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Altered Hydric Soils

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by: Wade Hurt, USDA, NRCS, NSSC/ University of Florida, Gainesville, FL, Chris Noble, USACE, Vicksburg, MS, and Victor Carlisle, University of Florida, Gainesville, FL. – PowerPoint PPT presentation

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Title: Altered Hydric Soils


1
Altered Hydric Soils
  • by
  • Wade Hurt, USDA, NRCS, NSSC/ University of
    Florida, Gainesville, FL, Chris Noble, USACE,
    Vicksburg, MS, and Victor Carlisle, University of
    Florida, Gainesville, FL.

2
Types of Altered Hydric Soils
  • Artificial
  • Drained (Protected)
  • Historic
  • Relict
  • The objectives of this lecture are to outline
    criteria used to identify each of these
    alterations and to outline the impact of
    alterations on the hydric status of a soil.

3
Development of Altered Soils
  • Hydrologic modification may result in
  • 1. Artificial Hydric Soils
  • 2. Drained (Protected) Hydric Soils.
  • Soil modification may result in
  • 1. Artificial Hydric Soils
  • 2. Historic Hydric Soils
  • 3. Relict Hydric Soils

4
Hydrologic Modification
  • Hydrologic modification results where saturation
    and/or inundation (ponding or flooding) has been
    changed by human or geologic processes.
  • Both geologic modifications and human
    modifications of hydrology may change the hydric
    status of a soil.

5
Soil Modification
  • Soil modification result where soils (not
    hydrology) have been altered either through
    geologic or human additions or removals.
  • Both geologic modifications and human
    modifications of a soil may change the hydric
    status of a soil.

6
Key
  • Hydric Soils are currently supporting or capable
    of supporting wetland ecosystems. Soil
    modifications are not needed to maintain or
    restore a wetland. In the case of drained hydric
    soils, only removal of hydrologic modifications
    are needed to restore wetlands.
  • Nonhydic soils currently are not supporting nor
    are they capable of supporting wetland
    ecosystems. Soil modifications are needed to
    create a wetland. Hydrology modifications may
    also create a wetland on nonhydric soils. The
    differences between creation and restoration will
    be discussed layer.

7
Review Why is a Soil Hydric
  • A soil is hydric because it
  • 1. Has a hydric soil indicator, or
  • 2. Meets hydric soil criteria 3 or 4, or
  • 3. By data meets the Hydric Soil
    Technical Standard (HSTS).

8
Artificial Hydric Soils
  • Wetness of these altered soils has been increased
    by human activities (constructed wetlands,
    irrigation leaks, rice fields, lake skeins and
    other construction activities) or the soils have
    been altered by human activities (constructed
    wetlands, pond fringes and other excavations).
  • These altered soils are hydric soils because
    they
  • 1. Have a hydric soil indicator, or
  • 2. Meet hydric soil criteria 3 or 4, or
  • 3. By data meet the HSTS.

9
Artificial Hydric Soil
This dug pond has an artificial hydric soil
fringe that was created when the pond was
constructed. It now supports a wetland ecosystem.
10
Artificial Hydric Soil
The wetland shown here and on the first slide was
created by removing soil material from a
nonhydric soil. The resulting soil is an
Artificial Hydric Soil.
11
Artificial Hydric Soil
Construction activities, note the railroad in the
background, may be the reason wetlands and hydric
soils exist here.
12
Drained (Protected) Hydric Soils
  • This is the 2nd type of altered hydric soils An
    attempt through human activities to decrease the
    wetness of these altered soils has been made
    (ditches, levees, dams, pumps, etc.).
  • Even with reduced wetness these altered soils
    maintain their hydric status because they
  • 1. Have a hydric soil indicator or,
  • 2. Meet hydric soil criteria 3 or 4 or,
  • 3. By data meet the HSTS.

13
Ditches, levees, dams, pumps, etc., do not alter
the hydric status of a soil.
14
Drained Hydric soils
  • The concept of drained hydric soils maintaining
    their hydric status should be thoroughly
    understood. This is important to wetland
    scientist. By recognizing a soil with a hydric
    soil indicator as being hydric regardless of
    hydrologic alteration we keep soils capable of
    supporting wetlands (if hydrology was restored)
    in the same class as soils that are currently
    supporting wetlands.
  • I have seen areas ditched, pumped, and protected
    by levees in the Mississippi delta that are in
    crop production (soybeans) that are still not
    drained hydric soils because they still pond
    water for up to one month during the growing
    season, still have a hydric soil indicator, and
    still meet the HSTS. One can hardly never
    underestimate the effect of ditches upon the
    hydric status of a soil.
  • In normal circumstances a wetland requires the
    presence of three criteria (wetland hydrology,
    wetland vegetation, and hydric soils). For an
    area to be a wetland each of these criteria are
    met independently.

