%
               NONPOINT  SOIREE  SICCESS STOIY
 Riparian Restoration Efforts Reduce Temperature and Sedimentation,
 Improving Polvadera Creek
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                                Off"road vehicle usa9e' rangeland grazing and a loss of riparian
                                habitat contributed to increased temperature and sedimentation
 which degraded water quality in New Mexico's Polvadera Creek. As a result, Polvadera Creek was
 added to the Clean Water Act (CWA) section 303(d) list of impaired waters for temperature in 2000
 and sedimentation in 2006. Following a CWA section 319 project with the Santa Fe National Forest
 (SFNF), which included riparian restoration practices such as native vegetation plantings and riparian
 livestock exclusion devices, water quality in Polvadera Creek improved. Due to these improvements,
 the segment was removed from the 2014 list of impaired waters for sedimentation and temperature.
 Problem
 Polvadera Creek (segment NM-2116.A _ 011) is in
 northern New Mexico near the town of Abiquiu
 (Figure 1). The creek flows north from its headwa-
 ters in the Jemez Mountains to its confluence with
 Cahones Creek, which flows into Abiquiu Reservoir
 on the Rio Chama in the Rio Grande Basin. The
 watershed is primarily in the SFNF; the main land
 use is rangeland grazing.

 Water quality surveys as far back as 1996 and 1999
 revealed that 14 miles of Polvadera Creek (from its
 headwaters to the confluence with Cahones Creek)
 were impaired by excess sediment and high tem-
 peratures. These impairments prevented Polvadera
 Creek from meeting its designated use of high
 quality co/dwateraquatic life and resulted in the
 listing of the creek for stream bottom deposits in
 1998 and temperature impairment in 2000.  Stream
 bottom deposits were delisted as an impairment
 in 2004 based on the assessment protocol  at that
 time;  however, in 2006 the stream was re-assessed
 using the current protocols, and it was listed as
 being impaired by sedimentation once again. To
 meet standards for sedimentation, the creek has to
 comply with the narrative standard, which requires
 it to be free of fine sediment that would clog the
 natural substrate. To  meet standards for tempera-
 ture, the maximum stream temperature must be
 less than 23°C (73°F), and  it cannot exceed  20°C
 for longer than four hours on three consecutive
 days (4T3). In 2004 the New Mexico Environment
 Department developed a total maximum daily load
 (TMDL) to address the temperature impairment on
 Polvadera Creek.
                                               	NM-2116JL011
                                                 NHD FLow line
                                               ^H Watershed Area
                                              Figure 1. The Polvadera Creek watershed is in
                                              northern New Mexico.
                                              Project Highlights
                                              In 2009 the SFNF began a CWA section 319
                                              restoration project to remove the temperature and
                                              sedimentation impairments in Polvadera Creek.
                                              The project had six major components:
                                              1. Riparian vegetation treatment. Beginning in
                                                2007, SFNF staff removed encroaching juniper
                                                bushes and planted willows. The treatment is
                                                credited with minimizing the impact of the 2010
                                                South Fork Fire on the riparian corridor.

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Figure 2. SFNF staff installed this steel pipe fence
to prevent ATVs from accessing and damaging the
riparian corridor in a recreation area.

2. Closing the stream corridor to all-terrain vehi-
  cles (ATV). SFNF staff constructed the primary
  barrier of rocks and steel pipe fencing in 2009,
  and it successfully reduced erosion and sedimen-
  tation from ATV use (Figure 2). Maintenance is
  ongoing because vandalism has occurred.
3. Beaver re-introduction. The project area his-
  torically supported a robust beaver population,
  which had helped to create and maintain a  sig-
  nificant wetland complex. The wetlands trapped
  sediment and increased baseflow, offering a buf-
  fer against high summer stream temperatures.
  Beaver re-introduction was planned but not
  carried out because of opposition by area farm-
  ers and ranchers; however, beavers reappeared
  in the project area on their own. With continued
  improvement of riparian habitat, the beaver popu-
  lation is likely to increase.
4. Riparian fencing. The riparian fence was con-
  structed in 2001 and continues  to be  maintained.
  In 2009 an additional 0.5 miles of fence was
  added to the riparian fence to further protect the
  creek. Post-fire flooding has required significant
  maintenance work on the fence.

5. Grazing allotment management. A National
  Environmental Policy Act (NEPA) analysis was
  completed for the Polvadera Grazing Allotment in
  2009, which resulted in the authorization of graz-
  ing under an Adaptive Management approach.
  This approach included actions such as the
  deferral of grazing in Rio Grande Cutthroat  Trout
  areas until after July 15th and the  installation of
  upland alternative water sources for livestock
  called "trick tanks." Completed  in  2011 and 2012,
  these alternative water sources reduce grazing
  pressure in the riparian areas (Figure 3).
6. Community education. In 2009 the SFNF
  teamed up with Santa Fe Youthworks, a
Figure 3. This completed livestock "trick tank," an
alternative water source installed in an upland area,
reduces grazing pressure on the riparian corridor.

   nonprofit community organization that helps
   disconnected youth and families  in northern
   New Mexico become engaged in community
   service. Youthworks and SFNF staff conducted
   two workshops on constructing fencing and
   fish habitat structures, as well as a workshop on
   careers in the Forest Service.
Results
Monitoring in 2012 revealed water quality improve-
ments in Polvadera Creek. There were 30.5 percent
sand and fines, which was above the 20 percent
threshold for Mountain Site  Class. However, the log
Relative Bed Stability (LRBS) was -0.63, which is
lower in absolute value than the threshold of -1.1 for
Mountain Site Class. This indicated that although
there was greater sand and fines, sufficient sedi-
ment transport capacity existed to protect aquatic
life. In addition, the maximum thermograph tempera-
ture was 20°C, which met the standard. Therefore, in
2014 sedimentation and temperature were removed
as causes of impairment for Polvadera Creek. The
vegetation treatment was credited with prevent-
ing greater damage to the riparian corridor from
the 2010 South Fork  Fire. Deferring grazing helped
protect the native Rio Grande Cutthroat Trout fishery.
Partners and Funding
The improvement in water quality in Polvadera
Creek was the result of a collaboration between
multiple partners. The SFNF, the primary coopera-
tor, was responsible for implementing the project
using $41,000 of CWA section 319 funding. Santa
Fe Youthworks provided education  and outreach.
Lastly, Polvadera Grazing Allotment permittees sup-
ported the restoration by modifying their grazing
activities due to the aforementioned NEPA analysis.
Ui
o
     U.S. Environmental Protection Agency
     Office of Water
     Washington, DC


     EPA841-F-15-001QQ
     October 2015
For additional information contact:
Daniel Guevara
New Mexico Environment Department, Surface
Water Quality Bureau
505-476-3086 • daniel.guevara@state.nm.us

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