NOISE
Noise is unwanted sound. Traffic is the main source of noise in Larkspur. Noise measurements taken in 1982 found noise levels to be highest near major traffic generators and quietest at locations remote from major traffic sources.
An understanding of the location and sources of noise in Larkspur is important to land use and transportation policies, and therefore the land use and circulation sections of the General Plan. "Sensitive" land uses (housing, schools, hospitals) should be located away from high noise levels, or, if that's not practical, protected from them. Since traffic is the major noise generator, policies that will increase or decrease traffic will affect the noise environment of adjacent land uses. Noise is also a factor in open space planning because noise can adversely affect the enjoyment of quiet activities in those areas.
Noise measurements were made at nine locations throughout the City in July 1982. Measurements taken in three general areas since then (for Environmental Impact Reports prepared in 1987 and 1988 for Creekside and the Landmark Building) show no measurable change. (All measurements have a one or two decibel margin of error.) Besides showing actual noise levels in various locations, these measurements were used to validate noise contours developed for the City's major arterials. The noise contours were modeled (not actually measured) using information on average daily traffic, peak and off-peak travel speeds, distribution of traffic by hour of the day, and the percentage of trucks on a given street.
The noise contours are shown in terms of the day/night average noise level (Ldn), which is the measurement commonly used in Environmental Impact Reports.
Noise contours were also modeled for 1990 (with a notation that they would be accurate at least through 1995).
See Figure 7-8.
Figure 7-8
1995 Noise Exposure Contours
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The 1990-95 noise contours were based on projected future traffic, which is not significantly different from the future traffic projected under this General Plan in terms of how it affects the noise contours.
The locations of the contours do not take into account shielding provided by terrain, buildings, or intervening walls. The contours therefore represent "worst case" conditions. For example, the contours indicate a noise level of about 65 Ldn at Site 1 (Via la Cumbre), but the actual noise measurement was 56 Ldn. At this location, Highway 101 is depressed relative to the homes along Via la Cumbre, and the cut slope reduces the noise levels. The same phenomenon was demonstrated when noise measurements were taken for the Lincoln Terraces project. The noise measurement at the site closest to Highway 101 was lower than at others farther away because the location is shielded from traffic noise by the old quarry walls.
Exterior Noise Levels and Land Use Compatibility
Over the years many studies have been performed to determine how much noise is acceptable for different land uses. Figure 7-9, "Land Use Compatibility Standards," shows the noise levels that are acceptable for various land use categories. The chart indicates that a land use can be made compatible with a range of noise levels if the necessary noise reduction features are included in its design. This table helps planners in making preliminary determinations about the suitability of a proposed project located in an area where there is information about the noise environment (e.g., from noise contours or noise measurements).
California Noise Insulation Standards require preparation of an acoustical report for multiple-family dwellings proposed in areas where the Ldn exceeds 60 dBA. The report must show how the project will be designed to reduce the noise level to at least 45 dBA in habitable rooms. Typical buildings with their windows open provide an exterior-to-interior noise reduction of about 15 dB. In areas where the exterior noise level exceeds an Ldn of 60 dB, other noise reduction measures must be employed (see Construction Modifications on page 151). No standards have been established for acceptable outdoor areas in multiple-family developments, but State Noise Element Guidelines recommend 60 dB as the upper limit for acceptable levels.
Figure 7-9
Land Use Compatibility Standards
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Comparable State standards do not exist for commercial development. However, an interior noise level of 40 to 45 dB is generally considered acceptable for an office environment during working hours.
Besides traffic, other noise sources have been identified as common problems in Larkspur. Unmuffled or improperly muffled motor vehicles are some of the most annoying sources in any community. Not only are these vehicles annoying, they are illegal. Identification of unmuffled vehicles and/or vehicles with modified exhaust systems is easy, and it should be the routine procedure of the Police Department to cite all offenders.
