20081319 Ver 3_Year 2 Monitoring Report Ph II_20120224

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TABLE OF CONTENTS
1.0 EXECUTIVE SUMMARY
2.0. PROJECT OVERVIEW ..................................................................................... ............................... 2
A. Introduction ................................................................................................ ............................... 2
B. Mitigation Goals and Objectives ............................................................... ............................... 2
C. Project Implementation ............................................................................. ............................... 3
3.0. MONITORING REQUIREMENTS ..................................................................... ............................... 4
4.0 MONITORING RESULTS ................................................................................. ............................... 6
A. Vegetative Monitoring ............................................................................... ............................... 6
B. Hydrologic Monitoring ............................................................................... ............................... 8
1. Overview ............................................................................................. ............................... 8
2. Bay Forest Restoration Areas ............................................................. ............................... 8
3. Wet Hardwood Forest Restoration Areas ........................................... ............................... 9
4. Year 1 vs. Year 2 .............................................................................. ............................... 14
5. Enhancement and Reference Areas ................................................. ............................... 14
6. Summary of Annual Precipitation .................................................... ............................... 14
5.0 CONCLUSION ................................................................................................ ............................... 18
LIST OF FIGURES, TABLES, AND APPENDICES
Figure1 .......................................................................................................... ............................... Phase Map
Figure 2 .............................................................................. ............................... Phase 2 (Well and Plot) Map
Figure 3 ............................................... ............................... Reference and Enhancement Well Map (On -site)
Figure 4 ................................................................................ ............................... Estimated Hydrologic Zones
Figure 5 ...................................... ............................... ......................Reference Well Map (Cameron Property)
Table 1 ..................................................................... ............................... Phase 2 Planting List (March 2009)
Table 2 ........................................ ............................... List of Acceptable Volunteer Species by Habitat Type
Table 3 ................................. ............................... Summary of Year 2 Vegetative Monitoring Data (Phase 2)
Table 4A ...................... Summary of Year 2 Hydrologic Monitoring Data (Bay Forest Restoration — Phase 2)
Table 4B ...................... Summary of Year 2 Hydrologic Monitoring Data (Bay Forest Restoration — Phase 2)
Table 5A..... Summary of Year 2 Hydrologic Monitoring Data (Wet Hardwood Forest Restoration — Phase 2)
Table 56..... Summary of Year 2 Hydrologic Monitoring Data (Wet Hardwood Forest Restoration — Phase 2)
Table 6A ................... Summary of Year 2 Hydrologic Monitoring Data (Reference and Enhancement Wells)
Table 6B ................... Summary of Year 2 Hydrologic Monitoring Data (Reference and Enhancement Wells)
AppendixA .............. ...............................
AppendixB .............. ...............................
AppendixC .............. ...............................
AppendixD .............. ...............................
Rutman Creek Watershed Restoration Project
Phase 2 — Year 2 Annual Monitoring Report
February 2012
.......................... ............................... Site Photographs
I .............................. Vegetative Monitoring Data (2011)
.............................. Hydrographs (2011) — enclosed CD
Palmer Hydrologic Drought Index Maps — enclosed CD

