Dam Operation and Maintenance PlanT 1 n d
onsultzngEngineers
Environmental Specialists
N-311-2-16
March 9, 1998
F1
Commonwealth of Massachusetts
Department of Environmental Protection
Office of Dam Safety
P.O. Box 173
Old Common Road
Lancaster, MA 01523
Re: Fitzgerald Pond Dam Repair
Northampton, MA
n . Gentlemen:
L 1-1
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0 Please review the application at your earliest convenience and contact the undersigned if you should
On behalf of the City of Northampton, we are submitting to you herewith two (2) copies of an
Application for Authorization to Construct or Alter Reservoir, Reservoir Dam or Mill Dam.
The application covers repairs to the dam crest, removal of brush, replacement of the outlet endwall,
modification of the drawdown gate, rebuilding the principal spillway inlet and lining the drop inlet and
discharge conduit with a stainless steel sleeve.
Please refer to the plans and specifications that are made part of the application package being
submitted to your office for review of details on the project. The application. form contains all
information regarding the capability of the dam to pass the design flood and elevations of pertinent
features of the dam.
have any questions.
Very truly yours,
TIG BOND, INC.
avid M. Lenart, P.E.
Associate
l fnU:V311\LTR\DML-A.DOC
1 Enclosures
Copy: Wayne Feiden, AICP, Northampton
Westfield Executive Park 53 Southampton Road, Westfield, MA 01085-5308. Tel 413-5621600 Fax. 413-56j-5317
J
Original printed on recycled paper.
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Commonwealth of Massachusetts
Executive Office. of Environmental. Affairs
Department ofEnvironmental. Management-
P.O. Box173
FDld Common Road
APPLICATION FOR AUTHORIZATION TO CONSTRUCT OR ALTER A
RESERVOIR, RESERVIOR DAM OR MILL DAM
I ancaster, MA
01523
[1jb17) 727-0627
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on:
-'Dam SafetyProgmm
General Laws: Chapter 253,s.44 et seq. as amended by
Chapter 706 of the Acts of 1975
Chapter 720 of the Acts of 1979
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The approval of the Commissioner shall not apply to sma.11
dams, constructed for irrigation or for other purposes, the
breaking of which would involve no risk to life or property, not
to standpipes or tanks, nor to a dam where the area draining into
the pond formed thereby does not exceed one square mile; unless
a
the dam is more than ten feet in height above the natural bed of
the stream at any point, or unless the quantity of water which
n
the dam impounds exceeds one million gallons. However, informa-
ti
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b
on must
e su
mitted to enable the Commissioner to determine
whether approval is necessary.
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Approval of this plan does not 'release the applicant from the
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requirements of Chapter 91, or Chapter 131 of the Massachusetts
General Law.
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Part "A"
JURISDICTIONAL DETERMINATION
(check. the- appropriate column). _
1. Is there a risk to life and property
downstream in the event of failure?
2. Does the area draining into the pond
exceed one square mile ?
3. Does the height of the dam exceed 10 ft.
above the natural bed of the stream at
any point?
41- Does the volumn of water impounded at
maximum pool level exceed one million
gallons?
Yes No
X
X
X
X
If. the answer to any one of. the above questions is Yes, then the
Commissioner of Department of Environmental Management has jurisdic-
tion. Proceed with Part B of this application.
If the answers to all four of the above questions are No, please
submit backup information fora review by this Department for our
jurisdictional determination. The backup information should include
at least:
a. A copy of a topographic map clearly indicating the location of
the dam and the effective drainage area.
b. A sketch showing the maximum section of the dam indicating its
height, as measured from the lowest point of the streambed.
c. Calculations for the volume of water impounded at the maximum
design pool level.
d. A brief statement pertaining to downstream. conditions with
respect to risk to life and property.
e. The signature of applicant and engineer.
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Part; "B"
GENERAL INFORMATION
1. Location (City-Town): City of Northampton
2. Detailed description of dam location:
The dam is located in the City of Northampton on a tributary
to Broad Brook and about 4000' east of North Farms Road,
along the tributary. See locus plan - Attachment A.
