tufa glen final report - monroe county, new york
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GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
Green InfrastructureGreen Infrastructure
Rapid Assessment PlanRapid Assessment Plan
Tufa Glen Creek WatershedTufa Glen Creek Watershed
May 2013May 2013
Prepared by:
The Stormwater Coalition
of Monroe County and
Monroe County
Department of
Environmental Services
Prepared for:
New York State Environmental
Protection Fund - Round 10
ii
iii
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
Table of Contents
List of Abbreviations II
1. Assessment Overview
1.1 Problems Statement 1
1.2 Purpose 1
1.3 Setting 1
1.4 Watershed Characteristics 3
1.4.1 Water Quality Concerns 3
1.4.2 Impervious Cover Analysis 4
1.4.3 Drainage Concerns 5
1.4.4 Streambank Erosion 5
1..4.5 Soils 6
2. Retrofit Ranking Inventory 8
2.1 Top Ranked Retrofit Project Diagrams 10
References 17
Appendix A Compiled Data 18
Appendix B NYSDEC Waterbody Datasheet 22
Cover Photo: Upper - Looking downstream at Creek Street; Lower - looking upstream at Creek Street
Page number
iv
List of Abbreviations
cfs cubic feet per second
CWP Center for Watershed Protection
E Education
EMC Event Mean Concentration
EPA US Environmental Protection Agency
GI Green Infrastructure
GIS Geographic Information System
GPS Global Positioning System
IC Impervious Cover
I Infiltration
NYS New York State
NYSDEC New York State Department of Environmental Conservation
POC Pollutant of Concern
S Flood Storage
CP Channel Protection
CR Community Revitalization
Sc Source Control
SWAAP Stormwater Assessment and Action Plan
RH Riparian Habitat
Wq Water Quality
WS Watershed
USGS US Geological Survey
1
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
Section 1. Assessment Overview
1.1 PROBLEM STATEMENT:
Similar to many developing areas, growth in Monroe County has caused some unfortunate
consequences to water quality. One consequence is that developed areas shed larger volumes of
stormwater from impervious surfaces (roads, buildings and parking lots) than natural landscapes.
Because there is more volume, there is more pollution. Typical pollutants include: petroleum
products and heavy metals from vehicles; fertilizers, chemicals and animal waste from lawns; and,
sediment from eroded streambanks, construction sites and roadways.
A second consequence is that streams more frequently flow full or overflow their banks. High
stormwater flows can cause flooding, damage property, and harm fish and wildlife habitat. Common
damages from high flows are eroded stream banks, wider and deeper stream channels, and excessive
sediment deposition. The degradation results in poor water quality and added maintenance costs to
municipalities and property owners. In Monroe County, stormwater pollution and associated wet
weather flows have harmed virtually all urban streams, the Genesee River and Lake Ontario’s
shoreline.
1.2 PURPOSE:
Developing plans to improve our impacted water resources is the objective of this the Rapid
Green Infrastructure Assessment Plan (Plan). Due to limited funding, a method was devised to
quickly evaluate multiple watersheds for stormwater retrofit potential. The main product is a
ranked inventory of retrofit projects that, if constructed, have the potential to improve water
quality and stream health while also providing flow attenuation to reduce erosive storm flows
and localized drainage problems. A second significant product is the creation of multiple,
electronic data files and maps that lay the foundation for future, more in-depth studies. These
files are listed and described in Appendix A. The Plan is a simplified version of more detailed
Stormwater Assessment and Action Plans being done in other parts of Monroe County. These
larger studies include water quality sampling as well as modeling the effects of the current
watershed’s condition and the potential improvement from proposed retrofits. The field work
completed for this report was kept to a minimum and only a summary report is produced
(herein). The project was conducted with funding from New York’s Environmental Protection
Fund, the Monroe County Department of Environmental Services, and the Stormwater
Coalition of Monroe County.
1.3 SETTING:
The entire 1900 acre Tufa Glen Creek watershed lies in the Town of Penfield (Figure 1). The
creek’s headwaters are East of Five Mile Line Road and south of Scribner Road in the
Winchester Woods Subdivision. The main land use throughout the watershed is residential with
a small agricultural area in the northeast (Figure 2). Table 1 shows key watershed
characteristics.
