollution Control  Administration  of its  cooperation  in
implementing the Arkansas Water Quality Standards in general and the non-
degradation policy in particular, including the furnishing of relevant informa-
tion and data;

NOW,  THEREFORE, BE  IT  RESOLVED,  That the Arkansas Pollution
* After December 2, 1970, the Administrator of the Environmental Protec-
 tion Agency.
                                  12

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 Control  Commission,  its agents, servants, and employees,  shall  cooperate
 with the Secretary  of Interior and  the  Federal  Water Pollution  Control
 Administration in implementing the Arkansas Water Quality Standards and
 the  non-degradation policy incorporated  therein.  In connection  with such
 implementation, the Secretary of the Interior and the Federal Water Pollution
 Control Administration will be kept advised and will be provided with such
 information as they will need  to discharge their responsibilities  under the
 Federal Water Pollution  Control Act, as amended.

 BE  IT FURTHER RESOLVED, That  the Director of the Commission is
 hereby authorized and directed to take such  action as may be necessary  or
 appropriate to effectuate the foregoing.

 Resolved the 25th day of October,  1968.
Resolved, That the statement adopted by  the  Arkansas Pollution Control
Commission on October 25, 1968 concerning implementation of the Arkansas
Water  Quality  Standards and  the  Federal Water Pollution  Control non-
degradation policy is hereby amended by adding a new paragraph immediate-
ly prior to the concluding paragraph  thereof reading as follows:

Be It Further Resolved, That it is recognized that certain of the waters of the
State  possess an existing quality which is better than established standards.
The quality of these waters will be  maintained  unless and until it has been
affirmatively demonstrated to the Commission that any reduction in quality
is justifiable as a  result of necessary economic or social  development.

Resolved the 28th day  of March,  1969.
                                  13

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IMPLEMENTATION PLAN

The  "action"  plan  of  the  standards is the plan of implementation ana en-
forcement. For example, Arkansas regulations provide that the discharge of
wastes into interstate waters or portions  thereof, which reduces the quality
of such  waters  below the water quality criteria established by regulation
(whether  the  matter  causing or  contributing  to  such reductions is  dis-
charged directly into such waters or reaches such waters after discharge into
tributaries of such waters)  is subject to the abatement and enforcement pro-
visions of the Arkansas Water and Air Pollution Control Act.

The  implementation plan sets forth the  requirements for treatment and/or
control of all conventional municipal and industrial  waste  discharges that
affect Arkansas waters. It also specifies the time within which treatment of
wastes is to be accomplished, and contains programs for dealing with other
water pollution control problems. In general, the Arkansas standards call for
a level of waste  treatment or control that must be consistent with the state-
of-the-art and  best practicable industry standards, the minimum requirement
being secondary treatment or equivalent, giving due  regard to quality and
flow of the receiving waters, the present, future and  potential uses of such
waters, economic feasibility,  and other relevant factors. The installation of
secondary treatment facilities  or their equivalent for  all municipal and in-
dustrial wastes is scheduled to be completed by the end of 1972. Detailed
information on  the treatment requirements for any particular waste water
may  be obtained from the Arkansas Department of Pollution Control and
Ecology.

This  Department is composed of ten members; six of these represent various
state agencies directly  concerned with pollution: the Department of Health,
Game and Fish Commission, Oil and Gas Commission, Soil and  Water Con-
servation Commission,  Geological Commission,  and  State Forestry Commis-
sion.  The other four  members  are  appointed  by  the Governor with  the
approval  of the State Senate, and represent industry, municipalities, mining,
and agricultural and livestock interests in the State.

Arkansas statutes provide for the control  of water pollution on the basis of a
permit system. Under  this  system an  industry or municipality must submit
complete  plans  and specifications for  waste  treatment facilities to  the
                                   15

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Department for approval and issuance of a permit before construction may
commence.  Industries  are required to submit a process flow sheet showing
each step in the  industrial process, and a materials  balance showing types
and quantities of materials that go into and leave each step in the industrial
process, including flow rates of water for present and  proposed future opera-
tions. Industrial  treatment  facilities,  as well as  municipal, are checked as
soon after construction as  possible to assure  compliance with the  permit
issued  and  to determine  if  efficiency of  waste treatment  is  adequate.

The  basis for most Department enforcement and corrective activity is the
basin survey. This is a  part of a routine and continuous observation to check
the efficiency of waste treatment  plants and their effects on  the receiving
streams. The waste survey consists of  twenty-four hour composite sampling
of each  municipal and  industrial waste stream for five days with appropriate
chemical analysis of each sample.  Flows are  measured continuously for ten
days in order to obtain averages  and extremes.  Where treatment facilities
exist, sampling is accomplished at  each stage of treatment  in order to obtain
efficiencies  and  locate possible problems. Streams that receive these wastes
are sampled on four different days above each point of discharge and at sev-
eral points below, covering a sufficient distance to determine the nature and
the extent of any damage to the watercourse. In addition to chemical analysis
of the stream, a complete biological analysis is performed including classifica-
tion and counts of plankton, bottom organisms, bacteria, and fish  life. Upon
completion  of the field work, all engineering, chemical, and biological data
is  tabulated and  a detailed report  including procedures, results, and  recom-
mendations is submitted for Department action.

The  State has been  divided into eight districts based on  concentrations of
potential  pollution  sources. Field inspectors  are responsible  for periodic
spot surveys of  all  significant wastewater  discharges in their district plus
monitoring of interstate and other streams for compliance with the  standards.

