Management of Non-Point Source Pollution CE 296B - PowerPoint PPT Presentation

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Management of Non-Point Source Pollution CE 296B

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Management of Non-Point Source Pollution CE 296B Department of Civil Engineering California State University, Sacramento Lecture #14, March 26, 1998 – PowerPoint PPT presentation

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Title: Management of Non-Point Source Pollution CE 296B


1
Management of Non-Point Source PollutionCE 296B
  • Department of Civil Engineering
  • California State University, Sacramento

Lecture 14, March 26, 1998 Receiving Water
Impacts - Part I
2
I. Receiving water impacts - Introduction
  • A. A central need of the overall effort to manage
    non-point source pollution is to discover the
    impacts that pollution is having on receiving
    waters. This is important to
  • 1. Focus efforts, and finite resources, on
    pollution that is causing the problem.
  • 2. Identify potential changes to land use policy
    that might help preserve the quality of water
    bodies in the future.
  • 3. Better identify aspects of water quality, both
    qualitatively and quantitatively, that affect
    beneficial uses.

3
I. Receiving water impacts - Introduction (cont.)
  • B. Fundamental problems exist in assessing the
    impact of non-point source pollution on receiving
    waters. Some of the problems exist everywhere
    and some are unique to arid climates such as
    California.
  • 1. Problems that exist everywhere
  • Differentiating between the effect of non-point
    source pollution from point source pollution,
    particularly when common constituents exist.
  • Differentiating beneficial from detrimental
    impacts of a particular constituent.

4
I. Receiving water impacts - Introduction
(cont.) B. Fundamental problems exist in
assessing the impact of non-point source
pollution on receiving waters. Some of the
problems exist everywhere and some are unique to
arid climates such as California. 1. Problems
that exist everywhere (cont.)
  • Differentiating between background concentrations
    and anthropogenic concentrations.
  • Establishing a priority ranking for
  • Problems within a receiving water
  • One receiving water from another

5
I. Receiving water impacts - Introduction
(cont.) B. Fundamental problems exist in
assessing the impact of non-point source
pollution on receiving waters. Some of the
problems exist everywhere and some are unique to
arid climates such as California. (cont.)
  • 2. Problems unique to arid climates
  • Substantial use of receiving water for
    irrigation.
  • Dramatic changes in flow rate from wet to dry
    season.
  • Normal pattern of successive drought years
    alternating with flood years.

6
Discussion Break
  • What are some of the problems in assessing
    receiving water impacts with respect to seasonal
    flow rate changes?
  • What are some of the problems in assessing
    receiving water impacts with respect to flow rate
    changes associated with alternating drought and
    flood conditions?
  • How about differentiating detrimental effects
    associated with natural phenomena vs. human
    impacts?

7
Discussion Break
  • Take as correct the assumption that the problems
    associated with determining the magnitude of a
    receiving water bodies impairment and in
    correctly assessing the causes, particularly in
    apportioning blame, are fundamental.
  • This is not news.
  • What effect has this had on the drafting of
    environmental laws and the regulations those laws
    promulgated?

8
I. Receiving water impacts - Introduction (cont.)
  • C. Currently two primary schools of thought exist
    on how to assess the quality of a receiving water
    and the impact that pollution, point and
    non-point has had on those waters
  • 1. The traditional approach. Setting beneficial
    uses, establishing the water quality standards
    required to meet those uses, and then testing the
    waters to see if those standards are met.
  • If the standards are not met, figure out who is
    responsible.

9
I. Receiving water impacts - Introduction
(cont.) C. Currently two primary schools of
thought exist on how to assess the quality of a
receiving water and the impact that pollution,
point and non-point has had on those waters
  • 2. The environmental indicator approach. In
    brief, this is, from several different different
    perspectives examining the overall health of the
    receiving water body. Much more later, but some
    indicators are
  • The diversity of species present, at several
    different levels
  • Flooding frequency

10
I. Receiving water impacts - Introduction (cont.)
  • D. An EPA report to Congress in 1988 on the
    health of the nations receiving waters indicated
    that for
  • 1. Rivers and streams
  • 70 of the river miles were fully supporting
    designated uses.
  • 20 of the river miles were partially supporting
    designated uses.
  • 10 of the river miles were not supporting
    designated uses

11
I. Receiving water impacts - Introduction
(cont.) D. An EPA report to Congress in 1988 on
the health of the nations receiving waters
indicated that for (cont.)
  • 2. Lakes (excluding the Great Lakes, but
    including Lake Champlain!!!)
  • 74 of the lake area fully supporting the
    designated uses.
  • 17 of the lake area partially supporting the
    designated uses.
  • 10 of the lake area did not support the
    designated uses.

12
I. Receiving water impacts - Introduction (cont.)
  • E. So what we would like to do by assessing
    receiving water impacts is
  • 1. Insure that those water bodies that are fully
    supporting beneficial uses continue to do so.
  • 2. Make reasonable progress in restoring
    beneficial uses to the other water bodies.
  • What we need from the assessment of receiving
    water impacts is information to guide our efforts.

13
II. Traditional method for evaluating receiving
water impacts.
  • A. Steps taken to assess receiving water impacts
    the traditional way might be as follows
  • 1. Assign historical, present, and potential
    beneficial uses to the water body.
  • 2. Assign water quality standards (objectives) to
    meet the beneficial uses.
  • 3. Determine the background concentrations of the
    constituents associated with the water quality
    objectives.
  • An assumption, false as it turn out, is that
    background concentrations are constant.