2
Figure 2: Land use within Tufa Glen Creek Watershed.
Tuffa Glen Creek
Land Use
Figure 1: Tufa Glen Creek Watershed.
3
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
1.4 WATERSHED CHARACTERISTICS:
1.4.1 Water Quality Concerns The New York State Department of Environmental
Conservation (NYSDEC), has grouped Tufa Glen Creek with two other minor tributaries of
Irondequoit Bay and designated the streams impaired from urban stormwater runoff (see
separate reports for Glen Haven and Densmore Creeks, Stormwater Coalition of Monroe
County 2013). The full NYSDEC waterbody datasheet is included in Appendix B. In 2010,
these minor tributaries of Irondequoit Creek were added to NYSDEC’s Waterbody Inventory/
Priority Waterbodies List (revised 2013, NYSDEC), or the “303d” list (because it refers to
section 303(d) of the Federal Clean Water Act). The 303d list is generated and updated every
two years by NYSDEC who must consider a restoration strategy to reduce the input of the
specific pollutant(s) that restrict a listed waterbody’s uses or, “impairments”.
Table 1. Watershed Data
Metric Value
Area 1,866 (Acres)
Mapped Stream Length 6.96 (Miles)
Percent of Stream Channelized 21%
Primary/secondary land use Residential/Vacant Land
Land Use (percent of watershed)
Agricultural 6
Residential 67
Vacant Land 14
Commercial 3
Recreation & Entertainment 0
Community Service 4
Industrial 0
Public Services 2
Wild, Forested, Conservation Lands & Public Parks 1
# of Stormwater Treatment Ponds 8
# of Stormwater Outfalls 68
Percent Current Impervious Cover 22 %
Estimated Future Impervious Cover (%)* 26 %
Wetland acres 68.5
Municipal Jurisdiction Penfield NY
* estimated for 20 year build out
4
An impaired water does not support appropriate uses (drinking, swimming, fishing etc.) and
may require the development of a Total Maximum Daily Load (TMDL), a prescribed diet that
limits the inputs of the listed problem pollutants or, some other restoration strategy. Pollutants
noted on the 303d list for these tributaries are oxygen demand, urban runoff, and phosphorus
from municipal sources. Adding to the complexity of the 303d process is how the list is divided
into three parts, depending on how much information is known about the impairments. The
tributaries are listed as a “Waterbody for which TMDL Development May be Deferred
(Requiring Verification of Cause/Pollutant)”. It is anticipated that implementation of this
report’s retrofit projects will help to reduce the impairment level and avoid the regulatory
approach of State and Federal mandates.
1.4.2 Impervious Cover Analysis The Center for Watershed Protection created the
“Impervious Cover Model” (ICM) to predict a typical stream’s health using the relationship
between subwatershed impervious cover and stream quality indicators and has been confirmed
by nearly 60 peer-reviewed stream research studies (Figure 3) . The ICM shows that stream
quality decline becomes evident when the watershed impervious cover exceeds ten percent.
Tuffa Glen has an average of 22 percent impervious cover placing stream quality somewhere
between poor and good and impacted aquatic life. Based on current zoning, future impervious
cover (over the next 20 years) will increase by 4 percent.
Figure 3. Impervious Cover Model
5
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
1.4.3 Drainage Concerns Interviews with DPW staff at the Town of Penfield and a review
of their drainage studies identified drainage issue areas. While most drainage issues have been
addressed by an active stormwater management program in the Town, some minor drainage
concerns persist in low-lying areas
1.4.4 Streambank Erosion There were no reported erosion sites on Tufa GlenCreek from
assessments done by the Monroe County Soil & Water Conservation District in 2001. However,
there is extensive lengths of eroded stream bank in the lower segment as the Creek falls
approximately 100 feet in elevation from Creek Street to Irondequoit Bay through highly
erodible glacial soils (Figure 4).
Staff at the Town of Penfield found no recent reports of erosion complaints in the upper
watershed however, as the stream has been channelized and heavily armored where it flows
through residential subdivisions built in the 1960’s and 70’s (Figure 5).