3. Present or Prospective Owner(s):
Name(s) City of.Northampton
Street 210 Main Street
State Zip
City/Town Northampton, MA 01060
Telephone 1-413-586-6950
4. Name of U.S. Geological Survey Map Quadrangle:
Easthampton, MA
5. Name of Reservoir or Waterway: Fitzgerald Pond
6. Is there specific legislative authority to construct the dam?
Yes ( ) Indentify
No (X )
7. Purpose. for the dam: Recreation
8. Nature of the work:
Proposed dam ( )
Alteration of existing dam. ( )
Major repair of. existing dam M
Regular maintenance. ( ) If checked go to Part. "C"
-4-
Part "B" (continued)
HAZARD EVALUATION
(Downstream Field Investigation)
1. The estimated number- of people that could be affected by over
topping or failure of the structure, and to what degree they
would be affected.
Overtopping or failure of Fitzgerald Pond Dam would not affect
any people due to the downstream area being unoccupied and the
flood surge would be dissipated before reaching populated areas.
2. The number of properties (homes, buildings etc.) and the esti-
mated extent of damage by overtopping or failure.
Other than flooding of wetlands and the stream bed, no homes
or.buildings would be damaged.
3. Roads (type) or other structures that could be affected by
overtopping or failure.
No roads or other structures would be affected before the
flood surge would be dissipated.
4. Additional Information:
N/A
-5-
.Part "B" (continued)
i
HYDROLOGIC CONSIDERATIONS
Procedures for hydrologic design as contained in the latest edi-
tion of the U.S. Department of the Interior, Bureau of Reclamation
"Design of Small Dams".
1. Peak Outflow 250.29(1) c.f.s..
2. Design Storm Duration 24 hr. (100 yr. event)(2)
3. 'Rainfall Intensity 4.5(3) "/hr. .
Percent Runoff 666 2,97 inches.
4. Contributory Drainage Area 1.61(6) sq. mi.
(Attach a copy of U.S. Topographic Map with
the outline of the drainage divide).
Refer to Attachment C.
5. Previous Known Flood of Record
.(month) August (year) 1955
6. Design Maximum Flood. Level.Elevation 99.39'
7. Additional Information:
Maximum flood level will be 0.39 ft. over
emergency spillway elevation 99.0 ft.
(1)Based on TR-20 results attached.
(2) Spillway design flood determined from Section 10 Dam Safety,
•302 CMR: Department of Environmental Management (December 1,
1993); Refer to Attachment B for the TR-.20 results.
(3) Rainfall intensity based on tc of 0.48 hours.
(4) The value given is the composite curve.number.
(5)Based on the SCS runoff equation.
(6) Fitzgerald Pond surface area not included.
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Part "B" (continued)
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DESIGN CRITERIA
1. Datum used:
(a) M.S.L~ of 1929 N/A
(b) Assumed Assumed
(c) Other N/A
2. Maximum height of the dam 9.5 ft.
(a) Top elevation of dam 101.5
(b) Top elevation of spillway 96.5 (Principal)
99.0 (Emergency)
3,1 Volume of water impounded, at
maximum design pool level. 140,000,000 (420 AF). gallons
4. Present river bed or channel
elevation @ dam 82.0
5. Normal pool elev. 96.5
surface area 42 acres ± ac.
6.. Maximum pool elev. 99.39
surface area 50 acres t ac.
7. Type of structure (earth, concrete, etc.)
Earth fill dam with side channel emergency spillway
8. Crest width 15 ft.
9. Freeboard, as measured from the maximum design
pool level 101.50 - 99.39 = 2.11 ft.
10. Length of principal spillway 66.0 in. diameter
11. Description of principal spillway 66.0 in. diameter
Drop inlet with galvanized debris shield..
-7-
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Part "B" (cont.inued.)
