TXU Trail-SY120531 I AIM
integrated environmental solutions
31 May 2012
Mr.Brian LaFoy,P.E.
Nathan D.Maier Consulting Engineers,Inc.
8080 Park Lane,Suite 600
Dallas,Texas 75231
Re: Waters of the United States Delineation
TXU Easement-Trail Expansion,Coppell,Dallas County,Texas
Dear Mr.LaFoy,
Integrated Environmental Solutions,LLC.(IES)performed a survey to identify any water features that meet a
definition of a water of the United States to facilitate design for the TXU Easement-Trail Expansion in the City
of Coppell, Dallas County,Texas (Attachment A,Figure 1). The proposed project will involve the expansion
of the hike and bike trail system within the TXU easement. As such,the delineation project area included the
TXU transmission line corridor (easement) from Sandy Lake Road south to Belt Line Road, and included a
small segment of corridor extending west between Mallard Drive and Hidden Hollow Court. This report will
ultimately assess the project's anticipated impacts to potential jurisdictional waters and determine the
appropriate Section 404 permits for the proposed project to ensure compliance with Section 404 of the Clean
Water Act(CWA).
INTRODUCTION
Agencies that regulate impacts to the nation's water resources within Texas include the U.S.Army Corps of
Engineers (USACE), the U.S. Environmental Protection Agency (USEPA), the U.S. Fish and Wildlife Service
(USFWS), and the Texas Commission on Environmental Quality (TCEQ). Jurisdictional waters of the United
States are protected under guidelines outlined in Sections 401 and 404 of the CWA,in Executive Order 11990
(Protection of Wetlands), and by the review process of the TCEQ. The USACE has the primary regulatory
authority for enforcing Section 404 requirements for waters of the United States,including wetlands.
The definition of waters of the United States,in 33 Code of Federal Regulations (CFR) 328.3,includes waters
such as intrastate lakes, rivers, streams (including intermittent streams), mudflats, wetlands, sloughs, wet
meadows,or natural ponds and all impoundments of waters otherwise defined as waters of the United States.
Also included are wetlands adjacent to waters (other than waters that are themselves wetlands). The term
adjacent is defined as bordering,contiguous,or neighboring. Jurisdictional wetlands are a category of waters
of the United States and have been defined by the USACE as areas that are inundated or saturated by surface
or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do
support,a prevalence of vegetation typically adapted for life in saturated soil conditions.
Integrated Environmental Solutions,LLC. 2150 South Central Expressway,Suite 110
McKinney,Texas 75070 www.intenvsol.com
Telephone:972.562.7672
Facsimile:972.562.7673
Mr.Brian LaFoy,P.E.
TXU Easement-Trail Expansion-Waters of the United States Delineation
31 May 2012 Page 2
Waters of the United States are defined in 33 CFR 328.3 (a)as:
1. All waters which are currently used, or were used in the past, or may be susceptible to use in
interstate or foreign commerce,including all waters which are subject to the ebb and flow of the tide;
2. All interstate waters including interstate wetlands;
3. All other waters such as intrastate lakes, rivers, streams (including intermittent streams), mudflats,
sandflats, wetlands, sloughs, prairie potholes, wet meadows, playa lakes, or natural ponds, the use,
degradation or destruction of which could affect interstate or foreign commerce including any such
waters:
i. Which are or could be used by interstate or foreign travelers for recreational or other purposes;
or
ii. From which fish or shellfish are or could be taken and sold in interstate or foreign commerce;or
iii. Which are used or could be used for industrial purpose by industries in interstate commerce;
4. All impoundments of waters otherwise defined as waters of the United States under the definition;
5. Tributaries of waters identified in paragraphs(a)(1)-(4)of this section;
6. The territorial seas;
7. Wetlands adjacent to waters (other than waters that are themselves wetlands) identified in
paragraphs 1-6 above.
8. Waste treatment systems, including treatment ponds or lagoons designed to meet the requirements
of CWA(other than cooling ponds as defined in 40 CFR 123.11(m)which also meet the criteria of this
definition)are not waters of the United States.
On 05 June 2007, the USACE and the USEPA issued joint guidance on delineation of waters on the United
States based on the U.S. Supreme Court decisions in Rapanos and Cara bell. Under this guidance, potential
waters of the United States have been classified as traditional navigable waters (TNW),relatively permanent
waters (RPW) (i.e., having flow most of the year or at least seasonally), or non-RPWs. Per the guidance,
TNWs, wetlands adjacent to TNWs, RPWs, and wetlands that directly abut RPWs are waters of the United
States. Wetlands that are bordering, contiguous, or neighboring another water of the United States are
considered"adjacent." Additionally,wetlands that are within the 100-year floodplain of another water of the
United States are also considered adjacent. Non-RPWs, wetlands contiguous or adjacent to non-RPWs, and
wetlands adjacent to but that do not directly abut a RPW must undergo a"significant nexus"test on a case-by-
case basis to determine the jurisdictional nature of these water features. Under the"significant nexus"test a
water feature must have substantial connection to a TNW by direct flow,or by indirect biological,hydrologic,
or chemical connection. Under the "significant nexus" test the USACE District Engineer must submit the
jurisdictional determination(JD)to the regional USEPA office,which makes the decision whether to move the
JD to Headquarters USACE to make the final determination.
The new guidance does not void the January 2001 decision of the U.S. Supreme Court in Solid Waste Agency
of Northern Cook County (SWANCC) v. USACE which disallowed regulation of isolated wetlands under the
CWA through the "Migratory Bird Rule." Previously,the USACE assumed jurisdiction over isolated waters of
the United States based on its 1986 preamble stating that migratory birds used these habitats. The
"Migratory Bird Rule" provided the nexus to interstate commerce and thus protection under the CWA.
However, the new guidance does require that the "significant nexus" test be performed in addition to an
analysis of other potential interstate commerce uses for isolated waters.
METHODOLOGY
Prior to conducting fieldwork, the U.S. Geological Survey (USGS) topographic map, the Soil Survey of Dallas
County,Texas and the Natural Resource Conservation Service (NRCS) digital soil database for Dallas County,
the Federal Emergency Management Agency (FEMA) Flood Insurance Rate Map (FIRM), and historic aerial
photographs of the proposed project area were studied to identify possible waters of the United States and
Mr.Brian LaFoy,P.E.
TXU Easement-Trail Expansion-Waters of the United States Delineation
31 May 2012 Page 3
areas prone to wetland development. Mr. Rudi Reinecke and Mr. Shae Kipp of IES delineated all potential
waters of the United States in the field in accordance with the USACE procedures on 27 April 2012.
Wetland determinations were performed on location using the methodology outlined in the 1987 Corps of
Engineers Wetland Delineation Manual and the Regional Supplement to the Corps of Engineer Wetland
Delineation Manual: Great Plains Region (Version 2.0,March 2010). The presence of a wetland is determined
by the positive indication of three criteria(i.e.,hydrophytic vegetation,hydrology,and hydric soils). Potential
jurisdictional boundaries for other water resources (i.e., non-wetland) were delineated in the field at the
ordinary high water mark (OHWM). The 33 CFR 328.3(e) defines OHWM as the line on the shore/bank
established by flowing and/or standing water, marked by characteristics such as a clear, natural line
impressed on the bank,erosion shelving,changes in the character of soil,destruction of terrestrial vegetation,
presence of litter and debris,or other appropriate means that consider the characteristics of the surrounding
areas.
Water feature boundaries were recorded on a Trimble GeoExplorer XT global positioning system (GPS) unit
capable of sub-meter accuracy. Photographs were also taken at representative points within the project area
(Attachment B). Wetland Determination Data Forms were completed where wetland features and variation
in these features were encountered and to determine wetland feature boundaries(Attachment C).
RESULTS
Literature Review
The USGS topographic map (Carrollton 7.5' Quadrangle, 1982) illustrates the project area as relatively flat,
between Denton Creek and Grapevine Creek near the Elm Fork Trinity River (Attachment A, Figure 2). It
appears that the project area is potentially within the floodplain of all three water features. Several overhead
utility lines,both above and below-ground,are shown within the project area and the surrounding vicinity is
shown as undeveloped.
The Soil Survey of Dallas County, Texas mapped six soil series within the project area-Altoga silty clay,5 to 12
percent slopes, eroded; Ferris-Heiden complex, 5 to 12 percent slopes; Frio silty clay, occasionally flooded;
Heiden clay, 2 to 5 percent slopes,eroded; Seagoville clay,occasionally flooded; and Trinity clay,occasionally
flooded. Trinity clay,occasionally flooded is listed on the National Hydric Soils list prepared by the National
Technical Committee for Hydric Soils within depressional areas(revision April 2012) (Attachment A,Figure
3).
The FEMA FIRM (Map Panel 48113C0155 J, effective date 23 August 2001) illustrates the project area from
Sandy Lake Road to MacArthur Boulevard within Zone AE (areas inundated within the 100-year flood with
base flood elevations determined to be at 443 above mean sea level [amsl]),with outlying areas within Zone X
(areas of 500-year flood; areas of 100-year flood with average depths of less than 1 foot or with drainage
areas less than 1 square mile; and areas protected by levees from the 100-year flood). The remainder of the
project area from MacArthur Boulevard to Belt Line Road is within Zone X (areas determined to be outside
500 year floodplain) (Attachment A,Figure 4).