The  Arkansas Game and Fish Commission has at least two wildlife officers
in each of the State's seventy-five counties who are on the alert for pollution,
especially if it results  in fish kills. The Fisheries Division  also  monitors the
temperature of trout streams.
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When abatement action becomes  necessary, the sequence usually follows
this pattern:

     a.   Complete basin survey.
     b.   Public Hearing.
     c.   Issuance of a general order.
     d.   A "show cause" hearing.
     e.   Issuance of a  specific order.
     f.   Litigation.

For specific cases in response to  complaints, or for irregularities found dur-
ing routine inspection, or because of predicted overloads based on treatment
plant files, the following sequence is normal:

     a.   Spot survey.
     b.   A "show cause" hearing.
     c.   Issuance of specific order.
     d.   Litigation.

In the event of pollution  immediately endangering the health  and welfare of
the public, the cease and desist order  is issued immediately followed directly
by litigation, if necessary.

The  Arkansas portion of the Arkansas River navigation  project will present
potential pollution problems that involve barge accidents and  oily and other
discharges from vessels. Such problems will be handled  in a manner similar
to fish kills, depend ing on notification and reporting by wildlife  officers of the
Arkansas Game and Fish Commission, field inspectors of the Arkansas Depart-
ment of Pollution Control and  Ecology, lock  and dam personnel,  marina
operator and other private citizens. Sanitary discharges from  navigation ves-
sels are presently controlled statewide  by the Arkansas Department of Health
under Rules and Regulations Pertaining to Marine Toilets and Disposal of
Sewage  from Boats.

Of major importance is water quality degradation caused by natural brine
emissions and by disposal of oil field brines in the watersheds of the Arkansas,
Ouachita, and Red Rivers. In the Arkansas and Red Rivers, excessive mineral
content results primarily  from natural brine emissions  upstream from  the
Arkansas boundary and eliminates  use of these waters for drinking purposes.
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The Arkansas Department of Pollution Control and Ecology has implement-
ed a successful program  for abatement of  mineral pollution from oil field
brines in the Ouachita and Red River basins. Additionally, Federal programs
now are under way to correct  natural mineral pollution in the Arkansas and
Red River watersheds but the results of these programs will not be known
for  several years.

The Arkansas  Department of Pollution Control  and Ecology has adopted a
state-wide policy to eliminate water quality  problems arising from combined
sewer systems. The Department policy is one of allowing no new combined
sewers while eliminating present systems by  scheduled construction projects.
The Department  has also adopted a  sewer use ordinance  which  limits by
name the amounts and types of pollutional materials which can be discharged
into the system.

The Arkansas Soil and Water Conservation Commission administers the Small
Watershed Program which alleviates siltation of surface waters from land
runoff.

Other existing water quality problems are  acid mine drainage, agricultural
feedlots and runoff, irrigation return flows, and nutrients  from municipal
sewage treatment plant discharges. As the technology for feasible solutions
improves, progress will  be made toward abatement of these problems to en-
hance the quality of Arkansas waters.

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EXPLANATION OF TERMS

 1.   Bacteria - For many years the best indicator of the sanitary quality of
     water has been an estimate of the density of coliform bacteria.  The
     results of this test are not specific in that many bacteria common to the
     soil are included;  therefore many agencies have not been satisfied with
     criteria based on this test. More recently, tests have been developed for
     the determination of fecal coliform and fecal  streptococci. However,
     sufficient information has not been developed to properly evaluate the
     results of these tests. Until criteria are developed  which are more specific
     the Arkansas Department of Pollution Control and  Ecology shall use
     the criteria given in Regulation No. 2 for bacteria.

 2.   Dissolved Oxygen (D.O.) — Due to the diurnal fluctuations of dissolved
     oxygen in streams, the  minimum dissolved  oxygen value shall apply at
     or near the time of the average concentration in the stream, taking  into
     account the diurnal fluctuations.

 3.   Ephemeral Streams — Those streams that have  no natural flow on the
     average of one (1) day  in two (2) years.

 4.   Interstate Streams - All major interstate streams have been included in
     the listing in Regulation 2. Others not included but  which were listed
     in the Federal Inventory will fall under the normal Department pollu-
     tion control  program under Act 472.

 5.   Milliliter — One-thousandth of a liter. One  liter is equal to 1.06 quarts.

 6.   pH - the pH  value indicates the relative intensity of acidity or alkalinity
     of water, with the neutral point at 7.0. Values  lower than 7.0 indicate
     the presence  of acids; above 7.0, the presence of alkalies.

 7.   Ppm  -  Parts per million, also referred to as  milligrams per liter (mg/1.).
     This  is a unit  for expressing the  concentration  of  any substance by
     weight, usually as grams of substance per million grams of solution. Since
     a liter of water weighs one kilogram at a specific gravity  of 1.0, one  part
     per million is equivalent to one milligram per liter.
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 8.  Secondary Treatment — The removal of practically all suspended solids
    and the reduction of the biochemical oxygen demand at all times by at
    least eighty-five (85) percent, and may include the in-plant control of
    industrial wastes as prescribed by the Department.

 9.  Temperature — The limitation of temperature increase or decrease of
    5° Fahrenheit from natural temperature conditions is so that a thermal
    shock barrier is prevented within the stream.

10.  Stream  Flow — On certain streams present low flows will be increased
    by minimum releases from future control structures.

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        STATE AND FEDERAL AGENCY ADDRESSES
A.  STATE

    Arkansas Department of Pollution Control and Ecology
    8001 National Drive
    Little Rock, Arkansas 72209

B.  FEDERAL

    Environmental Protection Agency
    Region VI
    1600 Patterson, Suite 1100
    Dallas, Texas 75201

    Environmental Protection Agency
    Washington, D. C. 20460
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