Design Criteria
12. Emergency spillway Yes ( X) No ( )
If yes, describe- 60 ft. long; 20 ft. crest width grass limed
13. Gates- Yes ( X ) Number 1 Size 18 in.
No ( )
14. Nature of slope protection
(riprap, vegetated etc.) riprap upstream/grass downstream.
15. Stop log structure(s)
Yes ( ) Mechanical ( ) Manual (
No (X )
4
SUBSURFACE INVESTIGATION
Boring logs, analysis and recommendations to accompany this
application
Borings not carried out due to nature of repairs.
CONSTRUCTION DRAWINGS
Names & addresses of property owners for all parcels of land
within the flowage area must be clearly indicated on the plan. Submit
2 copies.with this application.
City of Northampton, MA
See Plans and Specifications under separate cover.
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Part "5" (continued)
SIGNATURE SHEET
APPLICANT
Name City of Northampton
Street 210 Main Street - City Hall
City/Town Northampton State MA Zip 01060
Telephone 1-413-586-6950
Signature Date
Wayne Feiden, AICP
DESIGN ENGINEER
Name Tighe & Bond, Inc. -
Street 53 Southampton Road
City/Town Westfield State MA Zip 01085
Telephone 1-413- 2-1600
Signature Date-3-5 9~
David M. Lenart, Y.E.
*Engineer's Stamp must be included.
Upon receipt of this required apllication a prompt determination
will be made on issuing a. permit to proceed. Conditions of such a
permit will be contingent upon the nature of proposed work.
*ENGINEER'S STAMP:
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Part "Cn
REGULAR MAINTENANCE.
PROJECT CONSISTS OF REPAIR
If the proposed work involves regular maintenance~_act.ivities. (i.e.
The proposed work does not. mater.ia.ll.y alter- the dam..) a.: permit.
% is not required..
Typical maintenance activities include, but are not limited to the
following items.
Please indicate the nature of proposed maintenance and return the
complete application. Use additional paper if necessary.
NO YES
Surface cracks?
Slumping or'cracking on
the upstream or downstream
side?
Erosion from runoff, wave
action or traffic?
Embankment/spillway seepage?
Water muddy?
Top of dam settled?
Loss of riprap?
Tress, brush,. or burrows
on embankment?
Spillways blocked?
Exposed metal rusty?
Concrete deterioration or
cracks?
Cracks or. uneven movement?
Scour?
Pipe joint separation?
Gates operational?
Trash racks blocked?
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LOCATION OF PROPERTY
1. Location (City-Town) City of Northampton, MA,
2. Registry of Deeds Book 1951 Page 261
/3. Locus Map; please- attach.
See Locus. Map in Attachment A.
-A.
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TR-20 Fitzgerald Lake
Flood Routing -100 Year Storm
F] Northampton, Massachusetts
******************80-80 LIST OF INPUT DATA FOR TR-20 HYDROLOGY******************
JOB TR-20
FULLPRINT
SUMMARY
TITLE 001
FITZGERALD LAKE
FLOOD ROUTING
FILE:
N-311-2-16
TITLE
MARCH 03, 1998
l
5 RAINFL
7
0.1
8
0.000
0.001
0.002
0.003
0.004
8
0.005
0.006
0.007
0.008
0.009
7-1
8
0.010
0.011
0.012
0.013
0.014
1
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8
0.015
0.016
0.017
0.018
0.019
-
8
0.020
0.021
0.022
0.023
0.024
8
0.026
0.027
0.028
0.029
0.030
8
0.031
0.032
0.034
0.035
0.036
8
0.037
0.038
0.040
0.041
0.042
8
0.043
0.045
0.046
0.047
0.049
8
0.050
0.051
0.053
0.054
0.055
8
0.057
0.058
0.060
0.061
0.063
i
8
0.064
0.066
0.067
0.069
0.070
_
8
0.072
0.074
0.075
0.077
0.079
8
0.080
0.082
0.084
0.085
0.087
8
0.089
0.091
0.093
0.095
0.097
I
8
0.100
0.103
0.106
0.109
0.112
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8