Figure 4. Eroded Streambank downstream of Creek Street on Tufa Glen
6
1.4.5 Soils A simplistic yet useful way to define how much stormwater runs off the
pervious land surface is to determine soils’ infiltration capabilities, their ability to absorb
stormwater. Soil scientist have categorized soils into four categories, A through D. A and B
soils are well drained and absorb much of the stormwater that drains on or over them. C and D
soils are more poorly drained. However, the soils in some parts of this watershed are not
categorized, denoting areas that have been so altered by land development that grouping a
specific soil type is not feasible. The amount of each soil type in Tufa Glen Creek is: A soils
1%; B soils 32%; C soils 41%; D soils or not verified 26% (Figure 6).
The fairly large percentage of B soils will allow for infiltration-type stormwater retrofits.
These practices installed in the watershed can prevent and reduce flooding, drainage problems,
and streambank erosion as well as greatly improving water quality in Tufa Glen Creek.
Figure 5. Tufa Glen Creek (blue dashed line) rock-lined and channelized
7
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
Figure 6. Hydric Soils Map of Tufa Glen Creek
Tuffa Glen Creek
Soils
8
Section 2. Retrofit Inventory
An inventory of potential retrofit sites was generated using GIS mapping tools to locate public
properties, stormwater practices like ponds, old urban areas (built before stormwater management
requirements) and, pervious soil areas. Next, the appropriate stormwater management practice was
determined for the properties identified and those were ranked based on their feasibility, how much
they would improve water quality and, cost-effectiveness. While the stormwater management
practice types focused on green infrastructure (stormwater volume-reducing practices such as
infiltration) retrofitting stormwater ponds is a highly cost-effective practice and these projects rank
well and are recommended. Complete details of methods used to complete the rapid assessment and
retrofit ranking is explained in a reference document titled “Assessment Methodology, Project
Descriptions, and Retrofit Ranking Criteria For Monroe County Green Infrastructure Rapid
Assessment Plans”.
Two broad categories of retrofit project types were considered:
1) New stormwater ponds, upgrades to existing stormwater ponds and new stormwater storage
to existing drainage channels.
2) Green Infrastructure (GI). This category was divided and ranked by where a GI project
might be installed and includes:
Public Right of Ways,
Older Residential Neighborhoods, and
Other Locations (such as areas with large impervious surfaces ie shopping malls)
Other watershed retrofitting that would help meet water quality goals though considered outside
of the scope of this report include the investigation and remediation of any stormwater hotspots
and dechannelization and revegetation of straightened and degraded stream corridors.
Figure 7 shows project locations and project number within the watershed. Table 2 lists project
addresses and how they scored. Diagrams of the top scoring projects follow the table.
9
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
Figure 7. Retrofit Project Locations Map of Tufa Glen Creek
10
Tab
le 2
T
ufa
Gle
n R
etro
fit
Ran
kin
g L
ist
Map
ID
Pro
ject
Typ
e O
vera
ll
Ran
k P
roje
ct L
oca
tio
n
Fea-
sab
ility
Wat
ers
hed
Ben
efits
Co
st E
ffe
c-
tivn
ess
Sco
re
D2
Dry
Po
nd
1
145
1 F
ive
Mile
Lin
e R
d
5
I, F
S, W
Q
3
13
D3
Dry
Po
nd
1
155
0 S
crib
ner
Rd
5
FS
, WQ
, CP
, 3
1
3
D1
Dry
Po
nd
1
157
5 F
ive
Mile
Lin
e R
d
5
I, F
S, W
Q, C
P
3
13
P2
New
Po
nd
2
con
stru
ct n
ew p
on
d in
mo
we
d a
rea
(no
re
crea
tio
n)
5
I, F
, WQ
, CP
, 3
1
1
P1
New
Po
nd
2
Pla
nk
Ro
ad S
ou
th a
t so
uth
we
st p
rop
erty
co
rner
4
F,
WQ
,CP
,E
3
11
W1
Wet
Po
nd
Co
n-
vers
ion
2
148
0 S
crib
ner
Rd
(B
eaco
n H
ills)
5
F,
WQ
, CP
3
1
1
O5
Oth
er G