Historic aerials of the project area and surrounding vicinity from 1942 to 2005 have been included in
Attachment D. A review of historic aerial photographs from 1942 until 1972 shows the project area and
surrounding vicinity as undeveloped. Multiple drainage patterns and areas of inundation can be seen
throughout, as indicated by the varying color signatures. In some areas it is hard to determine which way
these drainages flow, as hydrology is influenced by Denton Creek, the Elm Fork Trinity River, and in some
cases,Grapevine Creek;although ultimately hydrology within this area reaches the Elm Fork Trinity River. In
1984,development of the surrounding vicinity began. Drainage patterns could still be seen within the project
area and immediate vicinity. Beginning in 1995, inundation of the project area, indicative of present day
conditions,was visible. By 2004, conditions, including the surrounding development, are similar to present
day.
Site Survey
As the project area was located within an overhead transmission line and a belowground pipeline easement,
maintenance is required to prevent the growth of trees, which could interfere with the overhead lines. As
Mr Brian LaFoy,P.E.
TXU Easement-Trail Expansion-Waters of the United States Delineation
31 May 2012 Page 4
such, the plant communities are dominated by herbaceous species, with a few shrubs and saplings present.
The two predominant plant communities were determined by hydrologic regime, as such, there was an
upland herbaceous community and a wetland herbaceous community. Dominant vegetation associated with
the upland herbaceous community was Japanese brome (Bromus japonicum), Bermudagrass (Cynodon
dactylon), beggars lice (Torilis arvensis), and common ragweed (Ambrosia artemisiifolia). The wetland
herbaceous community was dominated by various sedges (Carex spp.), water horehound (Lycopus
americanus), water paspalum (Paspalum fluitans), water primrose (Ludwigia repens), spike rush (Eleocharis
palustris),frog fruit(Phyla nodiflora),and sand dropseed (Sporobolus cryptandrus). Woody species observed,
included,black willow(Salix nigra),green ash (Fraxinus pennsylvanica), cottonwood (Populus deltoides),and
willow baccharis(Baccharis salicina).
The topography of the project area was complex, as it was generally flat, but sloped to the center of the
project area; ultimately to the east. The project area sloped away from the major drainages (i.e., Denton
Creek and Grapevine Creek) and their tributaries. Ultimately,when water elevations reached the capacity of
the depressional area,water flowed into adjacent impoundments on the golf course to the east of the project
area. It appeared that as the developments have occurred in the vicinity, fill was placed to elevate the
surrounding developed land from the 100-year floodplain, further exacerbating the depressional nature of
the project area. Denton Creek flows to the east to the Elm Fork Trinity River, north of the project area and
Grapevine Creek flows east to the Elm Fork Trinity River, south of the project area. The Elm Fork Trinity
River is located a short distance to the east of the project area. Aquatic features identified within the project
area are connected to the Elm Fork Trinity River through various drainages and impoundments that drain to
the river and through the 100-year floodplain. The Elm Fork Trinity River,within this reach,is considered a
TNW-in fact. Eleven potentially jurisdictional waters, six tributaries and five wetlands, were delineated
within the project area are summarized in Table 1 and detailed below(Attachment A,Figure 5).
Table 1. Aquatic Features Delineated within Project Area
Water of the Hydraulic Length Area
Water Identification Water Feature Type United States Characteristics (Linear Feet) (Acre)
Tributary 3 Drainage Channel No Ephemeral 52 0.014
Tributary 5 Drainage Channel No Ephemeral 185 0.021
Tributary 6 Drainage Channel No Ephemeral 254 0.100
Subtotal of Non-Jurisdictional Features 491 0.135
Tributary 1 Tributary Yes Ephemeral 113 0.006
Tributary 2 Tributary Yes Ephemeral 87 0.008
Tributary 4 Tributary Yes Intermittent 796 0.261
Wetland 1 Herbaceous Wetland Yes Oxidized 1.535
Rhizospheres
Wetland 2 Herbaceous Wetland Yes Oxidized 0.085
Rhizospheres
Wetland 3 Herbaceous Wetland Yes Oxidized 4.153
Rhizospheres
Wetland 4 Herbaceous Wetland Yes Inundated --- 16.779
Wetland 5 Herbaceous Wetland Yes Water Marks --- 5.147
Subtotal of Jurisdictional Features 996 27.974
TOTAL AQUATIC FEATURES 1,487 28.109
Wetland 1, Wetland 2, and Wetland 3 were located at the north end of the project area near Sandy Lake
Road. As with the rest of the project area,this area is relatively flat and collects stormwater from the adjacent
residential neighborhoods that drain into this area. Vegetation was dominated by frogfruit,water paspalum,
sand dropseed, and sedges (Carex tribuloides), meeting the criteria for hydrophytic vegetation. Hydric soils
were indicated by redox dark surface,with soil matrix colors of 90 percent 10 YR 3/2 with 10 percent 10 YR
3/6 redox concentrations. Hydrology was indicated around the fringe of the wetlands by oxidized
rhizospheres on living roots,the presence of crawfish burrows,and geomorphic position;however,the center
Mr.Brian LaFoy,P.E.
TXU Easement-Trail Expansion-Waters of the United States Delineation
31 May 2012 Page 5
of these wetlands were inundated and saturated with water. Wetland 1, Wetland 2, and Wetland 3 met all
three criteria for a wetland. These wetland areas differed from the surrounding uplands,which contained the
same vegetation but did not contain hydric soils or any primary indicators of hydrology; crawfish burrows
were present in the uplands; however,which is a secondary indicator. No culverts or other type of physical
connection to Denton Creek were identified during field investigations. As such, it is likely that Wetland 1,
Wetland 2, and Wetland 3 are connected, or considered adjacent, to the surrounding features and the Elm
Fork Trinity River, and possibly Denton Creek as well, only after high rainfall events and through the 100-
year floodplain. Per the 2007 guidance,as wetlands adjacent to a TNW,Wetland 1,Wetland 2,and Wetland 3
would be considered waters of the United States and regulated under Section 404 of the CWA.
Wetland 4 was located in the center of the project area and was the largest of the wetlands. Wetland 4
collects a large amount of stormwater from the adjacent developments and was characterized by large areas
of deeper water. Tributary 1 and Tributary 2 provide outlets for water into the adjacent impoundments
located on the golf course, which eventually drain into the Elm Fork Trinity River. Tributary 3 provides
another source of hydrology into Wetland 4. Vegetation within Wetland 4 was dominated by water
horehound, various species of sedges, black willow saplings, small areas of cattails, water paspalum, water
primrose, green ash saplings, and spike rush. Several soil test pits were taken throughout the wetland;
however, hydric soils in all test pits were indicated by redox dark surface. Hydrology was indicated by
surface water,saturation,water marks, drift deposits,algal mats,inundation visible on aerial imagery,water
stained leaves,crawfish burrows,and geomorphic position. Wetland 4 met all three criteria for a wetland. A
physical connection was provided by Tributary 1 and Tributary 2 to the adjacent impoundments and Wetland
4 would be considered adjacent to the Elm Fork Trinity River,and possibly Denton Creek as well,through the
100-year floodplain. Per the 2007 guidance,as a wetland adjacent to a TNW,Wetland 4 would be considered
a water of the United States and regulated under Section 404 of the CWA.
Tributary 1 and Tributary 2 provide a hydrologic connection between Wetland 4 and adjacent
impoundments located outside of the project area. The limits of these tributaries were identified and
delineated at the OHWM based on field indicators including destruction of terrestrial vegetation, standing
water,and a shallow bed and bank. Water was flowing from the wetland to the golf course impoundments
through these tributaries. These tributaries appear to have been recently formed as a result of a beaver dam
restricting water through the engineered overflow structure. The location of these tributaries is the next
lowest point in the topography after the beaver dam has restricted the engineered spillway. It is believed that
water within these tributaries is not influenced by ground water,but is surface water only,as such Tributary
1 and Tributary 2 would be considered ephemeral. However, as this water likely flows at least seasonally
with the overflow of runoff from the surrounding developments and wetland areas,Tributary 1 and Tributary
2 would be considered RPWs. Under the 2007 guidance, channels that transport relatively permanent flow
between two or more waters of the United States, including wetlands, are waters of the United States and
regulated under Section 404 of the CWA.
Tributary 3,located along the western project area boundary,is a stormwater drainage channel that directs
stormwater into Wetland 4 from the surrounding uplands and developments to the west. The limits of this
channel were identified and delineated at the OHWM based on destruction of terrestrial vegetation.
Hydrology is provided by stormwater runoff and this channel would be considered ephemeral. As a channel
constructed in uplands to direct stormwater, that does not contain a relatively permanent flow of water,
under the 2007 guidance,Tributary 3 would not be considered a water of the United States and would not be
regulated under Section 404 of the CWA.
