This section describes the required infrastructure improvements necessary to meet the demands of the preferred land use plan. As this project is a policy-level plan, it should be noted that the timing of all infrastructure improvements identified in this section represent the ultimate buildout conditions of the Route 66 Corridor specific plan.
A. Domestic Water System.
1. Domestic Water—Existing Conditions.
a. The city's water delivery system was created through the purchase of small private water companies and by the city's own expansion projects. As shown in Exhibit 4-16—Existing Domestic Water System, the system is comprised of eleven service zones containing approximately two hundred miles of pipe. The city receives water from two sources; groundwater pumping, and imported water obtained from the Metropolitan Water District of Southern California. Portions of the water supply system have been identified as requiring rehabilitation or replacement in the near-term. This is mainly due to reaches of pipe that are over fifty years old, or pipe diameters that do not meet city standards for providing current fire flow requirements.
b. The Route 66 Corridor specific plan area is located in the city's zone 1 and zone 2 service areas. The land use districts located in the zone 1 service area are: Barranca gateway, town center mixed use, Route 66 service commercial (portion), Grand Avenue gateway mixed use and central Route 66 residential. Zone 1 is the largest zone within the city's system, and varies in elevation from six hundred twenty feet above mean sea level (amsl) at Gladstone Street and Barranca Avenue to eight hundred ninety feet amsl at Ben Lomond north of Sierra Madre Avenue. The zone is served from a high water elevation of 969.5 feet amsl by five reservoirs. Refer to Exhibit 4-16—Existing Domestic Water System for identification of the existing zone 1 system within the Route 66 Corridor specific plan area.
c. The zone 2 service area is located to the east of zone 1. The development areas in the zone 2 service area are: Lone Hill Gateway and Glendora technology/commercial/office and the remaining portion of Route 66 service commercial. Zone 2 service elevations vary from eight hundred ten feet amsl at Alosta Avenue and the Big Dalton Wash to one thousand thirty feet amsl north of Oak Knoll Drive, with a high water level of one thousand ninety feet amsl. Four reservoirs provide head to the zone with locations at three different sites. The zone 2 system within the specific plan area is shown in Exhibit 4-16—Existing Domestic Water System.
d. The existing domestic water demand for the specific plan area was calculated using the current land use, and demand factors from the city's water master plan. Demands were calculated for each of the land use districts, based on a field survey identifying existing land uses by visual appearance, and information obtained in the city's geographic information system (GIS). Table 4-2—Water Demand Factors summarizes the water usage factors used for this study, as provided in Table V-3 of the city's WMP.
Table 4-2 Water Demand Factors |
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Land Use | Residential Water Demand Factor (gpd/du) | Non-Residential Water Demand Factor (gpd/ac) |
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Commercial | — | 2900 |
Single-Family | 600 | — |
Multifamily | 400 | — |
Mobilehome | 400 | — |
Motel | — | 2900 |
Medical | — | 4600 |
Religious | — | 2000 |
e. The existing average day water demand for the specific plan area is calculated in Table 4-2—Water Demand Factors to be 0.98 MGD. Using the max day factor of 1.85 from the WMP, the existing max day demand is estimated to be one thousand two hundred fifty-four gallons per minute (gpm).
f. Under the water master plan, several recommendations were made. The WMP determined several reaches of pipe within the study area to be either undersized for fire flow requirements or of such age that replacement was recommended. Most of the existing system currently remains the same as it was at the time of the writing of the WMP. In particular, the backbone to both the zones 1 and 2 systems is a parallel eight-inch loop running on each side of Route 66. These parallel lines were constructed in 1935—1936 and 1954. Therefore, the WMP (which set a fifty year lifespan) determined these pipelines require upgrading.