1.0
EXECUTIVE SUMMARY
On behalf of PCS Phosphate Company, Inc. (PCS), Wetlands Resource Center LLC (WRC), has
completed Year 2 annual monitoring of Phase 2 of the Rutman Creek Watershed Restoration
Project. Phase 2 includes the restoration of 1,232 acres of non - riparian wetland restoration and
the preservation and enhancement of 448 acres of bay forest wetlands. Two wetland community
types, headwater bay forest and wet hardwood forest, were restored based on landscape position
and soil type. Construction of this phase was completed in March 2010. Work included the
backfilling of interior (lateral) ditches, disking of fields, the installation of clay plugs, and the planting
of over 643,950 bare -root seedlings (refer to the As -Built Report submitted June 2010).
Per the approved restoration plan, monitoring of the site includes the assessment of both
hydrologic and vegetative conditions over the course of a five year monitoring period. Following
the completion of the earthwork, a total of one hundred twenty -three (123) 0.10 acre plots were
established throughout the planted area. Approximately 90% of the vegetation plots were
associated with the bay forest community and 10% were associated with the wet hardwood forest
community, A total of sixty -two (62) shallow groundwater monitoring wells were installed within
approximately 50% of the plots. Additional wells have been installed in enhancement wetland
areas and within reference wetlands (both on -site and off - site). Please refer to the Year 1 Annual
Monitoring Report (AMR) (submitted February 2010) documenting site conditions during the 2010
growing season.
The Year 2 annual monitoring was conducted in October 2011. Based upon the data collected, the
Phase 2 project area exhibits high rate of survivorship ( >90 %) of planted species as evidenced by
an average observed density of 537 stems per acre. The hydrologic response to restoration efforts
is also evident via data collected from the shallow groundwater monitoring wells. Subsequent to
the backfilling of lateral ditches and installation of clay plugs within canals (completed in March
2010), observed hydroperiods continue to increase in duration and amplitude. In Year 2, fifty -eight
(58) of the sixty -two (62) wells exhibited hydroperiods greater than 5% of the growing season. The
mean hydroperiod of all wells was 49.1 days (equivalent to 18.7% of the growing season). The
following AMR provides more detailed information regarding the findings of Year 2 monitoring.
Rutman Creek Watershed Restoration Project j
Phase 2 — Year 2 Annual Monitoring Report
February 2012

2.0 PROJECT OVERVIEW
A. Introduction
Wetlands Resource Center (WRC) began implementation of Phase 2 of the restoration project
(encompassing 1,680 acres of the 4,213 -acre project area) in December 2009. Phase 2 is located
in the central section of the larger Rutman Creek Watershed Restoration Project and is bounded by
New Lake Road to the north, Airport Road to east, and Bama Canal to the southwest (Figure 1).
Restoration activities included earthwork (backfilling of interior ditches, disking of fields, installation
of clay plugs, etc.), planting of characteristic non - riparian bay and wet hardwood forest trees, and
the installation of monitoring devices. Placement of fill material within existing ditches was
authorized under Nationwide Permit 27 issued by the U.S. Army Corps of Engineers (USACE) with
attached conditions (issued February 20, 2009), and the NC Division of Water Quality (DWQ) 401
Water Quality Certification with attached conditions (issued March 16, 2009). Refer to the Phase 1
As -Built Report for copies of these authorizations. The entire restoration project is designed to
provide suitable, high - quality wetland and stream restoration to mitigate for authorized impacts
associated with the PCS mine continuation project in Aurora (Beaufort County), NC (USACE
Permit No. SAW- 2001 - 10096; DWQ 401 Certification No. 3771).
B. Mitigation Goals and Objectives
The objective of the Rutman Creek project is to provide for the functional restoration and ecological
up -lift of wetland and stream habitat via the re- establishment of characteristic hydrologic conditions
and vegetative assemblages. Anticipated functions and values resulting from the restoration
project include increased nutrient retention /transformation, sediment retention, floodwater
storage /flood abatement, wetland /wildlife habitat, and groundwater recharge. Given the scale of
the restoration effort, the project will provide considerable habitat benefits on a watershed and
regional level. The project offers the unique opportunity to provide habitat connectivity between
vast acreage of wildlife refuge areas (to the northeast) and the Pungo River Estuary (to the
southwest).
Phase 2 of the project is intended to restore the hydrology and vegetation to 1,232 acres of
Rutman Creek Watershed Restoration Project 2
Phase 2 — Year 2 Annual Monitoring Report
February 2012