15
Historic Hydric Soils
  • This is the 3rd type of altered hydric soils
    These altered soils have had additional soil
    material placed on top of the original soil by
    human activities to the extent that that they are
    no longer hydric (1993 flooding deposition on the
    Missouri River flood plain, filling a wetland).
    The additions may be intentional (illegal fill)
    or non intentional (erosional deposition).
  • These altered soils are nonhydric because they
  • 1. Do not have a hydric soil indicator and,
  • 2. Do not meet hydric soil criteria 3 or 4 and,
  • 3. Do not, by data, meet the HSTS.

16
Historic Hydric Soils are altered soils that were
once hydric but have had human modifications
(additions) such that they are no longer hydric.
The additions may be intentional (illegal fill)
or non intentional (erosional deposition).
Nonhydric Hydric
15 cm
17
Historic Hydric Soils
  • Even though fill material has been placed over
    the entire soil area shown in the previous slide
    it has areas that are still hydric as well as
    areas that are no longer hydric. The area to the
    right of the vertical arrow is still hydric even
    though fill material has been placed on the
    surface it has the HS Indicator S6 (Stripped
    Matrix) starting within 15 cm (6 inches) of the
    surface. The lower horizontal arrow indicated
    where the stripped matrix starts. The soil area
    to the left of the vertical arrow still has a
    stripped matrix but it starts below the depth
    required (15 cm) by the HS Indicator S6 (Stripped
    Matrix).
  • Can you think of other ways (other than the
    presence of a HS Indicator) that a soil can be
    proven to be hydric? What about monitoring to
    see if it floods or ponds long enough to satisfy
    Criteria 3 or 4 or monitoring to see if it meets
    the HSTS?

18
Areas which may have changed from hydric to
nonhydric.
Channelization and the resulting spoil may change
the hydric status of a soil. Also the
surrounding area may have reduced wetness.
Culvert
19
Historic Hydric or Still Hydric?
Depleted Matrix starts here
20
Historic?
  • The soil in the previous slide has had fill
    material placed over the original soil. The knife
    blade points to the limit of the 10YR 5/4 fill
    material (24 cm). The blue arrow points to the
    start of HS indicator F3, Depleted Matrix (28
    cm). This new soil is nonhydric because the
    depleted matrix does not start within 25 cm and
    because the fill material has a chroma of 4. This
    is a Historic Hydric Soil.
  • What if the same fill material was only 18 cm
    thick over the same underlying soil? This means
    the depleted matrix would start at 22 cm. Would
    the soil be hydric or nonhydric? This new soil
    would still be nonhydric. Remember the
    introductory Unless otherwise indicated,all
    mineral layers above any of the Indicators have
    dominant chroma 2 or less,or the layer(s)with
    dominant chroma of more than 2 is less than 15 cm
    (6 in)thick (Hurt, et al. 2002, p.5). It would
    still be a Historic Hydric Soil.
  • In this example the fill material would have to
    be less than 15 cm (6 in) thick for the soil to
    be a hydric soil.

21
Relict Hydric Soils
  • This is the 4th type of altered hydric soils
    These altered soils were once hydric but are no
    longer hydric due to geologic activities (pimple
    mounds of Texas Gulf Coast Prairie, stream
    downcutting).
  • Only on close examination is it evident that
    hydric soil morphologies do not exist.
  • These altered soils are nonhydric because they
  • 1. Do not have a hydric soil indicator and,
  • 2. Do not meet hydric soil criteria 3 or 4 and,
  • 3. Do not, by data, meet the HSTS.

22
Relict Hydric Soils
  • Several morphological characteristics can suggest
    relict redoximorphic features (Vepraskas, 1994).
    These are
  • 1. Feature type and boundary characteristics,
  • 2. Location to macropores,
  • 3. Redox feature color, and
  • 4. Pore lining continuity.

23
1. Feature and Boundary Characteristics
  • A. Nodules and concretions
  • B. Other redox concretions.

24
1 A Nodules and Concretions Feature and Boundary
Characteristics
  • Contemporary nodules and concretions have
  • 1. Diffuse boundaries (the color grade is
    commonly more than 2 mm wide),
  • 2. Irregular surfaces, and
  • 3. If smooth and round surfaces, red to yellow
    corona (halos) should be present.
  • Relict nodules and concretions may have
  • 1. Sharp boundaries (color grade is commonly less
    than 0.1 mm wide) and
  • 2. Smooth surfaces.