2. Proposed Domestic Water System Improvements.
a. A water demand analysis was performed for this study. Existing demands were estimated for the study area shown in Exhibit 4-17—Domestic Water System Improvements, as described above. Identical water usage factors (per Table V-3 of the city WMP as included in the appendix) were applied to the existing and proposed land uses for the specific plan area. Table 4-3—Estimated Domestic Water Demand summarizes the estimated demands and provides a side-by-side comparison. The average day demand for the proposed redeveloped area is 1.41 MGD. The max day demand for the proposed redevelopment area is one thousand eight hundred ten gpm.
b. The proposed system recommended should be planned to current operating standards, or as close to current standards as feasible. According to the city staff, the existing system was based upon an approximate one thousand two hundred fifty gpm fire flow for residential and small commercial land use, and two thousand five hundred for large commercial. The current fire flow standard is provided in the WMP for the city which states: two thousand two hundred fifty gpm for two hours for single-family residential, two thousand five hundred gpm for two hours for multifamily residential, one thousand seven hundred fifty gpm for two hours for mobilehome and five thousand gpm for five hours for large commercial. Eight inch lines under current fire flow standards are typically only sufficient for mobile home or single-family residential land uses. The WMP includes recommendations to replace the two eight-inch lines with a single eighteen-inch line to serve both sides of Route 66. However, the city has decided to continue maintaining a parallel system. The parallel pipeline layout facilitates service to each side of the street. Therefore, it is recommended that a fourteen-inch diameter pipe replace each eight-inch pipeline in order to provide the same capacity as the master-planned eighteen-inch.
c. Based on this analysis, the following is a list of recommended system improvements for adequate service to the Route 66 Corridor redevelopment project:
i. The zone 2 eight-inch diameter pipelines within Route 66 from Lorraine Avenue east to Amelia Avenue should be upsized to fourteen-inch or dual twelve-inch diameter pipelines to achieve the anticipated five thousand gpm fire flow requirements of the "Route 66 Commercial" land use district.
ii. Upsize the pipeline in Lorraine Avenue as proposed in the WMP (Improvement Project E-4) to a minimum of a sixteen-inch for the looped system within zone 1.
d. Exhibit 4-17—Domestic Water System Improvements, shows the changes recommended for the system. The proposed system upgrades described here will improve system capacity. However, computer modeling would be necessary to verify that current fire flow standards are met.
Table 4-3 |
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Estimated Domestic Water Demand |
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REFER TO SPECIFIC PLAN EIR |
B. Wastewater System.
1. Existing Wastewater System.
a. The portion of the city's wastewater system that will be used for the Route 66 Corridor redevelopment project is a gravity system that flows to the Los Angeles County Sanitation District 22 trunk sewer lines. The city's gravity sewers will collect the generated wastewater flows within the specific plan area. The general direction of the wastewater flow is east to west. The Lorraine Avenue Trunk and Baseline Road Trunk sewers convey the flows from the existing land uses within the study area to the main Los Angeles County Sanitation trunk tie-in at the intersection of Barranca Avenue and Baseline Road. Exhibit 4-18—Wastewater System shows alignments and diameters of the existing sewers within the study area.
b. In the absence of city standards, typical industry-standard water-to-wastewater "return" ratios were used for estimating wastewater flows. The return ratio figures are derived from standards of similar water agencies within Southern California, as shown in Table 4-4—Water Demand/Wastewater Generation Factors.
Table 4-4 Water Demand/Wastewater Generation Factors |
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Land use | Return Ratio (%) | Residential Water Demand Factor (gpd/du) | Wastewater Generation Factor (gpd/ac) | Non-Residential Water Demand Factor (gpd/ac) | Wastewater Generation Factor (gpd/ac) |
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Commercial | 85 | — | — | 2900 | 2465 |
Single-Family | 50 | 600 | 300 | — | — |
Multifamily | 75 | 400 | 300 | — | — |
Mobilehome | 75 | 400 | 300 | — | — |
Motel | 80 | — | — | 2900 | 2320 |
Medical | 100 | — | — | 4600 | 4600 |
Religious | 80 | — | — | 2000 | 1600 |
c. The proposed redevelopment will increase the flow to the sewers serving the specific plan area. Redevelopment within the specific plan area consists of various land uses. The two thousand nine hundred gpd/ac demand factor was used for the study for all commercial areas as a conservative assumption.
d. Consultation with Los Angeles County Sanitation District No. 22 and the city has indicated that the current sewer system should have sufficient capacity for the additional flows. Table 4-5—Estimated Wastewater Generation provides an analysis of the system by estimating the flows by land use district (location).
Table 4-5 |
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Estimated Wastewater Generation |
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REFER TO SPECIFIC PLAN EIR |
e. Differences between "existing" and "proposed" at intermediate points within the study area. The existing average flow for the study area is calculated as 0.79 MGD. All of the defined land use districts are estimated to increase wastewater flow to some degree. Table 4-6—Estimated Flow Increases, summarizes estimated flow increase percentages at selected intermediate locations.
