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Rainfall parameters for hydrologic modeling shall be derived from the ADOT Hydrology Manual. Rainfall intensity estimates for use with the Rational Method shall be taken from the appropriate charts on the NOAA ATLAS 14 web site. Point precipitation values for hydrologic modeling shall be taken from the appropriate charts on the NOAA Atlas 14 web site.
(Res. 1637, passed 2-28-02; Am. Res. 2871, passed 9-17-15; Am. Ord. 872, passed 9-17-15)
(A) General. Rainfall losses are to be estimated in accordance with the procedures in the ADOT Hydrology Manual. The Green & Ampt infiltration method is to be used with the Clark Unit Hydrograph Method.
(B) Determination of soil texture. The rainfall loss characteristics of soils for undeveloped land within the town and the contributing watersheds have been prepared as a part of the PDMP. The results are summarized in Table 3.2. A soils map and report for the Town of Payson is available from the Engineering Department. This information is to be used for all unit hydrograph models prepared for studies within the town. The engineer may use more detailed information specific to a site with written approval of the Public Works Department.
(Res. 1637, passed 2-28-02; Am. Res. 2871, passed 9-17-15; Am. Ord. 872, passed 9-17-15)
Soil Class (1) | Hydrologic Soil Group (HSG) (2) | Bare Ground XKSAT In/hr (3) | Natural |
Soil Class (1) | Hydrologic Soil Group (HSG) (2) | Bare Ground XKSAT In/hr (3) | Natural | ||
RTIMP % (4) | Veg. Cover % (5) | IA In (6) | |||
1A | D | 0.04 | 0 | 90 | 0.25 |
2A | C | 0.25 | 0 | 90 | 0.25 |
3A | C | 0.40 | 0 | 80 | 0.25 |
4A | C | 0.40 | 0 | 75 | 0.25 |
4B | C | 0.40 | 0 | 75 | 0.25 |
4C | C | 0.40 | 0 | 75 | 0.25 |
5A | C | 0.25 | 0 | 75 | 0.25 |
5B | D | 0.06 | 5 | 75 | 0.25 |
6A | D | 0.04 | 0 | 85 | 0.25 |
6B | D | 0.04 | 0 | 75 | 0.25 |
6C | D | 0.06 | 20 | 85 | 0.25 |
7A | C | 0.40 | 50 | 25 | 0.25 |
7B | C | 0.40 | 30 | 10 | 0.25 |
73 | C | 0.40 | 0 | 80 | 0.25 |
3730 | C | 0.40 | 5 | 62 | 0.25 |
3731 | C | 0.40 | 5 | 62 | 0.25 |
3753 | C | 0.40 | 20 | 62 | 0.25 |
3821 | C | 0.40 | 0 | 62 | 0.25 |
4140 | D | 0.06 | 0 | 45 | 0.25 |
4170 | D | 0.06 | 0 | 51 | 0.25 |
4175 | C | 0.40 | 15 | 76 | 0.25 |
4240 | C | 0.40 | 5 | 78 | 0.25 |
4241 | C | 0.40 | 10 | 80 | 0.25 |
4242 | C | 0.40 | 10 | 82 | 0.25 |
4457 | C | 0.40 | 15 | 75 | 0.25 |
4468 | C | 0.40 | 10 | 47 | 0.25 |
4469 | C | 0.40 | 10 | 47 | 0.25 |
5350 | C | 0.40 | 0 | 83 | 0.25 |
5351 | C | 0.40 | 0 | 83 | 0.25 |
5352 | C | 0.40 | 15 | 83 | 0.25 |
(Res. 1637, passed 2-28-02)
The rainfall loss characteristics of future condition developed land within the town and the contributing watersheds have been prepared as a part of the PDMP. The results are summarized in Tables 3.3 and 3.4. This information is to be used for all existing and proposed condition unit hydrograph models prepared for studies within the town. The engineer may use more detailed information specific to a site with written approval of the Public Works Engineer. Land-use rainfall loss characteristics for developed land for use with the Rational Method ("C" coefficients) are to be derived from Table 3.5.