previously disturbed wetland habitat. An additional 384 acres of preservation and 64 acres of
enhancement are also included within the boundaries of Phase 2. Restoration and preservation
efforts will contribute to enhanced water quality and food -web support of downstream waters. The
vegetative restoration component is intended to reestablish a characteristic assemblage of bay
forest and wet hardwood forest coinciding with existing topography, soil types, and restored
hydroperiods. The restored wetland communities will provide valuable refuge and feeding habitat
previously degraded or removed entirely by historic conversion to agriculture and subsequent long-
term farming practices.
C. Project Implementation
Restoration activities within the existing farm fields were initiated in December 2009 with the
backfilling of the existing network of lateral ditches. Clay plugs were then installed in five (5)
specific locations within outlet canals per the approved restoration plan (Figure 2). Clay material
for these plugs was excavated from existing spoil piles along Mooney Canal. The plug material
was placed within the canals and subsequently compacted utilizing the excavator equipment. All
the clay plugs were installed during February and March 2010. Clay plugs #7 through #10 and #13
are 50 ft in length. To provide additional reinforcement during high -flow events, filter- fabric and
large rip -rap was placed over the entire length of each plug (including the upstream and
downstream slopes). All water - control structures on each of the canals within Phase 2 have been
removed from operation. Note that access across the water - control structures has been
maintained to provide all- terrain vehicle ingress /egress for monitoring and long -term management.
Planting of the 1,232 -acre restoration area was conducted by Superior Tree Planting Service
during the week of March 1 through March 12, 2010. All planting activities were supervised by
environmental scientists from LMG. Plant material was provided by Arborgen Nursery (Blenheim,
SC). Per the restoration plan, two non - riparian vegetative communities (bay forest and wet
hardwood forest) were established throughout the 1,232 -acre restoration area. The bay forest
community (approximately 1,111 acres) was planted with characteristic species such as bald
cypress (Taxodium distichum), sweet bay (Magnolia virginiana) and pond pine (Pinus serotina).
The wet hardwood forest community (approximately 121 acres) was planted with species such as
swamp chestnut oak (Quercus michauxii), laurel oak (Quercus laurifolia), and black gum (Nyssa
Rutman Creek Watershed Restoration Project 3
Phase 2 — Year 2 Annual Monitoring Report
February 2012

sylvatica). A total of 643,950 seedlings were planted (corresponding to an average density of 523
stems /acre). Table 1 provides additional information regarding community composition and total
stem counts for Phase 2.
Table 1. Rutman Creek Watershed Restoration Project — Phase 2 Planting List (March 2010)
Bay Forest
1,111
Non - Riparian Restoration
Common Name
Scientific Name
% Composition
# Planted
Red Bay
Persea borbonia
2.0
11,525
Sweetbay
Magnolia virginiana
15.2
89,000
Pond Pine
Pinus serotina
23.6
138,450
Atlantic White Cedar
Chamaecyparis thyoides
12.8
75,000
Bald Cypress
Taxodium distichum
303
177,900
Black Gum
Nyssa sylvatica
16.2
94,800
TOTAL
586,675
Wet Hardwood Forest
121
Non-Riparian Restoration
Common Name
Scientific Name
% Composition
# Planted
Swamp Chestnut Oak
Quercus michauxii
18.0
10,300
Laurel Oak
Quercus launfolia
17.8
10,200
Cherrybark Oak
Quercus falcata
180
10,300
Black Gum
Nyssa sylvatica
180
10,300
Ironwood
Carpinus carohmum
57
3,275
Tulip Poplar
Liriodendron tulipifera
225
12,900
TOTAL
57,275
GRAND TOTAL
643,950
3.0 MONITORING REQUIREMENTS
Annual monitoring is being conducted near the end of each growing season for a period of five
years. This monitoring includes both a vegetative and hydrologic component per the approved
restoration plan. The vegetative component for Phase 2 includes an assessment of the conditions
within each of the 123 permanent monitoring plots that have been established throughout the
project area (Figure 2).
Rutman Creek Watershed Restoration Project 4
Phase 2 — Year 2 Annual Monitoring Report
February 2012