Table 4-6 Estimated Flow Increases |
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# | Location of Sewer | Sewer Diameter (inches) | Estimated Percent of Flow Increase (%) |
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1 | Elwood and Route 66 | 12 | 48 |
2 | East end of Mauna Loa Avenue | 15 | 49 |
3 | Glendora and Route 66 | 10 | 23 |
4 | Baseline and Glendora | 15 | 48 |
5 | Grand Avenue and Route 66 | 15 | 33 |
6 | Baseline and Grand Avenue | 18 | 39 |
7 | Barranca and Baseline | 18 | 34 |
f. Table 4-7—Capacity by Pipe Diameter, was developed using the Flowmaster software by Haestad Methods to determine the capacity of different diameter pipes resulted in the following values:
Table 4-7 Capacity by Pipe Diameter |
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Pipe Diameter (inches) | Minimum Slope (ft/ft)* | Full Capacity (gpm) |
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8 | 0.0033 | 300 |
10 | 0.0024 | 500 |
12 | 0.0018 | 700 |
15 | 0.0012 | 1300 |
18 | 0.0012 | 2000 |
Note: |
* | commonly used industry minimum slopes. |
g. Based upon correspondence with the Los Angeles County Sanitation District, the Baseline Avenue trunk sewer is currently being monitored. It is estimated that the flows from the Route 66 Corridor study area will increase by approximately thirty-four percent from existing flows as discussed in the following section, and shown in Exhibit 4-18—Wastewater System and Table 4-5—Estimated Wastewater Generation.
2. Proposed Wastewater System Improvements. A wastewater flow analysis was performed for this study and existing wastewater generation figures were estimated. Identical wastewater flow factors (per Table V-3 of the city WMP with return ratios) were applied to the existing and proposed land uses for the specific plan area. Table 4-5—Estimated Wastewater Generation, summarizes the estimated flows and provides a side-by-side comparison. The average flow for the proposed redeveloped area is 1.06 MGD. The peak wastewater estimated for the Route 66 Corridor redevelopment project is one thousand four hundred seventy gpm. The existing trunk sewers within the collection system evaluated for the redevelopment project may or may not require upsizing or realigning. Monitoring at key locations during development would indicate whether this is necessary, as discussed below.
3. Wastewater System Recommendations. Analysis of the existing wastewater collection system and proposed flow increase indicates there is adequate facilities to serve the redevelopment project, it is recommend flow monitors be installed at key locations. Based on this analysis, RBF Consulting recommends the seven sewer locations within the study area, and described in Table 4-5—Estimated Wastewater Generation, should undergo extended-period flow monitoring at the seventy-five-, and ninety-five-percent build-out to ensure the collection system is operating with adequate excess capacity, for build-out conditions.
C. Storm Drainage System.
1. Storm Drain System Existing Conditions.
a. The Route 66 Corridor specific plan project area provides a number of storm drain systems collecting surface runoff and providing conveyance to the main flood control channel in the area, the Big Dalton Wash. Existing storm drain facilities are indicated on Exhibit 4-19—Existing Storm Drain System.
b. A majority of the catch basins on Route 66 drain to mainlines in streets that cross under the roadway. Most of these catch basins and laterals on the north side Route 66. The runoff from the south portion of Route 66 typically flows in the gutter to the streets that intersect Route 66. At these locations, the runoff turns the corner and continues in the cross streets to one of the major flood control channels in the area or is picked up in catch basins on the cross streets. The streets providing storm drain mainlines include:
ix. Route 66, east of Lone Hill Avenue.
c. The Big Dalton Wash, the East Branch of the Big Dalton Wash, and the Alosta Avenue Drain all cross Route 66 within the city limits of the city.
d. The following section provides as summary of Exhibit 4-19—Existing Storm Drain System, including a detailed description of the storm drain mainlines in each of the cross streets as well as some of their catch basin laterals.
i. Barranca Ave. The storm drain mainline in Barranca Ave north of Route 66 is a thirty-six-inch RCP. South of Route 66, the mainline is a forty-two-inch RCP. This mainline has numerous laterals connected to it, which pick up surface flow on Barranca Ave and one twenty-four-inch RCP that drains Route 66 on the northeast corner of the intersection. These laterals range in size from fifteen inches to twenty-four inches.