(Res. 1637, passed 2-28-02)
Land-Use Class (1) | Developed |
Land-Use Class (1) | Developed | ||
RTIMP % (2) | Veg. Cover % (3) | IA In (4) | |
VLDR | 20 | 50 | 0.20 |
LDR | 25 | 45 | 0.20 |
MDR | 45 | 25 | 0.20 |
MFR | 65 | 20 | 0.20 |
C | 90 | 5 | 0.05 |
GC | 0 | 98 | 0.20 |
GC/N | 2 | 85 | 0.20 |
P | 100 | 0 | 0.05 |
RW | 75 | 12 | 0.08 |
N | --- | --- | --- |
NC | --- | --- | --- |
L | 100 | 0 | 0.00 |
LDR1 | 51 | 29 | 0.16 |
LDR3 | 58 | 25 | 0.13 |
LDR5 | 45 | 33 | 0.15 |
S | 45 | 52 | 0.13 |
RES | 45 | 33 | 0.15 |
REDI | 55 | 21 | 0.18 |
REDH | 57 | 26 | 0.16 |
REDF | 60 | 28 | 0.14 |
(Res. 1637, passed 2-28-02)
Land-Use Class (1) | Description (2) |
Land-Use Class (1) | Description (2) |
VLDR | Very Low Density Residential |
LDR | Light Density Residential |
MDR | Medium Density Residential |
MFR | Multi-Family Residential |
C | Commercial |
GC | Golf Course/Park |
GC/N | Golf Course - Not Designed |
P | Paving |
RW | Street Right-of-Way |
N | Natural (see soils parameters) |
NC | Non-Contributing |
L | Lake; contributing drainage area |
LDR1 | Low Density PAD #1 |
LDR3 | Low Density PAD #3 |
LDR5 | Low Density PAD #5, #6, #7 |
S | School/Resort |
RES | Reservation |
REDI | Redevelopment Area in Sub-basin 120I |
REDH | Redevelopment Area in Sub-basin 121H |
REDF | Redevelopment Area in Sub-basin 121F |
(Res. 1637, passed 2-28-02)
Land Uses | Return Period |
Land Uses | Return Period | |||
2-10 Year | 25 Year | 50 Year | 100 Year | |
Streets and Roads | ||||
Paved Roads | 0.75 - 0.85 | 0.83 - 0.94 | 0.90 - 0.95 | 0.94 - 0.95 |
Gravel Road- ways and Shoulders | 0.60 - 0.70 | 0.66 - 0.77 | 0.72 - 0.84 | 0.75 - 0.88 |
Industrial Areas | ||||
Heavy | 0.70 - 0.80 | 0.77 - 0.88 | 0.84 - 0.95 | 0.88 - 0.95 |
Light | 0.60 - 0.70 | 0.66 - 0.77 | 0.72 - 0.84 | 0.75 - 0.88 |
Business Areas | ||||
Commercial - Downtown | 0.75 - 0.85 | 0.83 - 0.94 | 0.90 - 0.95 | 0.95 |
Commercial - Neighborhood | 0.55 - 0.65 | 0.61 - 0.72 | 0.66 - 0.78 | 0.69 - 0.81 |
Residential Areas | ||||
Lawns - Flat | 0.10 - 0.25 | 0.11 - 0.28 | 0.12 - 0.30 | 0.13 - 0.31 |
Lawns - Steep | 0.25 - 0.40 | 0.28 - 0.44 | 0.30 - 0.48 | 0.31 - 0.50 |
Very Low Density Residential | 0.30 - 0.40 | 0.33 - 0.44 | 0.36 - 0.48 | 0.38 - 0.50 |
Low Density Residential | 0.45 - 0.55 | 0.50 - 0.61 | 0.54 - 0.66 | 0.56 - 0.69 |
Medium Density Residential | 0.50 - 0.60 | 0.55 - 0.66 | 0.60 - 0.72 | 0.63 - 0.75 |
Multi-Family Residential | 0.60 - 0.70 | 0.66 - 0.77 | 0.72 - 0.84 | 0.75 - 0.88 |
Parks/Cemeteries | 0.10 - 0.25 | 0.11 - 0.28 | 0.12 - 0.30 | 0.13 - 0.31 |
Playgrounds | 0.40 - 0.50 | 0.44 - 0.55 | 0.48 - 0.60 | 0.50 - 0.63 |
Note: Values of C for the 25-, 50- and 100-year frequencies were derived using frequency adjustment factors of 1.10, 1.20, and 1.25, respectively, with an upper limit of 0.95 for C for the 2- through 10-year values.