Wetland 5 was located at the southern end of the project area and also collected stormwater like the other
wetland areas. Wetland 5 was connected to Wetland 4 through culverts constructed under MacArthur
Boulevard. Vegetation within Wetland 5 was dominated by spike rush, water horehound, and cattails with
areas dominated by willow baccharis. Two soil test pits were dug; hydric soils in both test pits were
indicated by redox dark surface. Hydrology was indicated by oxidized rhizospheres on living roots, water
marks, drift deposits,water stained leaves, and geomorphic position. Wetland 5 met all three criteria for a
wetland. Wetland 5 is shown by FEMA to be located outside the 100-year floodplain;however,it is connected
to Wetland 4 through culverts and topographic surveys show that elevations of Wetland 5 match elevations
within the adjacent 100-year floodplain. Through this connection to a wetland adjacent to a TNW,Wetland 5
would also be considered a water of the United States as well and regulated under Section 404 of the CWA.
Mr Brian LaFoy,P.E.
TXU Easement-Trail Expansion-Waters of the United States Delineation
31 May 2012 Page 6
Tributary 4 was located near the southern end of the project area,flowing from west to east, outfalling into
the project area through culverts and exiting the project area through culverts. It appears that Tributary 4
then continues east, outfalling into an impoundment located on the adjacent golf course. The limits of
Tributary 4 were identified and delineated at the OHWM based on the destruction of terrestrial vegetation
and the presence of a bed and bank. Flowing water was observed within the tributary and it is surmised that
flow is influenced by ground water and as such,Tributary 4 would be considered intermittent. As this water
likely flows at least seasonally,Tributary 4 would be considered a RPW. Drainage patterns within the vicinity
of Tributary 4 can be seen on aerial photographs since 1942. As such, despite is current configuration;
Tributary 4 is likely a functional replacement of a former water of the United States providing a relatively
permanent flow to water of the United States. Under the 2007 guidance,Tributary 4 would be considered a
water of the United States and regulated under Section 404 of the CWA.
Tributary 5 was a stormwater drainage channel that directed stromwater from the surrounding
development into Tributary 4. The limits of this channel were identified and delineated at the OHWM based
on the destruction of terrestrial vegetation and the presence of a shallow bed and bank. Hydrology is
provided by stormwater runoff and this channel would be considered ephemeral. As a channel constructed in
uplands to direct stormwater, that does not contain a relatively permanent flow of water, under the 2007
guidance,Tributary 5 would not be considered a water of the United States and would not be regulated under
Section 404 of the CWA.
Tributary 6 was located at the southern end of the project area, directing stormwater from west to east,
parallel to Belt Line Road. The limits of Tributary 6 were identified and delineated at the OHWM based on the
destruction of terrestrial vegetation and the presence of a shallow bed and bank. Hydrology is provided by
stormwater runoff and this channel would be considered ephemeral. As a channel constructed in uplands to
direct stormwater, that does not contain a relatively permanent flow of water, under the 2007 guidance,
Tributary 5 would not be considered a water of the United States and would not be regulated under Section
404 of the CWA.
SECTION 404 PERMIT ASSESSMENT
The final proposed project has not yet been determined; however,it will involve the construction of hike and
bike trails through the project area. Depending on the final project plan,two nationwide permits,Nationwide
Permit(NWP) 14-Linear Transportation Crossings and NWP 42 -Recreational Facilities could be utilized to
authorize the proposed project. Both permits authorize trails; however,should the proposed project include
other attendant features such as park benches or structures (e.g., gazebos or covered areas), exercise or
information stations,or other recreational-like structures, NWP 42 would have to be utilized. As the project
area consists of large wetland, it is likely that the proposed project would impact wetlands. As such, pre-
construction notification (PCN) under either permit would be required. The following is a summary of the
terms of each permit.
NWP 14 authorizes activities required for the construction,expansion,modification,or improvement of linear
transportation projects (e.g., roads, highways, railways, trails) within waters of the United States; the
discharge cannot exceed 0.5 acre of waters of the United States. Any stream channel modification,including
bank stabilization, is limited to the minimum necessary to construct or protect the linear transportation
project; such modifications must be in the immediate vicinity of the project. The permittee must submit a
PCN to the USACE prior to commencing the activity if the loss of waters of the United States exceeds 0.10 acre
or there is a discharge in a special aquatic site, including wetlands. NWP 14 also authorizes the temporary
structures, fills, and work necessary to construct the linear transportation project. Appropriate measures
must be taken to maintain normal downstream flows and minimize flooding to the maximum extent
practicable, when temporary structures, work, and discharges, including cofferdams, are necessary for
construction activities, access fills, or dewatering of construction sites. Temporary fills must consist of
materials,and be placed in a manner,that will not be eroded by expected high flows. Temporary fills must be
removed in their entirety and the affected areas returned to pre-construction contours. The areas affected by
temporary fills must be re-vegetated,as appropriate.
NWP 42 authorizes the discharge of dredged or fill material into waters of the United States for the
construction or expansion of recreational facilities (e.g., playing fields, basketball or tennis courts, hiking
Mr.Brian LaFoy,P.E.
TXU Easement-Trail Expansion-Waters of the United States Delineation
31 May 2012 Page 7
trails, bike paths, golf courses, ski areas, horse trails, nature centers, campgrounds). This NWP also
authorizes the construction or expansion of small support facilities, such as maintenance and storage
buildings and stables that are directly related to the recreational activity, but it does not authorize the
construction of hotels,restaurants,racetracks,stadiums,arenas,or similar facilities. The discharge must not
cause the loss of greater than 0.5 acre waters of the United States, including the loss of no more than 300
linear feet of stream bed,unless for ephemeral and intermittent streams this limit is waived in writing by the
USACE. The permittee must submit a PCN to the UASCE prior to commencing the activity, regardless of the
size of the impact.
CONCLUSIONS
To summarize the delineation, six tributaries and five wetlands were identified and delineated within the
project area. A summary of these features is presented in Table 1. Based on the June 2007 guidance,
Wetland 1,Wetland 2,Wetland 3,and Wetland 4,as wetlands adjacent to a TNW,would be considered waters
of the United States. A surface connection is provided between Wetland 5 and Wetland 4,as such,Wetland 5
would also be considered a water of the United States. Tributary 1 and Tributary 2 would be considered
waters of the United States as they transport relatively permanent flow between two waters of the United
States. Tributary 4 is likely a functional replacement of a former water of the United States, providing a
relatively permanent flow to a water of the United States,and would therefore also be considered a water of
the United States. All of these features would be regulated under Section 404 of the CWA.
As channels constructed in uplands to direct stormwater that do not contain a relatively permanent flow of
water,under the 2007 guidance,Tributary 3,Tributary 5,and Tributary 6 would not be considered waters of
the United States. These features would not be regulated under Section 404 of the CWA.
This delineation is based on professional experience in the approved methodology and from experience with
the USACE Fort Worth District regulatory biologists; however, this delineation does not constitute a
jurisdictional determination of waters of the United States. Only the USACE can make the final jurisdictional
determination,which can be based on the professional opinions presented in this report.
Proposed activities associated would likely result in impacts to waters of the United States. Depending on the
final outcome of the proposed project plans,permanent impacts could be authorized under either NWP 14 or
NWP 42,with PCN to the USACE.
IES appreciates the opportunity to work with you and Nathan D. Maier Consulting Engineers, Inc. on this
project, and hope we may be of assistance to you in the future. If you have any comments, questions, or
concerns,please do not hesitate to contact Rudi Reinecke at 972/562-7672 (rreinecke @intenvsol.com).
Sincerely,
Integrated Environmental Solutions,LLC.