ii. Vecino Drive/Forestdale Avenue. The storm drain mainline in Vecino Drive south of Route 66 is thirty-nine-inch RCP. The mainline in Route 66 between Vecino Drive and Forestdale Avenue is thirty-six-inch RCP. The mainline in Forestdale Avenue north of Route 66 is also thirty-six-inch RCP. Several laterals collect surface runoff in Forestdale Avenue, ranging from fifteen-inch RCP to twenty-seven-inch RCP. There are two laterals that collect surface runoff from Route 66. A twenty-four inch RCP lateral drains the north side of Route 66, east of Forestdale Avenue. A twenty-seven inch RCP lateral drains the south side of Route 66, east of Vecino Drive.
iii. Grand Avenue. The storm drain mainline in Grand Avenue between Ada Avenue and Heber Street is twenty-seven-inch RCP. The mainline between Heber Street and Leeside Street is thirty-inch RCP. The mainline between Leeside Street and Route 66 is thirty-six-inch RCP. The mainline in Grand Avenue south of Route 66 is forty-five-inch RCP. There are numerous eighteen-inch RCP laterals that pick up surface runoff from Grand Avenue and the streets draining toward Grand, north of Route 66. There is also a twenty-one-inch RCP lateral that collects runoff from the north side of Route 66, east of Grand Avenue.
iv. Glendora Avenue. The storm drain mainline in Glendora Avenue is thirty-three-inch RCP between Colorado Avenue and Route 66, as well as north of Route 66 to Lemon Avenue. There are several laterals that collect runoff on Glendora Avenue north of Route 66, that range in size from twenty-one-inch to twenty-four-inch RCP. There is also a twenty-one-inch RCP lateral that drains the north side of Route 66, east of Glendora Avenue.
v. Pasadena Avenue. The storm drain mainline in Pasadena Avenue south of Route 66 is fifty-four-inch RCP. There is approximately a two hundred ten-foot stretch of the mainline just north of Route 66 that is forty-five-inch RCP. However, north of the stretch, the mainline increases to forty-eight-inch RCP. There are several laterals collecting runoff from Pasadena Avenue, ranging in size from eighteen inches to twenty-one-inch RCP. There are two laterals collecting runoff on Route 66. There are two catch basins to intercept surface flow on the north side of Route 66, east of Pasadena Avenue that are connected with a twenty-four-inch RCP lateral. There is also an eighteen-inch RCP lateral collecting runoff on the south side of Route 66, east of Pasadena Avenue.
vi. Glenwood Avenue. The storm drain mainline in Glenwood Avenue is forty-five-inch RCP between its outlet at the Big Dalton Wash and Route 66, as well as north of Route 66. There is a fifteen-inch RCP lateral draining the west side of Glenwood Avenue just north of Route 66, and another fifteen-inch RCP lateral collecting surface runoff from the north side of Route 66, east of Glenwood Avenue.
vii. Loraine Avenue. The storm drain mainline in Loraine Avenue is sixty-inch RCP between its outlet at the Big Dalton Wash and Route 66, as well as north of Route 66. There is an eighteen-inch RCP lateral collecting flow from the east side of Loraine Avenue, north of Route 66. There is also an eighteen-inch RCP lateral collecting runoff from the north side of Route 66, east of Loraine Avenue.
viii. Big Dalton Wash. Both the Big Dalton Wash and the East Branch of the Big Dalton Wash cross Route 66. However, neither of these major flood control channels directly intercepts runoff from Alosta Avenue (Route 66). The East Branch of the Big Dalton Wash travels from east to west to its termination at the Big Dalton Wash near the intersection of Loraine Avenue and Route 66. The Big Dalton Wash travels from the northeast to the southwest through the city. A majority of the storm drain mainlines in the area drain to one of these two flood control channels.
ix. Alosta Avenue Drain. A majority of the Alosta Avenue Drain is a sixty-six-inch RCP. However, near its outlet into the East Branch of the Big Dalton Wash, the mainline was increased to an eighty-four-inch RCP. Tying into this larger section of the mainline, there are three laterals that collect surface runoff from Route 66. A twenty-one-inch RCP lateral collects runoff from the south side of the highway, and an eighteen-inch RCP along with a twenty-one-inch RCP lateral collect runoff from the north side of the highway.