0.115
0.118
0.121
0.124
0.127
8
0.130
0.134
0.137
0.140
0.144
8
0.148
0.151
0.155
0.159
0.163
8
0.167
0.171
0.176
0.180
0.185
8
0.189
0.194
0.199
0.205
0.210
8
0.216
0.222
0.228
0.235
0.242
8
0.250
0.258
0.266
0.276
0.287
8
0.298
0.312
0.328
0.363
0.416
8
0.500
0.584
0.638
0.673
0.689
8
0.702
0.714
0.725
0.734
0.743
8
0.751
0.758
0.766
0.772
0.779
8
0.785
0.790
0.796
0.801
0.806
8
0.811
0.816
0.821
0.825
0.829
8
0.834
0.838
0.842
0.845
0.849
8
0.853
0.857
0.860
0.864
0.867
8
0.870
0.874
0.877
0.880
0.883
8
0.886
0.889
0.892
0.895
0.898
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0.900
0.903
0.906
0.908
0.910
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0.911
0.913
0.915
0.917
0.919
8
0.920
0.922
0.924
0.925
0.927
8
0.929
0.930
0.932
0.933
0.935
8
0.936
0.938
0.939
0.941
0.942
8
0.944
0.945
0.946
0.948
0.949
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0.951
0.952
0.953
0.955
0.956
8
0.957
0.958
0.960
0.961
0.962
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8
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0.965
0.966
0.967
0.968
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**********************80-80 LIST OF INPUT DATA (CONTINUED)**********************
8
0.969
0.971
0.972
0.973
0.974
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0.978
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JOB NO. SHEET OF
Tighe&Bond CLIENT
s
Consulting Engineers SUBJECT t~C7aerWU C~ TU't31 +,,,nr Clk
I
Emdronmenta SpeciaE3t$ PREPARED BY V j~ DATE CHECKED BY DATE
PC-. 11 ~ " G~O~~ (~lC7et Jt'ilj c'_C(u&6, )
Z
l mil= (P- U,~ S> 1 = (-L inks
CN = (,L.%
S= Imo'
GN
✓ Cam, lcx~c~ _ ~U = 77
,12
(G,( t O'S (Y, 97))
C Gnl -
T'G = I.0bo (IQ
- 31, `l3
/G,-sS
Z11 in, ^i.Jly
i~
- Chapter 2: Estimating runoff
1~
I
SCS Runoff Curve I4umber method
The SCS Runoff Curve Number (CN) method is
i~
described in detail in NEH-4 (SCS 1985). The SCS
n
runoff equation is
~J
Q = (P - I.)? [Eq. 2-11
(P - Ia+S
where
Q = runoff (in),
P =rainfall (in),
S = potential maximum retention after runoff
begins (in), and
% = initial abstraction (in).
Initial abstraction (I0 is all losses before runoff
begins. It includes water retained in surface
depressions, water intercepted by vegetation,
evaporation, and infiltration. Ia is highly variable but
generally is correlated with soil and cover
parameters. Through studies of many small
11
agricultural watersheds, Ia was found to be
X
approximated by the following empirical equation:
Ia = 0.2S. [Eq. 2-21
By removing Ia as an independent parameter, this
I- approximation allows use of a combination of S and P
Ili to produce a unique runoff amount. Substituting
equation 2-2 into equation 2-1 gives
Q = (P - 02S)2 [Eq. 2.31
(P + 0.8S) '
S is related to the soon and cover conditions of the .
watershed through the CN. CN has a range of 0 to
100, and S is related to CN by
a]
i
~l
S = 1000 - 10. [Eq. 2-41
CN
Figure 2-1 and table 2-1 solve equations 2-3 and-2-4
for a range of CN's and rainfall.
Factors considered in determining
runoff curve numbers
The major factors that determine CN are the
hydrologic soil group (HSG), cover type, treatment,
hydrologic condition, -and antecedent runoff condition
(ARC). Another factor considered is whether
impervious areas outlet directly to the drainage
system (connected) or whether the flow spreads over
pervious areas before entering the drainage system
(unconnected). Figure 2-2 is provided to aid in
selecting the appropriate figure or table for
determining curve numbers.