`/('
Rudi Reinecke
Vice President
Attachments
File ref: 04.051.022
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County: Dallas
State: Texas 1 inch = 2,000 feet
Date map created: 5/24/2012
Source: ESRI 10 Streetmap 0 1,500 3,000 6,000
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Figure 2 N
Topography of the Survey Area 4
Survey Area w_( — E
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County: Dallas S
State: Texas 1 inch = 2,000 feet
Date map created: 5/24/2012
Source: USGS Topographic Map 0 1,500 3,000 6,000
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Soil Series Description
Figure 3 Survey Area
Soil Series located within and Other Values N
adjacent to the Survey Area 1 -Altoga silty clay, 5 12% slopes, eroded
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County: Dallas 36 Frio silty clay, occasionally flooded s
State: Texas 42 - Heiden clay, 2 5% slopes, eroded
Date map created: 5/24/2012 59 Seagoville clay, occasionally flooded 1 inch = 750 feet
Source: 2008 USDA FSATOP
Aerial Photography; 2007 USDA 72 Trinity clay, occasionally flooded
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Figure 4 II Survey Area I
FEMA FIRM FEMA Zone Descriptions W E
with the Survey Area Zone X-Areas determined to be outside the 500-year floodplain s
County: Dallas Zone X-Areas of 500-year flood; areas of 100-year flood with average
depths of less than 1 foot or with drainage areas less than 1 square
State: Texas mile; and areas protected by levees from 100-year flood
Date map created: 5/24/2012 ::.,,,, Zone AE - Special Flood Hazard Areas inundated by 100 ear flood;
Source: Federal Emergency Management "�''' Base Flood Elevations determined y y
Agency Flood Insurance Rate Map r,a Zone AE - Floodway areas in Zone AE
Panel #FM48113C0155J 0 500 1,000 2,000
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Figure 5 Survey Area
Water Features identified a Dataform Locations N
within the Survey Area Features that meet a definition of a Water of the United States
W E
Tributary
County: Dallas _ Wetland S
State: Texas Features that do not meet a definition of a Water of the United States
Date map created: 5/30/2012 Tributary 1 inch = 650 feet
Source: 2008 USDA FSA TOP 0 500 1,000 2,000
Aerial Photography ■ Feet
ATTACHMENT B
Representative Photographs
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Survey Area
Photograph Location Map N
D Photograph Location
Features that meet a definition of a Water of the United States W E
Tributary
County: Dallas s
State: Texas Wetland
Date map created: 5/30/2012 Features that do not meet a definition of a Water of the United States
Source: 2008 USDA FSA TOP Tributary 1 inch = 650 feet
Aerial Photography 0 500 1,000 2,000
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Photograph 3—Facing west Photograph 4—Facing east
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Photograph 11—Facing south Photograph 12—Facing southeast
Photograph 13—Facing southwest Photograph 14—Facing south
Photograph 15—Facing southwest Photograph 16—Facing southeast
Photograph 17 Facing west Photograph 18—Facing northwest
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ATTACHMENT C
Wetland Determination Data Forms-Great Plains Region
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Date: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point 1
Investigator(s): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.), Terrace Local relief(concave,convex,none): Slope%, 0-1
Subregion(LRR): J Lot 32.962651 N Long: -96.955301 W Datum: NAD83
Soil Map Unit Name: Trinity clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, El Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No ❑
Are vegetation, El Soil, El Or hydrology El Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No El
❑ Is the Sampled Area
Hydric Soil Present? Yes ® Na within a wetland? Yes ® No ❑
Wetland Hydrology Present? Yes ® No ❑
Remarks: Herbaceous wetland type.
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator Number of Dominant Species That
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status
Are OBL,FACW,or FAC
(excluding FAC-): (A)
2.
Total Number of Dominant Species
3. Across All Strata: (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: (A/B)
Saalino/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1• Total%Cover of Multiply By
2. OBL species x I=
3- FACW species x 2=
4. FAC species x 3=
5. FACU species x 4=
=Total Cover UPL species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: (A) (8)
1. tyropusamericana 50 Yes OBL
2. Carex tribu/aides 30 Yes OBL Prevalence Index=B/A=
3. Carexrrus-rorvi 5 No OBL
4. Hydrophytic Vegetation Indicators:
5.
6. X 1- Rapid Test far Hydrophytic Vegetation
7. 2- Dominance Test is>50%
8. 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or on a separate sheet)
85 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
I Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plat Size: 30x30 ) disturbed or problematic.
I.
2.
Hydrophytic Vegetation
=Total Cover Present? Yes ® No El
%Bare Ground in Herb Stratum 30
Remarks:Areas with no cover is water or mudflats.
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point: 1
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) % Color(moist) n/o Type' Lac' Texture Remarks
0-2 10YR3/2 95 IORY4/6 5 C _ PL Clay saturated
2-18 10Y03/2 80 10YR4/6 20 C PL/M Clay
'Type: (=Concentration,D=Depletion,RM=Reduced Matrix,CS=Covered or Coated Sand Grains. 'Location: PL=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils':
❑ Histosol(Al) El Sandy Gleyed Matrix(54) ❑ 1 CM Muck(A9)(LRR I,J)
❑ Histic Epipedon(62) ❑ Sandy Redox(55) El Coast Prairie Redox(Al6)(LRR F,G,H)
❑ Black Histic(A3) ❑ Stripped Matrix(56) ❑ Dark Surface(57)(LRR 0)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(Fl) ❑ High Plains Depressions(F16)
❑ Stratified Layers(A5)(LRR F) ❑ Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
❑ 1 cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(F18)
❑ Depleted below Dark Surface(All) ® Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
❑ Thick Dark Surface(Al2) ❑ Depleted Dark Surface(F7) El Very Shallow Dark Surface(TF12)
El Sandy Mucky Mineral(51) ❑ Redox Depressions(F8) El Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(S2)(LRR 6,H) El High Plains Depressions(F16 'Indicators of hydrophytic vegetation and wetland hydrology must
El 5 cm Mucky Peat or Peat(53)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type: Hydric Soil Present? Yes IN No El
Depth(inches):
Remarks:Redox features in a depressed area.
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
® Surface Water(A1( ❑ Salt Crust(B11) ❑ Surface Soil Cracks(B6)
❑ High Water Table(A2) ❑ Aquatic Invertebrates(B13) El Sparsely Vegetated Concave Surface(BB)
® Saturation(A3) El Hydrogen Sulfide Odor(Cl) El Drainage patterns(B10)
❑ Water Marks(81) ❑ Dry-Season Water Table(C2) ❑ Oxidized Rhizospheres on Living Roots(C3)
E l Sediment Deposits(B2) El Oxidized Rhizospheres on Living Roots(C3) (where tilled)
® Drift Deposits(B3) (where not tilled) ❑ Crayfish Burrows(C8)
El Algal Mat or Crust(84) ❑ Presence of Reduced Iron(C4) ❑ Saturation Visible on Aerial Imagery(C9)
E l Iron Deposits(05) El Thin Muck Surface
® Geomorphic Position(D2)
® Inundation Visible on Aerial Imagery(B7) El Other(Explain in Remarks) El FAC-Neutral Test(DS)
® Water Stained Leaves(09)
❑ Frost-Heave Hummocks(D7) (LRR F)
Field Observations:
Surface Water Present? Yes? ® No?❑ Depth(inches): 0-2
Water Table Present? Yes? El No?® Depth(inches): Wetland Hydrology Present? Yes ® No El
Saturation Present? Yes? ® No?El Depth(inches): 0
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Depressed area along TXU powerline.Surrounding landscape was developed and was raised from natural topography.
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Date: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point: 2
Investigator(s): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.): Terrace Local relief(concave,convex,none): concave Slope%:
Subregion(LRR): J Lot: 32.962032 N Long: -96.955511 W Datum: NAD83
Soil Map Unit Name: Trinity clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No El
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No ❑
Hydric Soil Present? Yes ® No El Yes the Sampled Area
within a wetland? Yes ® No El
Wetland Hydrology Present? Yes ® No ❑
Remarks: Shrub dominated wetland type.
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator Number of Dominant Species That
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status
Are OBL,FACW,or FAC
1. (excluding FAC-): (A)
2.
Total Number of Dominant Species
3. Across All Strata: (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: (A/B)
Saolina/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1. Solix nigro 30 Yes FACW Total%Cover of: Multiply By:
2. Fraxinuspennsylvanira 10 Yes FACW OBL species x l=
3. FACW species x 2=
4. FAC species x 3=
5. FACU species x 4=
40 =Total Cover UPI.species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: (A) (B)
1. Solixnigro 5 No FACW
1. Carexlribuloides 10 Na OBL Prevalence Index=B/A=
3. lyropusamericana 40 Yes OBL
4. Typho latifolio 5 No OBL Hydrophytic Vegetation Indicators:
5.
6. X 1- Rapid Test for Hydrophytic Vegetation
7. 2- Dominance Test is>50%
8. 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or on a separate sheet)
60 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
'Indicators of hydric sail and wetland hydrology must be present,unless
Woody Vine Stratum (Plot Size: 30x30 ) disturbed or problematic.
1.
2.
Hydrophytic Vegetation Yes ® No ❑
=Total Cover Present?
%Bare Ground in Herb Stratum 60
Remarks:Shrub canopy<15 feet tall.