14
II. Traditional method for evaluating receiving
water impacts. (cont.) A. Steps taken to assess
receiving water impacts the traditional way might
be as follows (cont.)
  • 4. Measure concentrations and compare those
    assessments with
  • Background levels
  • Water quality objectives
  • 5. Measure effluent concentrations of regulated
    dischargers, point and non-point.
  • 6. Determine how much of the elevated
    concentrations are due to point source discharges.

15
II. Traditional method for evaluating receiving
water impacts. (cont.) A. Steps taken to assess
receiving water impacts the traditional way might
be as follows (cont.)
  • 7. Calculate, by difference, the contribution
    from non-point (diffuse) sources.
  • 8. If concentrations are measurably greater than
    background, but less than water quality
    objectives, determine the pollutant most likely
    to cause a problem in the future and focus on
    that as an issue.

16
II. Traditional method for evaluating receiving
water impacts. (cont.) A. Steps taken to assess
receiving water impacts the traditional way might
be as follows (cont.)
  • 9. If concentrations exceed water quality
    objectives, regulated dischargers will have to
    reduce the amount of pollutants they discharge.
  • 10. Based on the trends observed in concentration
    measurements, determine the quantitative
    improvements pollution management efforts are
    having.

17
II. Traditional method for evaluating receiving
water impacts.
  • B. Crucial problems associated with the
    traditional approach.
  • 1. Evaluation of receiving water impacts via the
    traditional approach take place at a individual
    moments in time.
  • The picture of a long period of time, what
    really matters for many beneficial uses, is not
    well considered.
  • 2. Background concentrations are not constant.
    Substantial changes occur with flow rate and time
    of year.

18
Discussion Break
  • What are some of the reasons that background
    concentrations, if they can be determined at all,
    are not constant?

19
II. Traditional method for evaluating receiving
water impacts. B. Crucial problems associated
with the traditional approach. (cont.)
  • 3. Measured concentrations are typically
    variable with flow rate and time of year.
  • What might seem like a substantial problem on
    September 15th, might not be of any concern on
    November 15th. (Another reason for seasonally
    adjusted water quality objectives.)
  • Whether action is demanded might depend heavily
    on the time the samples were taken.

20
Discussion Break
  • The flow rate in most rivers and streams in
    California is regulated by dams. How might the
    operator of a dam affect the assessment of
    receiving water impacts?

21
II. Traditional method for evaluating receiving
water impacts. B. Crucial problems associated
with the traditional approach. (cont.)
  • 4. The impact that constituents can have on many
    beneficial uses is far more complicated than the
    current water quality objectives approach
    assumes.
  • An excellent example of this are effect metals
    concentrations have on aquatic life. As we have
    seen, a fraction of total metals present have a
    toxic effect. Just measuring metals
    concentration tells us nothing about the fish.

22
II. Traditional method for evaluating receiving
water impacts. B. Crucial problems associated
with the traditional approach. (cont.)
  • 5. An even more complicated situation is the
    effect on dissolved oxygen concentrations. The
    text covers this with some thoroughness, a good
    example is
  • If BOD type pollution is reduced, the
    heterotrophic organism population will decrease.
    These organisms are predators of algae . If
    nutrients are not reduced as well, algae blooms
    will lead to high daytime dissolved oxygen
    concentrations and low nighttime concentrations.

23
II. Traditional method for evaluating receiving
water impacts. B. Crucial problems associated
with the traditional approach. (cont.)
  • 6. The effluent concentrations from point source
    discharges might be relatively constant, but the
    effluent concentrations from non-point source
    discharges will be highly variable.
  • Determining the quantitative contribution from
    the non-point source discharge is problematical.

24
II. Traditional method for evaluating receiving
water impacts. B. Crucial problems associated
with the traditional approach. (cont.)
  • 7. The traditional approach for evaluating
    receiving water impacts directs solutions to be
    technology driven, end-of-pipe approaches.
  • 8. Only concentrations are measured, aspects that
    can have a profound effect on the receiving water
    such as the size of peak flows are not included
    in the environmental side of the equation.

25
Discussion Break
  • How does the traditional approach to assessing
    receiving water impacts encourage the use of
    technology driven, end-of-pipe solutions?

26
II. Traditional method for evaluating receiving
water impacts. B. Crucial problems associated
with the traditional approach. (cont.)
  • 9. Determining if management efforts have
    produced statistically significant changes in
    pollutant concentrations in receiving waters is
    problematical at best.
  • Consider the following scenario
  • Management efforts have significantly reduced
    metals concentrations in non-point source
    effluent. During a drought year, the
    contribution from mine drainage and POTW effluent
    is elevated along with metals concentrations.

27
Discussion Break
  • What other scenarios, particular to arid
    climates such as California might make it very
    difficult to detect differences in receiving
    water pollutant concentrations?

28
II. Traditional method for evaluating receiving
water impacts.
  • C. Benefits of the traditional method for
    evaluating receiving water impacts
  • 1. The traditional method does conform with the
    law, both the Federal Clean Water Act and the
    California Porter-Cologne Act.
  • 2. The reliance on concentration measurements is
    at least somewhat understandable to the public.

29
A Preview of the Alternative Approach to
Assessing Receiving Water Impacts Environmental
Indicators - I
  • The idea is to take a holistic approach to the
    examination of the water body. To be included is
    aspects of the watershed.
  • This method is being developed using EPA funding
    with most of the current work being tested in
    Ohio and Maryland. It has no standing in the law
    and is by no means perfect, but does have some
    promise and the support of senior EPA officials.

30
A Preview of the Alternative Approach to
Assessing Receiving Water Impacts Environmental
Indicators - II
  • Six different categories of indicators are
    evaluated simultaneously, they are
  • Water quality indicators
  • Physical and hydrological indicators
  • Biological indicators
  • Social indicators
  • Programmatic indicators
  • Site indicators
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