CN's in table 2.2 (a to a) represent average
antecedent runoff condition for urban, cultivated
agricultural, other agricultural, and and and semiarid
rangeland uses. Table 2-2 assumes impervious areas
are directly connected. The following sections explain
how to determine CN's and.how to modify them for
urban conditions.
Hydrologic soil groups
Infiltration rates of soils vary widely and are affected
by subsurface permeability as well as surface intake
rates. Soils are classified into four HSG's (A, B, C.
and D) according to their minimum infiltration rate,
which is obtained for bare soil after prolonged
wetting. Appendix A defines the four groups and
provides a List of most of the soils in the United
States and their group classification. The soils in the
area of interest may be identified from a soon survey
report,.which can be obtained from local SCS offices
or soil and water conservation district offices.
Most urban areas are only partially covered by
impervious surfaces: the soil remains an important
factor in runoff estimates. Urbanization has a greater
effect on runoff in watersheds with soils having hien
infiltration rates (sands and gravels) than in
watersheds predominantly of silts and clays, which
generally have low infiltration rates.
Any disturbance of a soil profile can significantly
change its infiltration characteristics. With
urbanization, native soil profiles may be mined or
removed or fill material from other areas maybe
introduced. Therefore, a method based on soil
2-1
(210-VI-TR-55, Second Ed., June 1986)
t -r
Chapter 4: Graphical Peak Discharge method
This chapter presents the Graphical Peak Discharge
method for computing peak discharge from rural and
urban areas. The Graphical method was developed
from hydrograph analyses using TR-20, "Computer
Program for Project Formulation-Hydrology" (SCS
1983). The peak discharge equation used is
qp = quAmQFp [Eq. 4-1]
where
qp = peak discharge (cfs);
qu = unit peak discharge (csm/in);
Am = drainage area (mi');
Q = runoff (in); and
Fp = pond and swamp adjustment factor.
The input requirements for the Graphical method are
as follows: (1) T, (hr), (2) drainage area (mM, (3)
appropriate rainfall distribution (I, IA, II, or III), (4)
24-hour rainfall (in), and (5) CN. If pond and swamp
areas are spread throughout the watershed and are
not considered in the T, computation. an adjustment
for pond and swamp areas is also needed.
Peak discharge computation
For a selected rainfall frequency, the 24-hour rainfall
(P) is obtained from appendix E or more detailed
local precipitation mans. C\ and total runoff (Q) for
the watershed are computed accordincr to the
methods outlined in chapter 2. The CINT is used to
determine the initial abstraction (IJ from table 4-1.
Id/P is then computed.
If the computed I„/P ratio is outside the range shown
in exhibit 4 (4-I, 4-IA, 4-II, and 4-III) for the rainfall
distribution of interest, then the limiting value
should be used. If the ratio falls between the limiting
values, use linear interpolation. Figure 4-1 illustrates
the sensitivity of I;,/P to CN and P.
Peak discharge per square mile per inch of runoff
(clu) is obtained from exhibit 4-I, 4-IA, 4-11, or 4-III
by using T, (chapter 3), rainfall distribution type, and
I:JP ratio. The pond and su-amp adjustment factor is
obtained from table 4-2 (rounded to the nearest table
value). Use worksheet 4 in appendix D ,to aid in
computing the peak discharge using the Graphical
method.
1.0
.8
.6
Figure 4-1.-Variation of I„/Y for Y and CN.