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point:2
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) % Color(moist) % Type, Lac' Texture Remarks
0-4 10YR3/2 BO lORY4/6 20 C PL/M CLAY
4-16 IOYR4/6 80 10YR4/6 20 C PL/M (LAY
'Type: C=-Concentration, D=Depletion,RM=Reduced Matrix,CS=Covered or Coated Sand Grains. 'Location: PL=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils':
❑ Histasol(Al) ❑ Sandy Gleyed Matrix(S4) ❑ 1 CM Muck(A9)(LRR I,J)
❑ Histic Epipedon(A2) ❑ Sandy Redox(S5) ❑ Coast Prairie Redox(A16)(LRR F,G,H)
❑ Black Histic(A3) ❑ Stripped Matrix(56) ❑ Dark Surface(S7)(LRR G)
El Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(FI) ❑ High Plains Depressions(F16)
❑ Stratified Layers(A5)(LRR F) El Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
El I cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(F18)
El Depleted below Dark Surface(All) ® Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
❑ Thick Dark Surface(Al2) ❑ Depleted Dark Surface(F7) ❑ Very Shallow Dark Surface(TFI2)
❑ Sandy Mucky Mineral(SI) ❑ Redox Depressions(F8) ❑ Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(S2)(LRR 0,H) ❑ High Plains Depressions(F16 'Indicators of hydrophytic vegetation and wetland hydrology must
❑ S cm Mucky Peat or Peat(S3)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type: Hydric Soil Present? Yes ® No El
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
® Surface Water(Al) ❑ Salt Crust(B11) ❑ Surface SoilCracks(B6)
❑ High Water Table(A2) ❑ Aquatic Invertebrates(B13) El Sparsely Vegetated Concave Surface(B8)
® Saturation(A3) ❑ Hydrogen Sulfide Odor(Cl) ❑ Drainage patterns(B10)
❑ Water Marks(BI) ❑ Dry-Season Water Table(C2) ❑ Oxidized Rhizospheres on Living Roots(C3)
❑ Sediment Deposits(B2) El Oxidized Rhizospheres on Living Roots(C3) (where tilled)
❑ Drift Deposits(B3) (where not tilled) ® Crayfish Burrows(C8)
❑ Algal Mat or Crust(84) El Presence of Reduced Iron(C4) El Saturation Visible on Aerial Imagery((9)
E l Iron Deposits(B5) ❑ Thin Muck Surface ® Geomorphic Position(D2)
® Inundation Visible on Aerial Imagery(B7) ❑ Other(Explain in Remarks) ❑ FAC-Neutral Test(05)
® Water Stained Leaves(B9) ❑ Frost-Heave Hummocks(D7) (LRR F)
Field Observations:
Surface Water Present? Yes? ® No?El Depth(inches): 0-2
Water Table Present? Yes? ❑ No?0 Depth(inches): Wetland Hydrology Present? Yes ® No ❑
Saturation Present? Yes? ® No?El Depth(inches): 0
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks:
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Date: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point: 3
Investigator(s): Rudi Reinecke Section,Township,Range:
Londform(hillslope,terrace,etc.): Local relief(concave,convex,none): Slope%: 0-1
Subregion(LRR): J Let: 32.962306 N Long: -96.955461 W Datum: NAD83
Soil Map Unit Name: Trinity clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No ❑
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No ❑
Hydric Soil Present? Yes ® No ❑ Is the Sampled Area
within a wetland? Yes ® No El
Wetland Hydrology Present? Yes ® No ❑
Remarks: Deep water.
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator Number of Dominant Species That
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status p
Are OBL,FACW,or FAC
1. (excluding FAC-): (A)
2.
Total Number of Dominant Species
3. Across All Strata: (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: (A/B)
Saoling/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1• Total%Cover of: Multiply By:
2. - OBL species x 1=
3. FACW species x 2=
4. FAC species x 3=
5. FACU species x 4=
=Total Cover UPL species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: (A) (B)
1. Paspulum Jluitens 5 No _ 08L
2. Ludwig/orepens 20 Yes OBL Prevalence Index=B/A=
3. fleorar/spolustric 5 No OBL
4. Hydrophytic Vegetation Indicators:
5.
6. X 1- Rapid Test for Hydrophytic Vegetation
7. 2- Dominance Testis>50%
8. 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or on a separate sheet)
30 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plot Size: 30x30 ) disturbed or problematic.
1.
2.
Hydrophytic Vegetation
=Total Cover Present? Yes 12:1
No ❑
%Bare Ground in Herb Stratum
Remarks: Dead stalks of cocklebur;and algae
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point:3
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) % Color(moist) % Type' Lac' Texture Remarks
'Type: (=Concentration, D=Depletion,RM=Reduced Matrix,CS=Covered or Coated Sand Grains. 'Location: Pl=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils3:
❑ Histosol(Al) ❑ Sandy Gleyed Matrix(54) El 1 CM Muck(A9)(LRR I,J)
❑ Histic Epipedon(A2) ❑ Sandy Redox(S5) ❑ Coast Prairie Redox(Al6)(LRR F,G,H)
El Black Histic(A3) El Stripped Matrix(S6) ❑ Dark Surface(57)(LRR G)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(Fl) ❑ High Plains Depressions(F16)
❑ Stratified Layers(A5)(LRR F) ❑ Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
❑ I cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(F18)
❑ Depleted below Dark Surface(All) El Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
❑ Thick Dark Surface(Al2) El Depleted Dark Surface(F7) ❑ Very Shallow Dark Surface(TF12)
❑ Sandy Mucky Mineral(Sl) ❑ Redox Depressions(ED) ® Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(52)(LRR G,H) ❑ High Plains Depressions(Fl6 3lndicators of hydrophytic vegetation and wetland hydrology must
❑ 5 cm Mucky Peat or Peat(53)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type: Hydric Soil Present? Yes ® No El
Depth(inches):
Remarks:No soils were recorded due to depth of water and obvious hydrophytic community.
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
® Surface Water(A1) El Salt Crust(B11) El Surface Soil Cracks(B6)
E l High Water Table(A2) El Aquatic Invertebrates(Bl3) El Sparsely Vegetated Concave Surface(B8)
▪ Saturation(A3) ❑ Hydrogen Sulfide Odor(Cl) El Drainage patterns(B10)
® Water Marks(Bl) El Dry-Season Water Table(C2) ❑ Oxidized Rhizospheres on Living Roots(C3)
El Sediment Deposits(82) ❑ Oxidized Rhizospheres on Living Roots((3) (where tilled)
® Drift Deposits(B3) (where not tilled) El Crayfish Burrows(CB)
® Algal Mat or Crust(B4) ❑ Presence of Reduced Iron(C4) El Saturation Visible on Aerial Imagery(C9)
❑ Iron Deposits(B5) El Thin Muck Surface ® Geomorphic Position(D2)
® Inundation Visible on Aerial Imagery(B7) El Other(Explain in Remarks) El FAC-Neutral Test(D5)
® Water Stained leaves(B9) El Frost-Heave Hummocks(D7) (LRR F)
Field Observations:
Surface Water Present? Yes? ® No?❑ Depth(inches): 8-12 _
Water Table Present? Yes? El No?® Depth(inches): Wetland Hydrology Present? Yes ® No ❑
Saturation Present? Yes? ® No?El Depth(inches): 0
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Deep water area—algae mats hanging on revegetation 4"higher than current water elevation.
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Date: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point: 4
Investigator(s): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.): Terrace Local relief(concave,convex,none): onvex Slope%: 0-I
Subregion(LRR): J Let: 32.961922 N Long: -96.956017 W Datum: NAD83
Soil Map Unit Name: Trinity clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No ❑
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ❑ No
Hydric Soil Present? Yes ❑ Na ® Is the Sampled Area
within a wetland? Yes ❑ No Ej
Wetland Hydrology Present? Yes ❑ No
Remarks: Upland transition into wetland complex
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator Number of Dominant Species That
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status Are OBL,FACW,or FAC
1. (excluding FAC-): 0 (A)
2.
Total Number of Dominant Species
3. Across All Strata: 2 (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: 0 (A/B)
Sapling/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1. Bhusg/ahra 5 Yes NL Total%Cover of: Multiply By:
2. OBL species x 1=
3. FACW species x 2=
4. FAC species x 3=
5. FACU species 105 x 4= 420
5 =Total Cover UPL species 10 x 5= 50
Herb Stratum (Plot Size: 5x5 ) Column Totals: 115 (A) 470 (B)
1. Bromusjaponirus 95 Yes FACU
2. Doke sp. 10 No FACU Prevalence Index=B/A= 4.08 _
3. Tori/isorvensis 5 No NL
4. Hydrophytic Vegetation Indicators:
5.
6. 1- Rapid Test for Hydrophytic Vegetation
7. 2- Dominance Testis>50%
8. 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or on a separate sheet)
110 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
'Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plot Size: 30x30 ) disturbed or problematic.
1.
2.
Hydrophytic Vegetation Yes 1:1 No=Total Cover Present?
%Bare Ground in Herb Stratum <2
Remarks:NL-Species was not listed on the wetland plant indicator status list;assumed upland.
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point:4
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) % Color(moist) % Type' Lac' Texture Remarks
0-16 10YR3/2 50 cloy many fine roots
10YR4/2 50 clay many fine roots
'Type: C=Concentration,D=Depletion,RM=Reduced Matrix,CS=Covered or Coated Sand Grains. 'Location: PL=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils':
❑ Histosal(Al) ❑ Sandy Gleyed Matrix(S4) El 1 CM Muck(A9)(LRR I,J)
❑ Histic Epipedon(A2) ❑ Sandy Redox(S5) ❑ Coast Prairie Redox(A16)(LRR F,6,H)
❑ Black Histic(A3) ❑ Stripped Matrix(S6) ❑ Dark Surface(S7)(LRR 6)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(FI) ❑ High Plains Depressions(F16)
❑ Stratified Layers(A5)(LRR F) ❑ Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
❑ 1 cm Muck(A9)(LRR F,6,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(FI8)
❑ Depleted below Dark Surface(All) ❑ Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
❑ Thick Dark Surface(Al2) ❑ Depleted Dark Surface(F7) ❑ Very Shallow Dark Surface(TFI2)
❑ Sandy Mucky Mineral(Si) ❑ Redox Depressions(F8) ❑ Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(S2)(LRR G,H) ❑ High Plains Depressions(FI6 'Indicators of hydrophytic vegetation and wetland hydrology must
❑ S cm Mucky Peat or Peat(53)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type: Hydric Soil Present? Yes ❑ No El
Depth(inches):
Remarks:Mixed soil,possibly imported.Sewer manholes nearby,possibly along utility line.