Barking dogs, especially during the night, are particularly annoying. The Environmental Protection Agency has developed a training procedure which has been very successful in teaching dogs not to bark. It is included in Larkspur's 1982 Draft Noise Element as Appendix C.
The use of power tools can be controlled through a noise ordinance which, in part, restricts their use to certain hours of the day--8 AM to 10 PM during weekdays and 9 AM to 9 PM on weekends. A noise ordinance could also control amplified music, public address system, radios, and other electronic noise sources.
Early morning garbage pick-up can be a problem. The City should encourage the scavenger company to consider the purchase of quiet trucks when upgrading or expanding their fleet. Additionally, the City should review new projects to determine whether approval will result in earlier garbage pickups in existing neighborhoods.
Noise Goals, Policies, and Programs
Goal 11: Reduce the adverse effects of noise upon persons living or working in Larkspur.
Policy u: Ensure that all new living and work areas are developed with acceptable noise environments.
Action Program [38]: Maintain the following standards for noise levels in new residential developments.
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Indoor noise levels should not exceed 45 dBA.
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Outdoor noise levels should not exceed 55 dBA.
Noise can be reduced through site planning, architectural layout, noise barriers, and construction modifications.
Site Planning. By taking advantage of the natural shape and contours of the site, it is often possible to arrange buildings and other facilities to reduce and possibly eliminate noise impacts. Planned unit developments are particularly conducive to site planning techniques.
Architectural Layout. Bedrooms will be considerably quieter if placed on the side of the house facing away from a roadway. Similarly, balconies facing roadways should be avoided. Quiet outdoor spaces can be provided by creating a U-shaped development that faces away from the roadway.
Noise Barriers. Noise barriers must be massive enough to prevent significant noise transmission through them and high enough to shield the receiver from the noise source. While effective - because of their massiveness - noise walls are not appropriate in all locations. They work well along freeways and in larger developments. Access doors should be placed in the walls at regular intervals for use during emergencies.
Construction Modifications. In general, windows and doors are the acoustical "weak links" in a building. If other noise reduction measures are not sufficient, sealed windows on the noisy side of the building and an alternate means of ventilating the building may help. Beyond this, thicker window panes or double-glazed windows will be required. Doors should face away from the noise source. They should be solid-core and equipped with an appropriate acoustical door gasket.
Policy v: For non-residential projects, use the "Land Use Compatibility Standards," Figure 7-9, to evaluate their suitability in particular locations.
Action Program [39]: Require acoustical studies for all projects that would be exposed to noise levels in excess of those deemed normally acceptable, as defined in Figure 7-9.
Action Program [40]: Require thorough noise assessments in all environmental analyses of major projects.
Goal 12: Reduce noise levels in areas where the existing noise exceeds "normally acceptable" levels, to levels compatible with land uses in those areas, as defined in Figure 7-9, "Land Use Compatibility Standards."
Policy w: Promote educational efforts that will encourage the citizens of Larkspur to improve their noise environments.
Policy x: Control unnecessary, excessive, and annoying noises within the city, where not preempted by federal or State control.
Action Program [41]: Adopt a noise ordinance.
Policy y: Enforce applicable federal and State laws.
Action Program [42]: Enforce the provisions of the California Motor Vehicle Code pertaining to vehicle noise emission.
Policy z: Support programs to reduce community noise levels where possible within the "normally acceptable" categories shown in Figure 7-9.
Action Program [43]: Work with neighboring communities to ensure compliance with Larkspur's land use and noise compatibility standards at the city's boundaries.
Goal 13: Prevent the escalation of noise levels in areas where noise-sensitive uses exist.
Policy aa: Analyze in detail the potential noise impacts of any actions the City may take that could significantly alter noise levels in the community.
Action Program [44]: Review all public works projects for potential noise impact.
Action Program [45]: Consider noise emission when purchasing vehicles, construction equipment, etc. This consideration shall be balanced against the required performance and cost.
Policy ab: Encourage creative solutions when potential conflicts arise between noise levels and land use.