Table 4-1.-I,, values for runoff curve numbers
Curve
I
Curve
i,
number
(in)
number
(in)
40
3.000
70
0.65-
41
-08-18
71
0.817
42
2.762
72
0.178
43
2.651
73
0.740
44
2.545
74
0.70 3
45
2.444
75
0.661
46
2.348
76
0.6::2
47
2..-5
7t
0.5117
48
167
78
0.564
41)
' 0,52
79
0.5::2
50
2.000
80
0.500
51
81
0.46.9
52
1.84G
82
0.439
53
1. 7 4
83
0.410
54
1.704
84
0.381
55
1.(i 6
85
0.3:]3
1.571
86
57
1.509
87
0:?'15i
58
1.448
t?~
0
55)
1.:3510
80
0-147
60
570
0
61
1-279
511
0.198
62
19116
92
0.174
(i3
1.175
51:3
0.151
64
1.125
514
0.125
65
1.07-1 1
95
0.105
(iii
1.0:30
96
0.0.1V)
67
0.985
517
0.0U-
68
0'1.11
578
0.041
69
0.891)
(210-VI-TR-55, Second Ed., June N86)
4-1
- r
0
I ] 5 ) 9 11 1] 15
Wnfall (P). Inches
.
-
-
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r _
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City of Northampton, Massachusetts
Office of Planning and Development
City Hall • 210 Main Street
Northampton, MA 01060 • (413) 586 -6950
FAX (413) 586 -3726
• Community and Economic Development
• Conservation • Historic Preservation
• Planning Board • Zoning Board of Appeals
• Northampton Parking Commission
Contact Person:
FITZGERALD LAKE MANAGEMENT PLAN
FITZGERALD LAKE CONSERVATION AREA
CONSERVATION COMMISSION
IN COOPERATION WITH THE BROAD BROOK COALITION, INC.
CITY OF NORTHAMPTON
Adopted by the Conservation Commission: January 13, 1997
Wayne Feiden
Office of Planning and Development
City of Northampton
City Hall, 210 Main Street
Northampton, MA 01060
(413) 586 -6950
ORIGINAL PRINTED ON RECYCLED PAPER
Location on Lake
Depth
Temperature
Oxygen
Secchi disk
pH 1
Narrowest point (east end)
1 meter
12.2° C
9.6 Mg /L
0.8 meters
7.0
Narrowest point (east end)
2.5 meters
12.0° C
10.2 Mg /L
- --
- --
Northern edge (hit bottom)
2.5 meters
10.7° C
7.3 Mg /L
0.8 meters
- --
Center (bend in lake)
1 meter
12.2° C
12.29 Mg /L
- --
- --
Center (bend in lake)
2.5 meters
12.2° C
10.13 Mg /L
- --
- --
West side (north of stream)
1 meter
12.1 ° C
9.82 Mg /L
0.5 meters
6.9
West (north of stream, hit
bottom)
2 meters
12.2 ° C
4 Mg /L
- --
- --
WATER ®TTAT,TTY DATA
Water quality data was collected on October 19, 1996. We dropped a dissolved
oxygen/temperature probe and a Secchi -disk from a kayak at various locations in the lake and
collected pH samples.
Given the shallow bottom at Fitzgerald Lake, it is unclear whether a thermocline develops in the
lake. On October 19, 1996, with surface temperatures dropping and strong wind, there was no
clear thermocline. As a result, with strong wind action, oxygen was relatively mixed throughout
the lake profile. Except the very bottom of the lake, where the probe was hitting the lake bottom,
oxygen levels were high.
RJOT,OGTCAT, RF,SOURC1 S
According to the Natural Heritage & Endangered Species Program, the only identified state -
listed rare species at Fitzgerald Lake is the Spotted Turtle (Clemmys guttata). The Spotted Turtle
considered a species of Special Concern under the Massachusetts Endangered Species Act.
Rediscovering Northampton: The Natural History of City -Owned Conservation Area by Laurie
Sanders (prepared for the Northampton Conservation Commission in December 1993 with DEM
Greenways and Wharton Trust funding) includes a partial inventory of plant and animal life in
the Fitzgerald Lake Conservation Area.
Cattails dominate the inlet cove and several other coves (Typha latifolia). A variety of other
aquatic plants exist in the lake, including three types of pondweed (Potamogeton amplifolius, P.
ephihdrys, P. foliosus), a diminutive bladderwort (Utricularia minor), a spatterdock lily (Nuphar
advena) and extensive patches of an uncommon water lily known as water shield (Brasenia
schreberi). At the edge of lake on the wettest muds are burreed (Sparganium androcladum),
arrowhead (Sagittaria latifolia), and grass -like plants (Eleocharis). There are also a variety of
Page 1
grasses, sedges and rushes.