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
❑ Surface Water(Al) ❑ Salt Crust(Bll) ❑ Surface Soil Cracks(116)
❑ High Water Table(A2) ❑ Aquatic Invertebrates(B13) ❑ Sparsely Vegetated Concave Surface(B8)
❑ Saturation(A3) ❑ Hydrogen Sulfide Odor(CI) ❑ Drainage patterns(B10)
❑ Water Marks(BI) ❑ Dry-Season Water Table((2) ❑ Oxidized Rhizospheres on Living Roots(C3)
❑ Sediment Deposits(82) ❑ Oxidized Rhizospheres on Living Roots(C3) (where tilled)
❑ Drift Deposits(B3) (where not tilled) ❑ Crayfish Burrows(C8)
❑ Algal Mat or Crust(B4) ❑ Presence of Reduced Iron(C4) ❑ Saturation Visible on Aerial Imagery(C9)
❑ Iron Deposits(115) ❑ Thin Muck Surface
® Geomorphic Position(D2)
❑ Inundation Visible on Aerial Imagery(87) ❑ Other(Explain in Remarks) ❑ FAC-Neutral Test(D5)
❑ Water Stained Leaves(B9)
❑ Frost-Heave Hummocks(07) (LRR F)
Field Observations:
Surface Water Present? Yes? ❑ Na?® Depth(inches):
Water Table Present? Yes? ❑ No?® Depth(inches): Wetland Hydrology Present? Yes ❑ No ED
Saturation Present? Yes? ❑ No?® Depth(inches):
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Ridge into wetland complex.
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Dote: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point: 5
Investigator(s): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.): Local relief(concave,convex,none): Slope%:
Subregion(LRR): 1 Lot: 32.962566 N Long: -96.954203 W Datum: NAD83
Soil Mop Unit Nome: Trinity clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, El Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No El
Are vegetation, El Soil, El Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No El
Hydric Sail Present? Yes ® No ❑ Is the Sampled Area
within a wetland? Yes ® No El
Wetland Hydrology Present? Yes ® No ❑
Remarks:
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator
Tree Stratum (Plot Size: 30x30 ) (overage Species? Status Number of Dominant Species That
Are OBL,FACW,or FAC
1. (excluding FAC-): 1 (A)
2.
Total Number of Dominant Species
3. Across All Strata: 2 (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: 50 (A/B)
Sapling/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1. Total%Cover of: Multiply By:
2. 0111 species 120 x l= 120
3. FACW species x 2=
4. FAC species x 3=
5. FACU species 110 x 4= 440
=Total Cover UPL species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: 230 _ (A) 560 (B)
1. Cynodondarty/on 95 Yes FACU
-
2. (orexlribulaides 25 No OBL Prevalence Index=B/A= 2.4
3. Ambrosia artemisiifolia 10 No FACU
4. Cleorarispa/uslris 60 Yes OBL Hydrophytic Vegetation Indicators:
5. (arex trasgoll, 5 No OBL
6. Sorghumba/epense 5 No FACU 1- Rapid Test for Hydrophytic Vegetation
7. &spalom fluidains 30 No OBL 2- Dominance Testis>50%
8. X 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or on a separate sheet)
230 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
'Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plat Size: 30x30 ) disturbed or problematic.
1.
2.
Hydrophytic Vegetation
=Total Cover Present? Yes ® No El
a Bare Ground in Herb Stratum 0
Remarks: Higher elevation with dominance of bermudagrass.
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point:5
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) % Color(moist) % Type' Lac' Texture Remarks
0-16 10YR3/2 90 10RY4/6 10 C PLUM CLAY
'Type: C=Concentration,D=Depletion,RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils':
❑ Histosol(Al) ❑ Sandy Gleyed Matrix(54) ❑ I CM Muck(A9)(LRR I,J)
❑ Histic Epipedon(A2) ❑ Sandy Redox(S5) ❑ Coast Prairie Redox(A16)(LRR F,G,H)
❑ Black Histic(A3) ❑ Stripped Matrix(56) ❑ Dark Surface(S7)(LRR G)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(F1) ❑ High Plains Depressions(FI6)
El Stratified Layers(A5)(LRR F) ❑ Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
❑ 1 cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(Fl8)
El Depleted below Dark Surface(All) ® Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
El Thick Dark Surface(All) ❑ Depleted Dark Surface(F7) ❑ Very Shallow Dark Surface(TF12)
El Sandy Mucky Mineral(Sl) ❑ Redox Depressions(F8) El Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(52)(LRR G,H) ❑ High Plains Depressions(F16 'Indicators of hydrophytic vegetation and wetland hydrology must
❑ 5 cm Mucky Peat or Peat(S3)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type:
Depth(inches): Hydric Soil Present? Yes ® No El
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
El Surface Water(Al) ❑ Salt Crust(BI I) ❑ Surface Soil Cracks(B6)
❑ High Water Table(A2) ❑ Aquatic Invertebrates(B13) ❑ Sparsely Vegetated Concave Surface(B8)
❑l Saturation(A3) ❑ Hydrogen Sulfide Odor(Cl) ❑ Drainage patterns(BI0)
❑ Water Marks(81) ❑ Dry-Season Water Table(C2) El Oxidized Rhizospheres on Living Roots(C3)
❑ Sediment Deposits(B2) ® Oxidized Rhizospheres on Living Roots(C3) (where tilled)
❑ Drift Deposits(B3) (where not tilled) ® Crayfish Burrows(CB)
❑ Algal Mat or Crust(84) El Presence of Reduced Iron(C4) El Saturation Visible an Aerial Imagery(C9)
❑ Iron Deposits(115) El Thin Muck Surface ® Geomorphic Position(D2)
❑ Inundation Visible on Aerial Imagery(87) El Other(Explain in Remarks) ❑ FAC-Neutral Test(D5)
❑ Water Stained Leaves(B9) ❑ Frost-Heave Hummocks(D7) (LRR F)
Field Observations:
Surface Water Present? Yes? ❑ Na?® Depth(inches):
Water Table Present? Yes? ❑ No?® Depth(inches): Wetland Hydrology Present? Yes ® No ❑
Saturation Present? Yes? ❑ No?® Depth(inches):
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Moist clay soil.
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Dote: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point: 6
Investigators): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.): Local relief(concave,convex,none): Slope%,
Subregion(LRR): J Lat: 32.964610 N Long: -96.953378 W Datum: NAD83
Soil Map Unit Nome: Frio silty clay,accasionolly flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No ❑
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No ❑
Hydric Soil Present? Yes ® No El Yes the Sampled Area
within a wetland? Yes ® No El
Wetland Hydrology Present? Yes ® No ❑
Remarks: Slight depressions within a matrix of uplands.
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status Number of Dominant Species That
Are OBL,FACW,or FAC
(excluding FAC-): (A)
2.
Total Number of Dominant Species
3. Across All Strata: (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: (A/B)
Sapling/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1. Total%Cover of: Multiply By:
2. OBL species x 1=
3. FACW species x 2=
4. FA(species x 3=
5. FACU species x 4=
=Total Cover UPL species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: (A) (B)
1. Phylanodi/loro 75 Yes FACW
2. Carextribu/aides 10 No OBL Prevalence Index=B/A=
3. Paspulumt/uiloins 30 Yes OBL
4. Sporobo/us rryptondrus 20 No FACU Hydrophytic Vegetation Indicators:
5.
6. X 1- Rapid Test for Hydrophytic Vegetation
7. 2- Dominance Testis>50%
8. 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or on a separate sheet)
135 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plot Size: 30x30 ) disturbed or problematic.
1.
2.
Hydrophytic Vegetation
=Total Cover Present? Yes ® No ❑
%Bare Ground in Herb Stratum 5
Remarks:Mowed vegetation.