I Pro
ject
s 3
T/O
Pen
fie
ld c
aptu
re r
un
off
fro
m c
or
emb
ury
an
d s
crib
ner
2
I,
WQ
, SC
, E
3
10
W2
Wet
Po
nd
Co
n-
vers
ion
3
36
A W
oo
dfi
eld
Dr
(ac
ross
fro
m P
lan
k R
d S
. Ele
m)
5
WQ
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3
1
0
N8
N
GI
4 B
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ill
2
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C
3
9
N2
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elvi
sta
2
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C
3
9
N9
N
GI
4 G
len
bro
ok
2
CR
,WQ
,E,S
C
3
9
N1
1
NG
I 4
Ind
ian
Rid
ge. w
ith
ersp
oo
n h
itch
cock
sto
ckto
n
2
CR
,WQ
,E,S
C
3
9
N1
4
NG
I 4
Man
se L
ane
2
CR
,WQ
,E,S
C
3
9
N7
N
GI
4 P
icci
dill
y P
ark
2
CR
,WQ
,E,S
C
3
9
N4
N
GI
4 R
oya
l Cre
st
2
CR
,WQ
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C
3
9
N1
2
NG
I 4
Ro
yal W
oo
ds
2
CR
,WQ
,E,S
C
3
9
N1
0
NG
I 4
Sheffi
eld
Sq
uar
e 2
C
R,W
Q,E
,SC
3
9
N1
3
NG
I 4
Sheffi
eld
Sq
uar
e 2
C
R,W
Q,E
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3
9
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N
GI
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e H
amp
ton
s 2
C
R,W
Q,E
,SC
3
9
N1
5
NG
I 4
Tho
mas
Mar
ia C
ircl
e 2
C
R,W
Q,E
,SC
3
9
N1
N
GI
4 Tu
fa G
len
2
C
R,W
Q,E
,SC
3
9
N5
N
GI
4 W
inch
este
r 2
C
R,W
Q,E
,SC
3
9
N6
N
GI
4 W
yan
dal
e 2
C
R,W
Q,E
,SC
3
9
O1
5
Oth
er G
I Pro
ject
s 4
c-d
-s b
iore
ten
tio
n B
eth
al G
reen
3
I,
WQ
3
9
O1
6
Oth
er G
I Pro
ject
s 4
c-d
-s b
iore
ten
tio
n C
aven
dis
h
3
I, W
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3
9
O8
Oth
er G
I Pro
ject
s 4
c-d
-s b
iore
ten
tio
n C
edar
bro
ok
Cir
3
I,
WQ
3
9
O2
1
Oth
er G
I Pro
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s 4
c-d
-s b
iore
ten
tio
n M
orn
ing
Wo
od
s 3
I,
WQ
3
9
11
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
Tufa
Gle
n C
reek
Ret
rofi
t R
ankin
g L
ist
Map
I.D
. P
roje
ct T
ype
Ove
rall
Ran
k P
roje
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Feas
abil-
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Wat
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B
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3
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3
8
W5
Wet
Po
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Co
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sio
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06 E
mb
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Ro
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San
filli
pp
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2
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3
8
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12
13
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
14
15
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
16
17
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
References:
Center for Watershed Protection. 2004a. Unified Stream Assessment: A User’s Manual. Manual 10 in
the Urban Subwatershed Restoration Manual Series. Center for Watershed Protection, Inc. Ellicott
City, MD.
2004b. Unified Subwatershed and Site Reconnaissance: A User’s Manual. Manual 11 in the
Urban Subwatershed Restoration Manual Series.
2005. An Integrated Framework to Restore Small Urban Streams User’s Manual. Manual 1 in
the Urban Subwatershed Restoration Manual Series.
2007. Stormwater Retrofit Practices. Manual 3 in the Urban Subwatershed Restoration
Manual Series.
New York State Department of Environmental Conservation. 2004. Ontario Basin Waterbody
Inventory and Priority Waterbodies List, Revised 2007
18
Rapid Assessment Compiled Data
APPENDIX A
19
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
Tufa
Gle
n C
reek
Rap
id A
sses
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t D
ata
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o t
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the
wat
ersh
ed b
ou
nd
ary.