Hydrologic monitoring is being conducted via sixty -two (62) automated, shallow groundwater
monitoring wells recording on daily intervals (refer to Figure 2 for location of the monitoring wells).
Data from the wells are downloaded on approximate three -month intervals and imported into
graphing software analysis. The following are the specific success criteria for both the vegetation
and hydrologic monitoring of the restoration areas. Note that the hydrologic success criterion for
Phase 2 (wet hardwood forest and bay forest community types) is identified in 2a and 2b below.
(1) Demonstrated density of planted species to meet or exceed 260 trees per acre at the end
of S years (post planting). 1
(2) The hydrologic criterion is premised on the specific community type to be restored.
(a) For the nonriverine wet hardwood forest community (mineral soils), the
hydrologic criterion will be the establishment of a static water table at, or within,
12 " of the soil surface for 6% of the growing season (equivalent to 16 days
based upon a growing season from March 11th through November 27th) during
periods of normal rainfall.
(b) For the nonriverine bay forest and swamp forest communities (organic soils),
the hydrologic criterion will be the establishment of a static water table at, or
within, 12 " of the soil surface for 10% of the growing season (equivalent to 26
days based upon a growing season from March 11th through November 27th)
during periods of normal rainfall.
(c) For the small stream swamp (headwater riparian) community (zero -order
geomorphic position), the hydrologic criterion will be the establishment of a
static water table at, or within, 12 " of the soil surface for 12.5% of the growing
season (equivalent to 33 days based upon a growing season from March I1 th
through November 27th) during periods of normal rainfall.
Monitoring reports include results of vegetative monitoring and photographic documentation of site
conditions. Reports also identify any contingency measures that may need to be employed to
remedy any site deficiencies. For instance, deer browse tubes and fencing may need to be used if
Volunteer species may be counted toward meeting the success criteria based upon the list of species identified in
Table 2; however, these will be tracked separately.
- 2 As determined from long -term climatic data of published WETS Table of Belhaven, NC station.
Rutman Creek Watershed Restoration Project $
Phase 2 — Year 2 Annual Monitoring Report
February 2012

evidence of significant herbivory or deer browse is observed. In addition, supplemental planting
may be necessary in areas of reduced survivorship.
Table 2. List of Acceptable Volunteer Species by Habitat Type
Swamp Forest
1,251 ac
Bay Forest
1,705 ac
Common Name
Scientific Name
Common Name
Scientific Name
Sweetbay
Magnolia virginiana
Fetterbush
Lyonia lucida
Red Bay
Persea palustris
American Titi
Cyrilla racemiflora
American Titi
Cyrilla racemiflora
Gallberry
Ilex conacea
Wax Myrtle
Myrica cerifera
Inkberry
Ilex glabra
Fetterbush
Lyonia lucida
Dahoon Holly
Ilex cassine
Sweet Pepperbush
Clethra alnifolia
Wax Myrtle
Myrica cerifera
American Holly
Ilex opaca
High -bush Blueberry
Vaccinium corymbosum
High -bush Blueberry
Vaccinium corymbosum
Wet Hardwood Forest
344 ac
Small Stream Swamp
42 ac
Common Name
Scientific Name
Common Name
Scientific Name
Red Bay
Persea palustris
Fetterbush
Lyonia lucida
Wax Myrtle
Myrica cerifera
American Titi
Cyrilla racemiflora
Sweet Pepperbush
Clethra alnifolia
Wax Myrtle
Mynca cenfera
American Holly
Ilex opaca
Tulip Poplar
Liriodendron tulipifera
High -bush Blueberry
Vaccinium corymbosum
High -bush Blueberry
Vaccinium corymbosum
4.0 MONITORING RESULTS (YEAR 2)
A. Vegetation Monitoring
A total of 6,618 plant stems (6,612 stems of planted species and 6 stems of acceptable volunteer
species) were enumerated throughout the one hundred twenty -three (123) plots. Note that three
plots ( #107, #108, and #110) occur in former road beds and are 0.05 -acre in size. Accounting for
the total monitored area, the observed mean stem density across the site is 544 stems per acre
(Table 3). Bald cypress was the most abundant woody species, with a total of 2,006 individuals
identified. Other planted species such as pond pine, black gum and Atlantic white cedar
(Chamaecyparis thyoides) were also prevalent within the monitored plots. With the inclusion of two
accepted volunteer species (namely American Holly and wax myrtle), the observed mean stem
density for Year 2 is 545 stems per acre. Additional woody volunteers, including eastern baccharis
Rutman Creek Watershed Restoration Project 6
Phase 2 — Year 2 Annual Monitoring Report
February 2012

