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1984.03.14 PC Minutes
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1984.03.14 PC Minutes
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Commissions
Meeting Date
3/14/1984
Document Type
Minutes
Commission Name
Planning
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Qz <br />types of Carriers are suited for all cli- <br />mates, and local conditions may cause <br />significant differences in the mainte- <br />nance cost of the various barrier types. <br />The cost questions must be evaluated on <br />a local basis. <br />Some of the frequently used materials for <br />fence and wall construction are masonry, <br />precast concrete, and wood. <br />Masonry noise barriers can be made of <br />concrete blocks, brick or stone. A con- <br />crete block barrier might range in cost <br />from $10 a linear foot for a 6 -ft. high wall, <br />to $75 a linear foot for a 12 -ft. high wall. <br />This latter figure includes a safety rail- <br />ing. In general, a concrete block wall <br />would cost $50 to $60 a linear foot.l To <br />alleviate the monotony of a long run of <br />wall, pilasters can be used: a 20 ft. high <br />concrete wall with pilasters might cost <br />$300 per linear foot.2 Brick and stone are <br />extremely expensive and should only be <br />used for special aesthetic considera- <br />tions.3 <br />Precast concrete panels offer opportuni- <br />ties for cost reduction. A 13'4" high wall <br />in Fairfield, California constructed of <br />pre -cast concrete panels cost only $29.50 <br />per linear foot. <br />Wood noise barriers are another possibil- <br />ity. They tend to be less expensive than <br />other methods but are not as durable. An <br />estimated cost for a 6' high 518" plywood <br />fence is $5.00 per linear foot.4 <br />C) Plantings Plants absorb and scatter <br />sound waves. However, the effectiveness <br />of trees, shrubs, and other plantings as <br />noise reducers is the subject of some <br />1 Figure provided by an official of <br />the California Highway De"n- <br />ment. <br />=Representative cost estimates of <br />materials and labor of construc- <br />tion but excluding real estate <br />acqutaklon; private <br />debate.: conclusions can, however, <br />be drawn. <br />• Plantings in a buffer strip, high, dense, <br />and thick enough to be visually opaque. <br />will provide more attenuation than that <br />provided by the mere distance which the <br />buffer strip represents. A reduction of <br />3-5 dBA per 100 feet can be expected. <br />Shubs or other ground cover are neces- <br />sary in this respect to provide the re- <br />quired density near the ground. <br />• The principal effect of plantings is psy- <br />chological. By removing the noise source <br />from view, plantings can reduce human <br />annoyance to noise. The fact that people <br />cannot see the highway can reduce their <br />awareness of it, even though the noise <br />remains. <br />• Time must be allowed for trees and <br />shrubs to attain their desired height. <br />• Because they lose their leaves, decidu- <br />ous t rees do not provide year-round noise <br />protection. <br />In general, plantings by themselves do <br />not provide much sound attenuation. It is <br />more effective, therefore, to use plant- <br />ings in conjunction with other noise re- <br />duction techniques and for aesthetic <br />enhancement. <br />The cost of plantings varies with the <br />species selected, the section of the <br />country, the climate, and the width of the <br />buffer strip. For deciduous trees and <br />evergreens, costs range from $10 to $50 a <br />linear foot. The width of such a strip <br />would be approximately 40 feet for deci- <br />duous trees and 20 feet for evergreens. <br />Planting shrubs between the trees so as <br />to form a dense ground cover would <br />double the price. <br />3Caiifornia Division of Highways, <br />Highway Noise Control, Value En- <br />gineedng Sfudy, (October 1972), <br />p. 33. <br />aCanfornia Division of Highways, <br />.40wary Noise Control. Valor En- 54 <br />0)Combinations of Various B& 7esigns <br />Of ten, the most economical, stically t <br />acceptable, and aesthetically pleasing <br />barrier ,s some combination of the barrier <br />types previously discussed. <br />F;;t example, the Milwaukee: County <br />Eyoressway and Transportation Commis- <br />sion feels that barriers constructed of <br />;,re -cast concrete on top of an earth berm <br />provide maximum benefit for the cost.5 <br />They estimate that such a co Tibination <br />costs $.51 per linear loot. <br />In addition to cost advantages an earth <br />berm with a barrier wall on top of it pos- <br />sesses several other advantages over <br />both a wall or a berm alone: 1) it is more <br />visually pleasing than a wall of equivalent <br />height; 2) the berm portion of this com- <br />bination is less dangerous for a motorist <br />leaving the roadway; 3) the non -vertical <br />construction of the berm does not reflect <br />noise back to the opposite side of the <br />highway the way a wall does; 4) the <br />combination requires less land than <br />would be required for a berm of equiva- <br />lent height and slope; and 5) the wall <br />provides a fencing function not provided <br />by a berm. <br />Another combination to be considered is <br />that of plantings in combination with a <br />barrier. Not only do plantings and ground <br />cover provide some additional noise at- <br />tenuation, but they also increase visual <br />appeal. <br />4.5 Conclusion <br />Figure 4.19 provides a summary of the <br />physical techniques which can be used <br />by designers, builders, and developers to <br />reduce highway noise impacts. Some <br />gireenng Study. iOctober 1972) <br />p• 46• <br />S Milwaukee County Expressway <br />and Transportation Commission, <br />Norse Impact Study of the Airport <br />Spur. V. 0: Technical Report, <br />(March 1973). pp. 7-21. <br />
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