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point:6
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) % Color(moist) % Type' Lot' Texture Remarks
0-14 10YR3/2 90 lORY3/6 10 C PL CLAY
'Type: (=Concentration,D=Depletion,RM=Reduced Matrix,(S=Covered or Coated Sand Grains. 'Location: PL=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils':
❑ Histosol(Al) ❑ Sandy Gleyed Matrix(S4) ❑ 1 CM Muck(A9)(LRR I,J)
El Histic Epipedon(A2) ❑ Sandy Redox(S5) ❑ Coast Prairie Redox(Al6)(LRR F,G,H)
El Black Histic(A3) ❑ Stripped Matrix(S6) ❑ Dark Surface(S7)(LRR G)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(Fl) ❑ High Plains Depressions(F16)
❑ Stratified Layers(A5)(LRR F) ❑ Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
El 1 cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(F18)
❑ Depleted below Dark Surface(All) ® Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
El Thick Dark Surface(Al2) El Depleted Dark Surface(F7) ❑ Very Shallow Dark Surface(TF12)
❑ Sandy Mucky Mineral(51) ❑ Redox Depressions(F8) ❑ Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(S2)(LRR G,H) El High Plains Depressions(F16 'Indicators of hydrophytic vegetation and wetland hydrology must
❑ 5 cm Mucky Peat or Peat(S3)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type: Hydric Soil Present? Yes ® No ❑
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
El Surface Water(AI) ❑ Salt Crust(611) ❑ Surface Soil(racks(B6)
❑ High Water Table(A2) El Aquatic Invertebrates(BI3) El Sparsely Vegetated Concave Surface(B8)
❑ Saturation(A3) El Hydrogen Sulfide Odor(CI) ❑ Drainage patterns(Bl0)
El Water Marks(Bl) ❑ Dry-Season Water Table(C2) ❑ Oxidized Rhizospheres on Living Roots(C3)
El Sediment Deposits(B2) ® Oxidized Rhizospheres on Living Roots(C3) (where tilled)
❑ Drift Deposits(B3) (where not tilled) ® Crayfish Burrows(C8)
❑ Algal Mat or Crust(84) El Presence of Reduced Iron(C4) ❑ Saturation Visible on Aerial Imagery(C9)
❑ Iron Deposits(B5) El Thin Muck Surface ® Geomorphic Position(D2)
❑ Inundation Visible on Aerial Imagery(B7) ❑ Other(Explain in Remarks) ❑ FAC-Neutral Test(D5)
El Water Stained Leaves(B9) ❑ Frost-Heave Hummocks(D7) (LRR F)
Field Observations:
Surface Water Present? Yes? El No?® Depth(inches):
Water Table Present? Yes? ❑ No?® Depth(inches): Wetland Hydrology Present? Yes ® No ❑
Saturation Present? Yes? ❑ No?® Depth(inches):
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Moist soil—many crayfish burrows,floodplain of Denton Creek.
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Date: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point 7
Investigator(s): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.): Local relief(concave,convex,none): Slope%:
Subregion(ERR): J Lat: 32.965407 N Long: -96.953398 W Datum: NAD83
Soil Map Unit Name: Frio silty clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No ❑
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No ❑
Is the Sampled Area
®
Hydric Soil Present? Yes ❑ No within a wetland? Yes El No
Wetland Hydrology Present? Yes ® No ❑
Remarks:
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status Number of Dominant Species That
Are OBI,FACW,or FAC
1. (excluding FAC-): 0 (A)
2.
Total Number of Dominant Species
3. Across All Strata: 1 (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: 0 (A/B)
5aolina/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1. Total%Cover of: Multiply By:
2. OBL species 40 x l= 40
3. FACW species 5 x 2= 10
4. FAC species x 3=
5. FAQ species 60 x 4= 240
5 =Total Cover UPI species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: 105 (A) 290 (B)
1. Sparabalus rryptandrus 60 Yes FAQ-
2. Carexhibi/aides 20 No OBI Prevalence Index=B/A= 2.76
3. Pospulum trillions 20 No OBL
—
4. lippanod/flora 5 No FACW Hydrophytic Vegetation Indicators:
5.
6. 1- Rapid Test for Hydrophytic Vegetation
7. 2- Dominance Testis>50%
B. X 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or an a separate sheet)
105 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
'Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plot Size: 30x30 ) disturbed or problematic.
1.
2.
Hydrophytic Vegetation Yes ® No ❑
=Total(over Present?
%Bare Ground in Herb Stratum 10
Remarks: Mowed area.
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point 7
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) % Color(moist) oh Type' Lac' Texture Remarks
0-16 10YR3/2 90 CLAY
10YR4/2 10 CLAY
'Type: (=Concentration,D=Depletion,RM=Reduced Matrix,CS=Covered or Coated Sand Grains. 'Location: PL=Pare Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils':
❑ Histosol(Al) ❑ Sandy Gleyed Matrix(54) ❑ 1 CM Muck(A9)(LRR I,J)
❑ Histic Epipedon(A2) ❑ Sandy Redox(55) ❑ Coast Prairie Redox(Al6)(LRR F,G,H)
❑ Black Histic(A3) ❑ Stripped Matrix(S6) ❑ Dark Surface(57)(LRR 6)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(F1) ❑ High Plains Depressiens(F16)
❑ Stratified Layers(A5)(LRR F) El Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
❑ I cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(Fl8)
❑ Depleted below Dark Surface(All) ❑ Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
❑ Thick Dark Surface(Al2) ❑ Depleted Dark Surface(F7) El Very Shallow Dark Surface(TF12)
❑l Sandy Mucky Mineral(51) ❑ Redox Depressions(F8) El Other(Explain in Remarks)
El 2.5 cm Mucky Peat or Peat(S2)(LRR G,H) ❑ High Plains Depressions(F16 'Indicators of hydrophytic vegetation and wetland hydrology must
El 5 cm Mucky Peat or Peat(S3)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type:
Depth(inches): Hydric Soil Present? Yes ❑ No
Remarks:No redox features.
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
❑ Surface Water(Al) ❑ Salt Crust(B11) ❑ Surface Soil Cracks(B6)
El High Water Table(A2) ❑ Aquatic Invertebrates(813) ❑ Sparsely Vegetated Concave Surface(88)
❑ Saturation(A3) El Hydrogen Sulfide Odor(Cl) ❑ Drainage patterns(Bl0)
❑ Water Marks(RI) El Dry-Season Water Table(C2) El Oxidized Rhizospheres on Living Roots(C3)
❑ Sediment Deposits(B2) El Oxidized Rhizospheres on Living Roots(C3) (where tilled)
El Drift Deposits(83) (where not tilled) ® Crayfish Burrows(C8)
El Algal Mat or Crust(84) El Presence of Reduced Iron(C4) El Saturation Visible on Aerial Imagery(C9)
❑ Iron Deposits(B5) ❑ Thin Muck Surface ® Geomorphic Position(D2)
El Inundation Visible on Aerial Imagery(117) El Other(Explain in Remarks) ❑ FAC-Neutral Test(D5)
❑ Water Stained Leaves(B9) El Frost-Heave Hummocks(07) (LRR F)
Field Observations:
Surface Water Present? Yes? El No?® Depth(inches):
Water Table Present? Yes? ❑ No?® Depth(inches): Wetland Hydrology Present? Yes ® No ❑
Saturation Present? Yes? El No?® Depth(inches):
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Few crayfish burrows,near wetland line.
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Date: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point: 8
Investigator(s): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.): Local relief(concave,convex,none): Slope%:
Subregion(LRR): 1 Lot: 32.957637 N Long: -96.958238 W Datum: NAD83
Soil Map Unit Name: Seagoville clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No ❑
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No ❑
Hydric Soil Present? Yes ® No ❑ Is the Sampled Area
within a wetland? Yes ® No 1:1
Wetland Hydrology Present? Yes ® No ❑
Remarks:
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status Number of Dominant Species That
Are OBL,FACW,or FAC
1. (excluding FAC-): (A)
2.
Total Number of Dominant Species
3. Across All Strata: (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: (A/B)
Saalina/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1. Total%Cover of: Multiply By:
2. OBL species x 1=
3. FACW species x 2=
4. FAC species x 3=
5. FAN species x 4=
=Total Cover UPI.species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: (A) (B)
1. Lyropusamericana 5 No OBL
2. E/eorarispa/ustris 75 Yes OBL Prevalence Index=B/A=
3. Lyropussp. 10 No
4. Typha 5 No OBL Hydrophytic Vegetation Indicators:
5.
6. X 1- Rapid Test for Hydrophytic Vegetation
7• 2- Dominance Testis>50%
8. 3- Prevalence Index is<3.0'
9• 4- Morphological Adaptations'(Provide supporting data
ID in Remarks or on a separate sheet)
95 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
'Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plot Size: 30x30 ) disturbed or problematic.
2.
Hydrophytic Vegetation Yes ® No El=Total Cover Present?