Tu
fa G
len
Wat
ersh
ed.p
df
Mo
nro
e C
ou
nty
A
map
of
the
wat
ersh
ed d
isp
layi
ng
the
diff
eren
t la
nd
use
ty
pes
bas
ed u
po
n p
arce
l dat
a.
Tufa
Gle
n L
ULC
.pd
f M
on
roe
Co
un
ty
Th
is m
ap d
isp
lays
all
of
the
ho
t sp
ot
loca
tio
ns
thro
ugh
ou
t th
e w
ater
shed
. Tu
fa G
len
HS.
pd
f M
on
roe
Co
un
ty
Th
is m
ap d
isp
lays
all
of
the
ou
tall
loca
tio
ns
thro
ugh
ou
t th
e w
ater
shed
. Th
e o
utf
alls
are
rat
ed b
ased
up
on
po
ssi-
ble
illic
iet
dis
char
ge.
Tufa
Gle
n O
utf
alls
.pd
f M
on
roe
Co
un
ty
Th
is m
ap d
isp
lays
th
e h
ydro
lic s
oils
(A
, B, C
, D)
thro
ugh
-o
ut
the
wat
ersh
ed.
Tufa
Gle
n S
oils
.pd
f M
on
roe
Co
un
ty
Th
is m
ap d
isp
lays
th
e lo
cati
on
s o
f va
rio
us
stre
am p
roje
cts
thro
ugh
ou
t th
e w
ater
shed
. Tu
fa G
len
Str
eam
Pro
-je
cts.
pd
f M
on
roe
Co
un
ty
Th
is m
ap d
isp
lays
th
e lo
cati
on
s o
f th
e p
ote
nti
al p
roje
cts
site
s th
rou
gho
ut
the
wat
ersh
ed.
Tufa
Gle
n P
roje
ct S
ite
s.p
df
Mo
nro
e C
ou
nty
20
Re
tro
fit
Dia
gram
s
D2
1
45
1 F
ive
Mile
Lin
e R
d
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
D3
1
55
0 S
crib
ner
Rd
.p
df
and
.mxd
M
on
roe
Co
un
ty
D1
1
57
5 F
ive
Mile
Lin
e R
d
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
P2
co
nst
ruct
new
po
nd
in m
ow
ed
are
a (n
o r
ecre
atio
n)
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
P1
P
lan
k R
oad
So
uth
at
soth
wes
t p
rop
erty
co
rner
.p
df
and
.mxd
M
on
roe
Co
un
ty
W1
1
48
0 S
crib
ner
Rd
(B
eaco
n H
ills)
.p
df
and
.mxd
M
on
roe
Co
un
ty
O5
T/
O P
enfi
eld
cap
ture
ru
no
ff f
rom
co
r em
bu
ry a
nd
scr
ib-
ner
.p
df
and
.mxd
M
on
roe
Co
un
ty
W2
3
6A
Wo
od
fiel
d D
r (
acro
ss f
rom
Pla
nk
Rd
S. E
lem
) .p
df
and
.mxd
M
on
roe
Co
un
ty
N8
B
eaco
n H
ill
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N2
B
elvi
sta
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N9
G
len
bro
ok
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N1
1
Ind
ian
Rid
ge. w
ith
ersp
oo
n h
itch
cock
sto
ckto
n
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N1
4
Man
se L
ane
.p
df
and
.mxd
M
on
roe
Co
un
ty
N7
P
icci
dill
y P
ark
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N4
R
oya
l Cre
st
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N1
2
Ro
yal W
oo
ds
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N1
0
Sheffi
eld
Sq
uar
e
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N1
3
Sheffi
eld
Sq
uar
e
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N3
Th
e H
amp
ton
s .p
df
and
.mxd
M
on
roe
Co
un
ty
N1
5
Tho
mas
Mar
ia C
ircl
e
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
N1
Tu
fa G
len
.p
df
and
.mxd
M
on
roe
Co