(Baccharis halimifolia), winged sumac (Rhus copallina), and sweet gum (Liquidambar styraciflua)
were identified in Phase 2; however, these species were not counted towards the success of the
site. Natural recruitment of red bay volunteers was noted in areas in close proximity to the forested
preservation areas of the tract. Refer to Appendix A for photographs of current site conditions. A
comprehensive plot data table is provided in Appendix B.
Table 3. Summary of Year 1 Vegetative Monitoring Data (Phase 2)
Species
Common Name
Planted (P) or
Volunteer (V)
Total
Stems
# plots
Average # Stems
Taxodium distichum
bald cypress
P
2,006
112
17.9
Pinus serotina
pond pine
P
1,577
100
15.7
Nyssa sylvatica
black gum
P
940
95
9.8
Chamaecyparis thyoides
Atlantic white cedar
P
857
77
11.1
Magnolia virginiana
sweetbay
P
562
73
7.6
Quercus pagoda
cherr bark oak
P
154
9
17.1
Persea borbonia
red bay
P
145
25
5.8
Quercus michauxii
swamp chestnut oak
P
116
9
12.8
Liriodendron tulipifera
tulip poplar
P
107
11
9.7
Quercus laurifolia
laurel oak
P
95
8
11.8
Nyssa biflora
swamp tupelo
P
34
2
17
Carpinus caroliniana
I ironwood
P
19
2
9.5
Ilex opaca
American holly
V
4
3
1.3
Morella cerifera
wax myrtle
V
2
2
1
Total Planted Stems (123 Plots)
6,612
54.4
Total Planted and Acceptable Volunteer Stems (123 Plots)
6,618
54.5
The number of stems of planted species observed during the Year 2 monitoring event suggests
that the site is progressing well toward the target communities. All of the 123 plots3 exceeded the
minimum success criteria of 26 stems and contained a variety of shrub and tree species.
During Year 2 monitoring, it was noted that herbaceous vegetation was very dense in select plots.
While most planted tree seedlings will likely remain unaffected by dense herbaceous growth, some
of the smaller planted material (particularly sweet bay seedlings) may be susceptible to mortality.
Plots consisting of panicgrass (Panicum spp.) and smartweed (Polygonum spp.) exhibited dense
herbaceous growth covering the smaller planted seedlings. While mortality of the planted stems
3 Note that three plots are 0.05 -acre in size.
Rutman Creek Watershed Restoration Project
Phase 2 — Year 2 Annual Monitoring Report
February 2012
7