Animals that spend a significant part of their life in the lake include pumpkinseeds (a fish), bass,
water snakes, green frogs, red - spotted newts and painted turtles. Two or three beaver lodges
support a healthy beaver population in the lake (with far more beaver found downstream in a
large wetland). Muskrat and otter have been reported in the lake, and a wide variety of upland
mammals visit the edge of the lake. Ducks and geese visit the lake in large numbers, especially
during fall and spring migrations.
MAPS
The maps at the end of this plan identify the Fitzgerald Lake and its watershed:
The first Fitzgerald Lake Watershed: Lake Management Plan map shows Fitzgerald Lake and
the entire watershed, with topography in five -foot contour intervals.
The second map, also titled Fitzgerald Lake Watershed: Lake Management Plan zooms in on the
lake and shows the lake and its surrounding wetlands. It shows the contours from a 1964 air
photo interpretation. These contours do not reflect a deeper channel that extends from the center
of the lake to the eastern edge of the lake where Broad Brook flowed before the lake was created.
A geographic information system analysis of this map shows that the lake is 41.6 acres and holds
approximately 245.5 acre feet of water (16.3 acres average 2.5 feet of water + 22.3 acres average
7.5 feet of water +3 acres average 12.5 feet of water= 10,693,980 cubic feet).
The third map is from the USDA's Soil Conservation Service's Soil Survey of Hampshire
County, Massachusetts, Central Part. It shows the soils surrounding the lake and throughout the
watershed.
The final map Fitzgerald Lake Watershed: Zoning and Landuse shows the zoning districts, sewer
lines, and buildings within the watershed, including buildings on properties abutting the lake and
its tributaries.
i,AKF, /WATF,RSHF,D HISTORY
Harold Fitzgerald created Fitzgerald Lake 1965 when he built a dam on the Broad Brook,
flooding 41 acres of the brook, marsh, wooded swamp and upland forest. Mr. Fitzgerald
originally built the dam to support his planned housing development, but he later bargain -sold
the 110 -acre property to the Northampton Conservation Commission for permanent protection as
a conservation area. The Conservation Commission has since acquired more property bringing
this conservation area to almost 500 acres, although only about 160 acres of the current
conservation area is is within the watershed of the lake.
Fitzgerald Lake Conservation Area includes all of the lake and its shore. There is a wheelchair -
accessible trail and boardwalk from a parking lot to the lake, but because the trail is 2/10 of a
Page 2
mile, large and heavy boats are not used on the lake. The lake is used for fishing, canoes and
other small boats, ice skating and skiing, and general passive enjoyment.
Slightly less than half the watershed is developed in urban uses, primarily single family homes.
The urban parts of the watershed includes a middle school, a recreation field, two cemeteries, and
part of a U.S. Veterans Administration Hospital. The remainder of the watershed is primarily
rural. Forest cover dominates, although there is some limited farmland and some suburban and
rural housing. The watershed is part of Hatfield's water supply (Zone III of their Roaring Gutter
well).
In the past ten years, there has been very little management of the lake itself. Lake access has
been developed with a boardwalk through a bordering marsh and into the lake. Trails have been
repaired to prevent erosion, and there has been some limited maintenance of the dam.
In the watershed, the most important management practice was the creation of a water supply
protection zoning overlay approximately six years ago. This overlay reduced the allowable
density of new housing developments by fifty percent.
LAKE PROBLEM AND CAUSES
The Conservation Commission and Broad Brook Coalition have identified the following as
possible problems at Fitzgerald Lake. Some of these problems are very well documented (e.g.
Fitzgerald Lake dam) others are areas of concern where more data is needed before we can
determine if there is a real problem (e.g. salt from road runoff).
Water Quality: Concerned about runoff from North Farms Road and urbanized areas within the
watershed including salt and heavy metals from road runoff, and nutrients from non -point source
pollution.