x. Route 66. There is a storm drain mainline that goes from the East Branch of the Big Dalton Wash, where the wash goes under Lone Hill Avenue, to Glengrove Avenue, which is a thirty-three-inch RCP. This mainline continues approximately six hundred fifty-feet east of Glengrove Avenue in Route 66. But, the pipe is reduced in size to a thirty-inch RCP. There are several small laterals that tie into this mainline at the intersection of Route 66 and Glengrove Avenue. There is an eighteen-inch RCP lateral that collects surface flows from the southeast corner of Route 66 and Glengrove Avenue, this lateral also collects runoff from the north side of Route 66, east of Financial Way on its way to the mainline.
There is also an additional twenty-one-inch RCP lateral that drains the north side of Route 66, east of Financial Way. At the upstream termination of this mainline, there are several eighteen inches laterals that collect surface runoff from the south side of State Route 66. |
e. The location and size of all existing mainlines and laterals are shown on Exhibit 4-19—Existing Storm Drain System. The capacity as well as the physical characteristics of the main lines are provided in Table 4-8—Storm Drain Mainline Characteristics. The corresponding Mainline Pipe Numbers are shown on Exhibit 4-19.
2. Storm Drain System Identified Deficiencies.
a. The city has observed two areas within the project area that currently experience flooding in large storm events. This localized flooding occurs approximately two to three times yearly. One of the two locations where flooding occurs within the project is located on the north side of Route 66 between Vermont Avenue and Grand Avenue. At this location, runoff flows south on Vermont and is never picked up in a catch basin lateral. It then ponds up at the intersection of Vermont and Route 66 and begins to flow west on Route 66. The runoff does not get into the storm drain network until the intersection of Grand Avenue and Route 66. In that area, the flow in the street overtops the eight-inch curb and creates localized flooding.
b. The other location where localized flooding occurs is on Route 66 near the intersection of Elwood Avenue. There are several catch basins on Route 66, but they do not connect to a storm drain network, nor are there any storm drain plans for these facilities. They have a very shallow slope and move water from Route 66 to the southern portion of Elwood Avenue where the runoff is discharged back into the street. The runoff then flows south in Elwood Avenue to the Big Dalton Wash.
Table 4-8 Storm Drain Mainline Characteristics |
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Mainline Pipe # | Location | Size | Slope | Capacity* (cfs) | Material | Installation Date |
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1 | Barranca Ave.—Orangepath St. to SR 66 | 36″ | 0.0064 | 53 | RCP | 1969 |
2 | Barranca Ave.—SR 66 to Bagnall St. | 42″ | 0.0041 | 64 | RCP | 1969 |
3 | Forestdale Ave.—North of SR 66 | 36″ | 0.0023 | 32 | RCP | 1968 |
4 | SR 66—Between Forestdale Ave. and Vecino Dr. | 36″ | 0.0048 | 46 | RCP | 1968 |
5 | Vecino Dr.—South of SR 66 | 39″ | 0.0010 | 26 | RCP | 1968 |
6 | Grand Ave.—Ada Ave. to Heber St. | 27″ | 0.0099 | 30 | RCP | 1965 |
7 | Grand Ave.—Heber St. to Leeside St. | 30″ | 0.0103 | 41 | RCP | 1965 |
8 | Grand Ave.—Leeside St. to SR 66 | 36″ | 0.0082 | 60 | RCP | 1965 |
9 | Grand Ave.—South of SR 66 | 45″ | 0.0100 ** | 121 | RCP | 1965 |
10 | Glendora Ave.—North of SR 66 | 33″ | 0.0100 | 53 | RCP | - |
11 | Glendora Ave.—South of SR 66 | 33″ | 0.0141 | 63 | RCP | 1960 |
12 | Pasadena Ave.—North of 45″ Stretch | 48″ | 0.0053 | 104 | RCP | - |
13 | Pasadena Ave.—45″ Stretch just North of SR 66 | 45″ | 0.0446 | 255 | RCP | - |
14 | Pasadena Ave.—South of SR 66 | 54″ | 0.0058 | 150 | RCP | - |
15 | Glenwood Ave.—North of SR 66 | 45″ | 0.0269 | 198 | RCP | 1960 |
16 | Glenwood Ave.—South of SR 66 | 45″ | 0.0232 | 184 | RCP | 1960 |
17 | Loraine Ave.—North of SR 66 | 60″ | 0.0408 | 526 | RCP | 1969 |
18 | Loraine Ave.—South of SR 66 | 60″ | 0.0264 | 423 | RCP | 1969 |
19 | Alosta Avenue Drain—66″ | 66″ | 0.0330 | 610 | RCP | 1993 |
20 | Alosta Avenue Drain—84″ | 84″ | 0.0052 | 460 | RCP | 1993 |
21 | Alosta Ave.—Between Lone Hill Ave and Glengrove Ave. | 33″ | 0.0100** | 53 | RCP | 1980 |
22 | Alosta Ave.—East of Glengrove Ave. | 30″ | 0.0188 | 56 | RCP | - |
Notes: |
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* | All capacities are based on the assumption that the pipes are flowing just full. No pressure flow was taken into consideration. |
** | Assumed slope. |
c. This system has shown historic evidence of surcharge on Route 66 because it does not have the needed head to push a large amount of water through the shallow box culvert.