remained relatively low, these areas will be continued to be monitored to determine if any
contingency measure is warranted.
B. Hydrologic Monitoring
1. Overview
Per the approved mitigation plan, a total of sixty -two (62) automated shallow groundwater
monitoring wells were installed throughout the Phase 2 project area the week of February 15,
2010. The number of wells installed was proportional to the acreage of the two targeted wetland
community types. Specifically, fifty -six (56) wells were installed in the bay forest restoration areas
and six (6) wells were installed within the wet hardwood forest areas (refer to Figure 2). In
addition, four (4) automated wells were installed within existing bay forest areas targeted for
wetland enhancement and five (5) wells had been previously installed within on -site bay forest
reference wetlands (refer to Figure 3).
2.. Bav Forest Restoration Areas
Of the 56 wells in the bay forest community type, fifty -five (55) wells exhibited hydroperiotls greater
than 5% (corresponding to 13 consecutive days), thus meeting the criteria for jurisdictional
wetlands. Forty -five (45) wells exhibited hydroperiotls greater than 10% of the growing season (i.e.
the hydrologic success criterion for bay forest wetland restoration, 26 days). Hydroperiods for the
bay forest wells ranged between 12 consecutive days (4.6% of the growing season) (Plot #89) and
93 days (35.5% of the growing season) (Plot #3 -7, 19, 21, 51, 73, 79, 99, 101, and 111). The
mean hydroperiod was 51.7 days (19.7% of the growing season). Refer to Table 4A for a
summary of the hydrologic data for the bay forest restoration wells. Hydrographs are provided in
Appendix C (on the enclosed CD). The estimated hydrologic zones of Phase 2 (Year 2) are
provided in Figure 4.
Note that based upon recent federal guidance regarding the length of the growing season in the
Atlantic and Gulf Coastal Plain Region (as detailed in the Regional Supplement to the Corps of
Engineers Wetland Delineation Manual: Atlantic and Gulf Coastal Plain Region), biological
indicators and soil temperature data often indicate that the growing season of a particular county
may be longer than that identified in WETS tables. As a result, the state Interagency Review Team
Rutman Creek Watershed Restoration Project g
Phase 2 — Year 2 Annual Monitoring Report
February 2012

(IRT) has recently moved toward the use of a growing season beginning February 1 and ending
November 30 of each year (unless site - specific data indicate otherwise). Available soil
temperature data at Rutman Creek support the use of an extended growing season (refer to
hydrographs provided in Appendix C). In light of recent agency guidance, a supplemental table
(evaluating hydroperiotls from February 1 through November 30) is provided for informational
purposes (refer to Table 46).
3. Wet Hardwood Forest Restoration Areas
Within the areas targeted for wet hardwood forest restoration, three of the six wells exhibited
hydroperiotls greater than 14% of the growing season. The remaining three wells exhibited
hydroperiotls between 4% and 5% of the growing season. The minimum hydrologic criterion for
the wet hardwood forest community type is 6% of the growing season (corresponding to 16
consecutive days). Hydroperiods for the wet hardwood forest wells ranged between 10
consecutive days (3.8% of the growing season) (Plot #113) and 39 days (14.9% of the growing
season) (Plot #115). The mean hydroperiod was 24.8 days (9.5% of the growing season). Refer
to Table 5A for a summary of the hydrologic data for the wet hardwood forest restoration wells. In
light of recent agency guidance, a supplemental table (evaluating hydroperiods from February 1
through November 30) is provided for informational purposes (refer to Table 56). Hydrographs are
provided in Appendix C. The estimated hydrologic zones of Phase 2 (Year 2) are provided in
Figure 4.
Rutman Creek Watershed Restoration Project 9
Phase 2 — Year 2 Annual Monitoring Report
February 2012