%Bare Ground in Herb Stratum 30
Remarks:
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point:8
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redax Features
(inches) Color(moist) '/o Color(moist) '/o Type' Lac' Texture Remarks
0-1 mud/organic
1-3 10YR3/2 95 10YR4/6 5 C PL/M CLAY
3-16 10YR4/2 80 10YR4/6 20 C PL/M
'Type: (=Concentration,D=Depletion,RM=Reduced Matrix,CS=Covered or Coated Sand Grains. =Location: PL=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils':
❑ Histosol(Al) El Sandy Gleyed Matrix(S4) ❑ 1 CM Muck(A9)(LRR I,J)
❑ Histic Epipedon(A2) ❑ Sandy Redox(55) ❑ Coast Prairie Redox(A16)(LRR F,G,H)
❑ Black Histic(A3) ❑ Stripped Matrix(S6) ❑ Dark Surface(57)(LRR G)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(Fl) ❑ High Plains Depressions(F16)
El Stratified Layers(AS)(LRR F) ❑ Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72 8 73)
❑ 1 cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(FI8)
❑ Depleted below Dark Surface(All) ❑ Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
❑ Thick Dark Surface(Al2) ® Depleted Dark Surface(F7) ❑ Very Shallow Dark Surface(TF12)
❑ Sandy Mucky Mineral(51) ❑ Rodeo Depressions(F8) ❑ Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(52)(LRR G,H) ❑ High Plains Depressions(F16 'Indicators of hydrophytic vegetation and wetland hydrology must
El 5 cm Mucky Peat or Peat(S3)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type:
Depth(inches): Hydric Soil Present? Yes ® No ❑
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
❑ Surface Water(Al) ❑ Salt Crust(B11) ❑ Surface Soil Cracks(B6)
❑ High Water Table(A2) ❑ Aquatic Invertebrates(B13) ❑ Sparsely Vegetated Concave Surface(B8)
❑ Saturation(A3) ❑ Hydrogen Sulfide Odor((l) ❑ Drainage patterns(BI0)
® Water Marks(Bl) ❑ Dry-Season Water Table(C2) El Oxidized Rhizospheres on Living Roots(C3)
❑ Sediment Deposits(82) ® Oxidized Rhizospheres on Living Roots(C3) (where tilled)
▪ Drift Deposits(B3) (where not tilled) ❑ Crayfish Burrows(C8)
El Algal Mat or Crust(B4) ❑ Presence of Reduced Iron(C4) ❑ Saturation Visible on Aerial Imagery(C9)
❑ Iron Deposits(05) ❑ Thin Muck Surface ® Geomorphic Position(D2)
® Inundation Visible on Aerial Imagery(67) ❑ Other(Explain in Remarks) ❑ FAC-Neutral Test(D5)
Water Stained Leaves(89) ❑ Frost-Heave Hummocks(D7) (LRR F)
Field Observations:
Surface Water Present? Yes? El No?® Depth(inches):
Water Table Present? Yes? ❑ No?® Depth(inches): Wetland Hydrology Present? Yes ® No ❑
Saturation Present? Yes? ® No?❑ Depth(inches): 0
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Water level appears to have been much higher based on wetland line on slopes.Possibly a beaver/nutria dammed this area a while back.
US Army Corps of Engineers Great Plains—Version 2.0
WETLAND DETERMINATION DATA FORM—Great Plains Region
Project/Site: TXU ROW Trail City/County: Coppell Sampling Date: 4/27/2012
Applicant/Owner: Coppell State: Texas Sampling Point: 9
Investigator(s): Rudi Reinecke Section,Township,Range:
Landform(hillslope,terrace,etc.), Local relief(concave,convex,none): Slope%:
Subregion(LRR): J Let: 32.956989 N Long: -96.958541 W Datum: NAD83
Soil Map Unit Name: Seagoville clay,occasionally flooded NWI Classification:
Are climatic/hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no,explain in Remarks.)
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Significantly disturbed? Are"Normal Circumstances"present? Yes ® No ❑
Are vegetation, ❑ Soil, ❑ Or hydrology ❑ Naturally problematic? (If needed,explain any answers in Remarks.)
SUMMARY OF FINDINGS—Attach site map showing sampling point locations,transects,important features,etc.
Hydrophytic Vegetation Present? Yes ® No ❑
Hydric Soil Present? Yes ® No ❑ Is the Sampled Area
within a wetland? Yes ® No ❑
Wetland Hydrology Present? Yes ® No ❑
Remarks: Higher position in landscape—possibly edge of former inundated area.
VEGETATION—Use scientific names of plants.
Dominance Test worksheet:
Absolute% Dominant Indicator Number of Dominant Species That
Tree Stratum (Plot Size: 30x30 ) Coverage Species? Status Are OBL,FACW,or FAC
1. (excluding FAC-): 2 (A)
2.
Total Number of Dominant Species
3. Across All Strata: 3 (B)
4.
Percent of Dominant Species That
=Total Cover Are OBL,FACW,or FAC: 66.7 (A/B)
Sapling/Shrub Stratum (Plot Size: 15x15 ) Prevalence Index Worksheet:
1. Barrharissahr/na 50 Yes FAC Total%Cover of: Multiply By:
2. Papulus de/loides 10 No FAC OBL species x l=
3. FACW species x 2=
4. FAC species x 3=
5. FACU species x 4=
60 =Total Cover UPL species x 5=
Herb Stratum (Plot Size: 5x5 ) Column Totals: (A) (B)
I. Barchorissulkino 50 Yes FAC
2. Sa/idagogigontea 10 No FAC Prevalence Index=B/A=
3. Sorghumhalepense 30 Yes TACO
4. Hydrophytic Vegetation Indicators:
5.
6. 1- Rapid Test for Hydrophytic Vegetation
7. X 2- Dominance Testis>50%
8. 3- Prevalence Index is<3.0'
9. 4- Morphological Adaptations'(Provide supporting data
10 in Remarks or on a separate sheet)
90 =Total Cover Problematic Hydrophytic Vegetation'(Explain)
'Indicators of hydric soil and wetland hydrology must be present,unless
Woody Vine Stratum (Plot Size: _ 30x30 ) disturbed or problematic.
1.
2.
Hydrophytic Vegetation Yes ® No El
=Total Cover Present?
%Bare Ground in Herb Stratum 40
Remarks:
US Army Corps of Engineers Great Plains—Version 2.0
SOILS Sampling Point:9
Profile Description:(Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color(moist) °/a Color(moist) % Type' Loc7 Texture Remarks
0-12 10YR3/2 20 10YR 4/6 80 C PL/M CLAY dry clay
'Type: (=Concentration, D=Depletion,RM=Reduced Matrix,CS=Covered or Coated Sand Grains. 'Location: PL=Pore Lining,M=Matrix
Hydric Soil indicators: (Applicable to all LRRs,unless otherwise noted.) Indicators for Problematic Hydric Soils3:
El Histosol(Al) ❑ Sandy Gleyed Matrix(54) ❑ 1 CM Muck(A9)(LRR I,J)
❑l Histic Epipedon(A2) ❑ Sandy Redox(55) ❑ Coast Prairie Redox(A16)(LRR F,G,H)
❑ Black Histic(A3) ❑ Stripped Matrix(S6) El Dark Surface(S7)(LRR G)
❑ Hydrogen Sulfide(A4) ❑ Loamy Mucky Mineral(Fl) ❑ High Plains Depressions(F16)
❑ Stratified Layers(A5)(LRR F) ❑ Loamy Gleyed Matrix(F2) ❑ (LRR H outside of MLRA 72&73)
❑ 1 cm Muck(A9)(LRR F,G,H) ❑ Depleted Matrix(F3) ❑ Reduced Vertic(F18)
❑ Depleted below Dark Surface(All) ® Redox Dark Surface(F6) ❑ Red Parent Material(TF2)
El Thick Dark Surface(Al2) ❑ Depleted Dark Surface(F7) ❑ Very Shallow Dark Surface(TFI2)
❑ Sandy Mucky Mineral(51) El Redox Depressions(F8) ❑ Other(Explain in Remarks)
❑ 2.5 cm Mucky Peat or Peat(52)(LRR G,H) ❑ High Plains Depressions(Fl6 'Indicators of hydrophytic vegetation and wetland hydrology must
El 5 cm Mucky Peat or Peat(S3)(LRR F) (MLRA 72&73 of LRR H) be present,unless distributed or problematic.
Restrictive Layer(if present):
Type:
Depth(inches): Hydric Soil Present? Yes ® No El
Remarks:Redox features in a depressed area.
HYDROLOGY
Wetland Hydrology Indicators:
Primary indicators(minimum of one required;check all that apply) Secondary Indicators(minimum of two required)
❑ Surface Water(Al) ❑ Salt Crust(011) El Surface Soil Cracks(B6)
El High Water Table(A2) El Aquatic Invertebrates(013) ❑ Sparsely Vegetated Concave Surface(08)
❑ Saturation(A3) El Hydrogen Sulfide Odor(C1) El Drainage patterns(010)
❑ Water Marks(Bl) El Dry-Season Water Table(C2) ❑ Oxidized Rhizospheres on Living Roots(C3)
❑ Sediment Deposits(82) ® Oxidized Rhizospheres on Living Roots(C3) (where tilled)
❑ Drift Deposits(83) (where not tilled) El Crayfish Burrows(C8)
❑ Algal Mat or Crust(B4) ❑ Presence of Reduced Iron(C4) El Saturation Visible on Aerial Imagery(C9)
❑ Iron Deposits(115) El Thin Muck Surface ® Geomorphic Position(02)
El Inundation Visible on Aerial Imagery(07) El Other(Explain in Remarks) ❑ FAC-Neutral Test(05)
El Water Stained Leaves(B9) El Frost-Heave Hummocks(D7) (LRR F)
Field Observations:
Surface Water Present? Yes? El No?® Depth(inches):
Water Table Present? Yes? ❑ No?® Depth(inches): Wetland Hydrology Present? Yes ® No ❑
Saturation Present? Yes? ❑ No?® Depth(inches):
(includes capillary fringe)
Describe Recorded Data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
Remarks: Dry area—possibly a relic condition of the former hydrology.
US Army Corps of Engineers Great Plains—Version 2.0
ATTACHMENT D
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