Plant Infestation: Concerned about eutrophication of the lake, especially from duckweed and
from invasive plants and animals that may be carried to the lake by boaters. The shallow
northwestern cove of the lake, by two of the three major inlets to the lake, appears to be slowly
filling in with sediment, but it also appears that the wetland in that inlet is successfully trapping
most of the nutrients and sediment entering the lake.
Algal Blooms: The lake has some algal growth, but does not yet have significant blooms.
Sediment and nutrients entering the lake from non -point sources certainly creates the risk of
significant blooms.
User Conflicts: User conflicts are relatively minimal (especially with the relocation of the
parking lot and access in 1996). Dirt bikes and ATV's on the dam are creating some erosion
problems on the dam. Before the relocation of the parking lot, vandalism at the parking lot was a
problem. We have some concern that, given the current design of the dam, vandals could
damage the dam outlet structure. In addition, in some areas, we have found shoreline erosion
problems from people walking along the edge of the lake.
Page 3
Lake Bottom Changes: Except for the eutrophication in the northwestern cove, there is no
evidence that the lake bottom is changing.
Changes in Fisheries: We do not have historical information to know if there have been
significant changes in fisheries. Again, nutrients entering the lake could change the fish
population of the lake.
Shallowness: Fitzgerald Lake has always been a shallow lake. The only area where this creates
any problems is in the northwest corner of the lake where a boardwalk provides access to the
lake.
Other: The most significant problem at Fitzgerald Lake is the integrity of the dam that created
the lake. The earthen dam is thirty -one years old and desperately needs capital improvements.
The City recently funded engineering work necessary for these repairs, but has been unable to
obtain funds to begin this work. We can either repair the dam in steps or all at once. The dam
needs an improved access road, repairs to the dam crest, removal of vegetation from the dam,
repairs to an outlet headwall, a relined outlet structure, and repairs to the emergency spillway. In
addition, until we repair the dam there is a greater risk that beavers could block the dam outlet
structure.
WATERSHED PROBT,EMS
Nonpoint Source Pollution Profile:
Stormwater from all surface roads, especially North Farm Road where it crosses Broad Brook.
Septic systems from the North Farms Road area.
Lawn chemicals and nutrients from throughout the watershed.
Farm run off from North Farms Road.
Possible cemetery chemical waste.
Possible waste and hazardous waste dumping.
Point Source Pollution Profile:
No known point sources in watershed.
LA iE ANI> WATERSHED MANAG. {E MEN _ GQALS (in ordero de reasing priority)
1. Preserve and enhance the diversity of habitats and species. Generally, encourage natural
succession, however, preserve and restore both the Fitzgerald Lake dam and existing
meadows and shrublands along the lake.
2. Maintain the integrity of aquatic and terrestrial habitats.
3. Encourage outreach to new users, conservation education, and ecological research.
4. Provide access for recreational users that are compatible with above goals, including
access to the lake.
Page 4
T,AKF AND WATERSHED MANAGEMENT ACTIONS
1. Secure steady stream of funding, including possible endowment, to insure long -term
management capabilities
2. Encourage educational campaign for people who live near or use the resource, so users
can understand and respect the resource.
3. Repair the Fitzgerald Lake dam to insure the lake and its ecosystem survive through the
next century.
4. Reduce road runoff and non -point source pollution to reduce sediment and nutrients
reaching the lake, especially runoff from North Farms Road by the Broad Brook.
5. Continue to acquire sensitive land abutting Fitzgerald Lake Conservation Area, in
accordance with the recommendations in Northampton's Open Space and Recreation
Plan.
6. Carefully examine user conflicts, especially those caused by motorized and to a lesser
extent no- motorized, vehicles within the conservation area.
7. Collect base data on in -lake water quality and especially on benthic organisms to allow us
to chart long -terms changes in the lake's condition.
C: I WFfileslWPfileslFitzgerald Lake Cons. Areallake management plan Janumy 14, 1997
Page 5