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4. Year 1 vs. Year 2
Cumulative days of groundwater levels within 12 inches of the soil surface were significantly higher
during Year 2 than Year 1 (Year 1 R= 73.9; Year 2 R= 194.6; p <0.0001). Such data indicate that
the rate of groundwater discharge has appreciably declined since Year 1, resulting in a gradual
elevation of the static water table. A similar trend was observed in Phase 1 as hydroperiods
increased in duration over each successive year of monitoring (through Year 3).
5. Enhancement and Reference Areas
As indicated above, wells were installed in both reference wetlands and those wetlands considered
for enhancement. Of the twelve reference and enhancement wells, four (Bay Reference Wells #1
through #3 and Enhancement Well #3) exhibited abnormally low groundwater levels throughout the
monitoring period (Figure 3). It is unclear as to the reason these areas lack wetland hydrology — as
they are located within histosol soils and are located greater than 300 ft from any drainage feature.
At the time of installation, it was unclear whether the lack of an observed water table was an
artifact of drought conditions or a regional drainage effect. Based upon the data collected, it
appears as though groundwater conditions are adversely affected by factors other than drought.
The three bay forest reference wells will be relocated within the same block of woods to an area
with more appropriate reference hydrology. The other reference and enhancement wells are
located in areas that appear to be more representative of relatively undisturbed wetlands and
display more characteristic hydroperiods (Figure 4). Refer to Table 6A for a summary of the
hydrologic findings for these wells. In light of recent agency guidance, a supplemental table
(evaluating hydroperiods from February 1 through November 30) is provided for informational
purposes (refer to Table 6B). Hydrographs are provided in Appendix C.
6. Summary of Annual Precipitation
Precipitation over the monitoring year was variable. Based upon documented rainfall (via on -site
data loggers and off -site weather stations), precipitation totals were generally considered "normal'
from January 2011 to April 2011. These findings were supported by the Palmer Hydrologic
Drought Index maps which depict hydrological (long -term cumulative) drought and wet conditions
by regions. According to the Palmer Index, drought conditions began in May 2011 and persisted
Rutman Creek Watershed Restoration Project 14
Phase 2 — Year 2 Annual Monitoring Report
February 2012

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until late August. In June and July, the drought was characterized as 'severe' and 'extreme',
respectively. Groundwater levels were recharged as a result of an extreme precipitation event
associated with Hurricane Irene on August 27, 2011. The subsequent groundwater recharge is
reflected by the Palmer Index indicating 'mid- range' (i.e. normal) hydrologic conditions from September
through November. Moderate drought conditions returned in December 2011. Site - specific rainfall
data are included on the hydrographs in Appendix C. The Palmer Hydrologic Drought Index maps for
2011 are provided in Appendix D. Both appendices are provided digitally on the enclosed CD.
5.0 CONCLUSION
Vegetation and hydrologic monitoring of the Phase 2 project area indicate that the site is progressing
well during the second year following the implementation of the restoration activities. Vegetation data
document high rates of survivorship ( >90 %) among the planted species, and there were no significant
vegetation issues noted. The observed average stem density across the site is 544 stems per acre.
All of the plots exceeded the minimum success criteria of 26 stems and contained a variety of shrub
and tree species.
The site continues to exhibit increased duration and amplitude of hydroperiods — suggesting that the
measures employed to eliminate prior site drainage (e.g. backfilling of ditches and installation of
impervious clay plugs) are functioning as intended. Among the sixty -two (62) wells monitored
throughout the site, forty -eight (48) wells exceeded the stated hydrologic success criterion.
Overall the Phase 2 project area appears to be performing well. Monitoring results indicate that target
wetland functions (including floodwater storage, increased hydrologic residency times,
nutrient/sediment retention, and wildlife habitat) are already being performed across the site. As a
result, no contingency measures are planned. The site will be continued to be monitored over the next
three years (through Year 5) and the findings of such will be provided in subsequent annual monitoring
reports for agency review and concurrence.
Rutman Creek Watershed Restoration Project 17
Phase 2 — Year 2 Annual Monitoring Report
February 2012

FIGURES

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APPENDIX A.
SITE PHOTOGRAPHS (2011)

(1) View of laurel oak in Plot 113
(2) View of monitoring in Plot 113 October 2011
Rutman Creek
Watershed Restoration Project
Phase 2
AkAMG
iwLAND MANAGEMENT GROUP ,Nc
Environmental Consultants
Site Photographs
Annual Monitoring
(Year 2)

1 t i `�� ,� ,�j'� � y ' � � • ��y�r s
5 * t Y

(1) View of monitoring well with bear deterrent in Plot 83
(2) View of Atlantic white cedar in Plot 83
Rutman Creek Site Photographs
Watershed Restoration Project LMG
1 LAND MANAGEMENT GROUPnrc Annual Monitoring
Phase 2 — Fnvitonmental Consultants (Year 2)

APPENDIX B.
INDIVIDUAL PLOT DATA (YEAR 2)

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