25
Relict Features
These redoximorphic features (nodules) most
likely are relict because they have sharp
boundaries and smooth surfaces. (photograph
Vepraskas. 1994)
26
1 B Other Redox Concentrations Feature and
Boundary Characteristics
  • Contemporary redox concentrations have diffuse
    boundaries.
  • Relict redox concentrations may have sharp
    boundaries.

27
Contemporary redox concentrations have diffuse
boundaries. Relict redox concentrations may have
sharp boundaries.
3 cm
1 cm
28
2 Redox Macropore Features
  • Contemporary macropores may have
  • Fe depletions along stable macropores in which
    roots repeatedly grow that are not overlain by
    iron rich coatings.
  • Relict macropores may have
  • Fe depletions along stable macropores in which
    roots repeatedly grow that are overlain by iron
    rich coatings.

29
3 Redox Color Features
  • Contemporary redox colors may be the results of
    the iron minerals
  • 1. Ferrihydrite (5YR), Lepidiocrocite (7.5YR),
    Goethite (7.5YR, 10YR), and Jarosite (2.5Y) and
  • 2. Have value and chroma 4 or more.
  • Relict redox colors may be the results of the
    iron mineral
  • 1. Hematite (10R, 5R, 2.5YR) and
  • 2. Have value and chroma lt4.

30
4 Pore Lining Continuity
  • Contemporary pore linings may be continuous
    especially around living roots. Relict pore
    linings may be broken and unrelated to live
    roots.
  • Pictured below is a continuous pore lining
    (reddish area) parallel to a reduced area
    (blue-green).

31
Relict Hydric Soils Texas Gulf Coast Prairie
Present Land Surface Geologic Land Surface
Geologic Hydric Soil Boundary
Telferner
Present Hydric Soil Boundary
2m
Nada, Dry
Nada, Wet
0-10 cm lfs 10YR 5/3 10-29 cm sc 10YR 5/2 cd
10R 3/3
Cieno
0-19 cm fsl 10YR 4/2 19-27 cm scl 10YR 4/2 fd
7.5YR 4/6
0-12 cm fsl 10YR 4/2 12-29 cm scl 10YR 4/2 cd
7.5YR 4/6
0-10 cm l 10YR 5/3 cd 7.5YR 4/6 10-25 cm sl
10YR 5/2 cd 7.5YR 4/6
cd common distinct fd few distinct
32
Relict Hydric Soils Texas Gulf Coast Prairie
  • The landscape depicted in the previous slide
    shows an area where climatic changes have made
    what once was the lowest area (Telferner soils)
    is now the highest area. Only by close
    examination do we know that the Telferner soils
    are now relict hydric soils the redox
    concentrations are 10R 3/3. cd common distinct
    and fd few distinct

33
Redox features forming
Original surface
Fill
34
Time and the formation of redox features
  • The soil shown on the previous slide has fill
    material about 10 inches thick placed over the
    original soil that had a depleted matrix.
  • The fill material had been in place for only a
    few years and redox features are forming in the
    lower ½ of the fill material indicating that in a
    few more years a hydric soil indicator would be
    present in the new soil.

35
Summary
  • The types of Altered Hydric Soils are Artificial,
    Drained (Protected), Historic, and Relict hydric
    soil. Artificial hydric soils were once nonhydric
    but now are hydric soils created by human
    modifications to hydrology (additional water) or
    soil (removal of soil). Drained hydric soils
    were hydric and still are hydric soils created
    by human modifications to hydrology. Historic
    hydric soils were once hydric but are now
    nonhydric soils created by geologic or human
    modifications to soils (additions). Relict hydric
    soils were hydric but are now nonhydric soils
    created by geologic modifications to hydrology.
  • A soil is hydric because it (1) Has a hydric
    soil indicator or, (2) Meets hydric soil criteria
    3 or 4 or, (3) By data meets the HSTS.

36
Caveats
  • Modified soil and hydrology may be due to illegal
    or legal activities.
  • By federal or state agency policy, modified areas
    may be subject to litigation (Section 404 CWA,
    Swampbuster) or still eligible for programs
    (USDAs EWP).

37
Literature Cited
  • Hurt, G.W., and L.M. Vasilas (Eds.). 2006. Field
    indicators of hydric soils in the United States
    (Version 6.0), USDA, NRCS, Fort Worth, TX.
    http//soils.usda.gov/soil_use/hydric/field_ind.pd
    f
  • Vepraskas, M. J. 1994. Redoximorphic Features for
    Identifying Aquic Conditions. Tech. Bulletin 301.
    North Carolina Ag. Research Service, North
    Carolina State Univ., Raleigh, North Carolina.
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