(Res. 1637, passed 2-28-02)
(A) Application for peak discharge and runoff volume estimation. The Rational Method may be utilized for computing peak runoff from small watersheds for the purpose of designing drainage conveyance facilities and storm water detention/retention basins. The Rational Method should be applied within the following limitations:
(1) The drainage area should not exceed 160 acres.
(2) The minimum time of concentration (Tc) is 5 minutes. The maximum Tc should not exceed 60 minutes.
(3) The watershed should be homogenous (i.e. the watershed should not consist of two or more land-uses of significantly different character). Lack of basin homogeneity can lead to errors in estimates of Tc and runoff coefficient “C”.
(4) The watershed should not contain storm water facilities that require routing and combination of hydrographs.
(B) Watersheds that do not meet the criteria in division (A) of this section should be modeled using the Clark Unit Hydrograph method.
(C) A number of variations of the Rational Method are currently in use by communities throughout the Southwestern United States. These methods vary mostly in the method used to compute the time of concentration, Tc. It is required that the Rational Method presented within Chapter 2 of the ADOT Hydrology Manual be utilized for hydrologic analysis within the town. This methodology was developed for use within Arizona, and the manual is readily available. Other Rational Methods may also be acceptable, but must be approved in writing by the Public Works Engineer prior to use. Refer to § 152.34 for the Payson Intensity-Duration-Frequency (I-D-F) for use with the Rational Method.
(D) Estimation of runoff coefficient, “C”. The runoff coefficient, “C”, for undeveloped watersheds shall be estimated using Figures 3.2 and 3.3. The hydrologic soil group (HSG) and an estimate of vegetation cover density for the area of concern can be obtained using Table 3.2 in combination with the town soils map. “C” values for developed land uses shall be obtained from Table 3.5.
(Res. 1637, passed 2-28-02)

Rational "C" Coefficient, Mountain, Juniper and Grass
As a function of Rainfall Depth, Hydrologic Scil Group (HSG), and % of Vegetation Cover (From ADOT Hydrology Manual Figure 2-7)
As a function of Rainfall Depth, Hydrologic Scil Group (HSG), and % of Vegetation Cover (From ADOT Hydrology Manual Figure 2-7)

Rational "C" Coefficient, Mountain, Ponderosa Pine
As a function of Rainfall Depth, Hydrologic Soil Group (HSG), and % of Vegetation Cover (From ADOT Hydrology Manual Figure 2-8)
As a function of Rainfall Depth, Hydrologic Soil Group (HSG), and % of Vegetation Cover (From ADOT Hydrology Manual Figure 2-8)
The Clark Unit Hydrograph Method shall be used in conjunction with HEC-1 for all watersheds greater than or equal to 160 acres, for design of detention basins; and where hydrograph channel or storage routing and combination is necessary. The Clark Unit Hydrograph method shall be applied in conformance with the procedures set forth in the ADOT Hydrology Manual.
(Res. 1637, passed 2-28-02)
(A) Channel routing. Hydrograph channel routing shall be done using the Muskingum-Cunge method using the procedures described in the ADOT Hydrology Manual. Routing reaches shall be subdivided appropriately when the average characteristics of a routing reach cannot be simulated using a single cross section. The number of computation steps for each reach must be optimized so that the number of steps input matches the number of steps calculated using the reach travel time computed by HEC- HMS. The kinematic wave method, or other approved method, may be used for routing hydrographs through storm drains or other prismatic sections where hydrograph attenuation is not expected. Other hydrograph channel routing methods may be used if appropriate for the situation and with prior written approval of the Public Works Department.
(B) Storage routing. All hydrograph storage routing shall be done using the Modified Puls Method as implemented in HEC-1. The operation shall be controlled using an input stage-storage discharge curve. The low-level outlet HEC-1 option shall not be used. The engineer shall document the hydraulic calculations performed to generate the stage-discharge relationship. Hydrograph storage routing shall be performed where hydrograph attenuation is significant due to ponding and storage. This example of hydrograph attenuation could be upstream of a street crossing, through a lake, or for detention basins.
(Res. 1637, passed 2-28-02; Am. Res. 2871, passed 9-17-15; Am. Ord. 872, passed 9-17-15)
FLOODPLAIN DELINEATION
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