un
ty
N5
W
inch
este
r .p
df
and
.mxd
M
on
roe
Co
un
ty
N6
W
yan
dal
e .p
df
and
.mxd
M
on
roe
Co
un
ty
O1
5
c-d
-s b
iore
ten
tio
n B
eth
al G
reen
.p
df
and
.mxd
M
on
roe
Co
un
ty
O1
6
c-d
-s b
iore
ten
tio
n C
aven
dis
h
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
O8
c-
d-s
bio
rete
nti
on
Ced
arb
roo
k C
ir
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
O2
1
c-d
-s b
iore
ten
tio
n M
orn
ing
Wo
od
s .p
df
and
.mxd
M
on
roe
Co
un
ty
O1
7
c-d
-s b
iore
ten
tio
n P
icca
dill
y .p
df
and
.mxd
M
on
roe
Co
un
ty
O1
0
c-d
-s b
iore
ten
tio
n R
ob
ert
Ro
ad
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
O2
5
c-d
-s b
iore
ten
tio
n s
un
leaf
.p
df
and
.mxd
M
on
roe
Co
un
ty
O9
c-
d-s
bio
rete
nti
on
Win
ner
s C
ir
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
Tufa
Gle
n C
reek
Rap
id A
sses
smen
t D
ata
All
file
are
loca
ted
in t
he
follo
win
g p
aren
t d
irec
tory
if n
ot
oth
erw
ise
stat
ed: H
:\IW
\Sto
rmw
ate
r\A
smn
t\Tu
fa G
len
\
Fold
er N
ame
De
scri
pti
on
Fi
le N
ame
Dat
a O
rigi
n
21
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
O1
B
iore
ten
tio
n -
Cap
ture
ru
no
ff f
rom
par
kin
g lo
t .p
df
and
.mxd
M
on
roe
Co
un
ty
W5
4
06
Em
bu
ry R
oad
(Sa
nfi
llip
po
) .p
df
and
.mxd
M
on
roe
Co
un
ty
O1
1
c-d
-s b
iore
ten
tio
n B
eech
bro
ok(
pri
vate
dr)
.p
df
and
.mxd
M
on
roe
Co
un
ty
O1
9
c-d
-s b
iore
ten
tio
n C
rab
tree
.p
df
and
.mxd
M
on
roe
Co
un
ty
O1
4
c-d
-s b
iore
ten
tio
n C
reek
Hill
.p
df
and
.mxd
M
on
roe
Co
un
ty
O2
2
c-d
-s b
iore
ten
tio
n C
rest
view
.p
df
and
.mxd
M
on
roe
Co
un
ty
O1
8
c-d
-s b
iore
ten
tio
n F
low
er
Val
ley
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
O2
3
c-d
-s b
iore
ten
tio
n R
oya
l Vie
w
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
O1
2
c-d
-s b
iore
ten
tio
n S
anfi
llip
po
Cir
.p
df
and
.mxd
M
on
roe
Co
un
ty
O1
3
c-d
-s b
iore
ten
tio
n S
avan
nah
Cir
.p
df
and
.mxd
M
on
roe
Co
un
ty
O2
0
c-d
-s b
iore
ten
tio
n T
ho
mas
Mar
ia
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
O2
4
c-d
-s b
iore
ten
tio
n w
oo
dfi
eld
.p
df
and
.mxd
M
on
roe
Co
un
ty
W3
1
35
0 F
ive
Mile
Lin
e R
d (
Ch
urc
h o
n c
or
of
Pla
nk)
.p
df
and
.mxd
M
on
roe
Co
un
ty
W4
5
Sea
wat
ch T
rail
.pd
f an
d .m
xd
Mo
nro
e C
ou
nty
Tufa
Gle
n C
reek
Rap
id A
sses
smen
t D
ata
All
file
are
loca
ted
in t
he
follo
win
g p
aren
t d
irec
tory
if n
ot
oth
erw
ise
stat
ed: H
:\IW
\Sto
rmw
ate
r\A
smn
t\Tu
fa G
len
\
Fold
er N
ame
De
scri
pti
on
Fi
le N
ame
Dat
a O
rigi
n
22
NYSDEC PWL Datasheet
APPENDIX B
23
GREEN INFRASTRUCTURE RAPID ASSESSMENT PLAN TUFA GLEN WATERSHED
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