3. Storm Drain System Improvements. Several alternatives for alleviating the localized flooding at the two identified problem locations have been developed. There are estimated sizes and costs associated with these possible solutions. However, a detailed hydrology study should be preformed to determine the required size of storm drain mainlines, laterals, and catch basins. If connection to an existing mainline is proposed, a hydraulic study should also be preformed to determine whether or not additional flows can be added to existing storm drain mainlines.
a. Route 66/Vermont Avenue Improvements. As shown on Exhibit 4-20—Storm Drain System Improvements. There are two possible options for alleviating the localized flooding on Route 66 between Grand Avenue and Vermont Avenue. Both of the alternatives would involve trenching in existing pavement and laying a new storm drain line with laterals and catch basins from the mainline in Grand Avenue to Vermont Avenue. All of the runoff from Vermont eventually gets into the Grand Avenue mainline so these possible new lines will not be changing the existing drainage patterns in the area.
i. Route 66/Vermont Option 1. The first alternative would be to run approximately one thousand seven hundred feet of thirty-inch RCP east in Route 66 from the mainline in Grand Avenue to the intersection of Route 66 and Vermont Avenue. A catch basin and lateral on either side of Vermont Avenue just north of the intersection will help alleviate the flooding on Route 66.
ii. Route 66/Vermont Option 2. Some of the runoff that attributes to the flooding on Route 66 comes from farther north in the city. The second alternative would be to run approximately one thousand seven hundred feet of twenty-four-inch RCP east in Ada Avenue from the mainline in Grand Avenue to the intersection of Ada Avenue and Vermont Avenue. A catch basin and lateral on either side of Vermont Avenue just south of the intersection will remove some of the surface water before it becomes a problem. However, there will still be a large area draining to the impacted area on Route 66, so this may not totally alleviate flooding in the area.
b. Route 66/Elwood Avenue Improvements. As shown in Exhibit 4-20—Storm Drain System Improvements. There are two possible options for alleviating the localized flooding at the intersection of Elwood Avenue and Route 66. Both of the alternatives would involve trenching in existing pavement and laying a new storm drain line with laterals and catch basins.
i. Route 66/Elwood Option 1. The runoff that is causing flooding at the intersection of Elwood Avenue and Route 66, eventually sheet flows south in Elwood Ave to the Big Dalton Wash. The first alternative to alleviate the flooding at the intersection would be to construct approximately six hundred feet of thirty-inch RCP storm drain in Elwood Avenue from the Big Dalton Wash to the intersection. The existing curb inlets would need to be replaced with catch basins and laterals to the proposed mainline in Elwood. The construction cost, including pavement removal and replacement, trenching, pipe, traffic control, and catch basins will be around one hundred fifty thousand dollars.
ii. Route 66/Elwood Option 2. The second alternative would be to connect to the storm drain mainline in Glenwood Avenue. However, since the runoff causing localized flooding at the intersection of Elwood Avenue and Route 66 does not get into that mainline in the existing condition, a hydraulic analysis of the mainline in Glenwood will need to be done to verify its capacity. This alternative would include approximately seven hundred feet of thirty-inch RCP storm drain in Route 66 from the mainline in Glenwood Avenue to the intersection. The existing curb inlets would need to be replaced with catch basins and laterals to the proposed line in Route 66.
(Ord. 2019 § 2, 2017)