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fundamentals of engineering supplied-reference handbook - Ventech!

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LANDFILL<br />

Break-Through Time for Leachate to Penetrate a<br />

Clay Liner<br />

2<br />

d η<br />

t = , where<br />

K d + h<br />

( )<br />

t = breakthrough time (yr),<br />

d = thickness <strong>of</strong> clay liner (ft),<br />

η = porosity,<br />

K = coefficient <strong>of</strong> permeability (ft/yr), and<br />

h = hydraulic head (ft).<br />

Typical porosity values for clays with a coefficient <strong>of</strong><br />

permeability in the range <strong>of</strong> 10 –6 to 10 –8 cm/s vary from 0.1<br />

to 0.3.<br />

Effect <strong>of</strong> Overburden Pressure<br />

p<br />

SWp = SWi +<br />

a+ bp<br />

where<br />

SWp = specific weight <strong>of</strong> the waste material at pressure<br />

p (lb/yd 3 ) (typical 1,750 to 2,150),<br />

SWi = initial compacted specific weight <strong>of</strong> waste<br />

(lb/yd 3 ) (typical 1,000),<br />

p = overburden pressure (lb/in 2 ),<br />

a = empirical constant (yd 3 /lb)(lb/in 2 ), and<br />

b = empirical constant (yd 3 /lb).<br />

Gas Flux<br />

N<br />

A<br />

Dη<br />

=<br />

4 3<br />

( C − C )<br />

Aatm<br />

L<br />

Afill<br />

, where<br />

NA = gas flux <strong>of</strong> compound A, g/(cm 2 ⋅ s)[lb ⋅ mol/ft 2 ⋅ d)],<br />

C A = concentration <strong>of</strong> compound A at the surface <strong>of</strong> the<br />

atm<br />

landfill cover, g/cm 3 (lb ⋅ mol/ft 3 ),<br />

C A = concentration <strong>of</strong> compound A at the bottom <strong>of</strong> the<br />

fill<br />

landfill cover, g/cm 3 (lb ⋅ mol/ft 3 ), and<br />

L = depth <strong>of</strong> the landfill cover, cm (ft).<br />

Typical values for the coefficient <strong>of</strong> diffusion for methane<br />

and carbon dioxide are 0.20 cm 2 /s (18.6 ft 2 /d) and 0.13<br />

cm 2 /s (12.1 ft 2 /d), respectively.<br />

D = diffusion coefficient, cm 2 /s (ft 2 /d),<br />

ηgas = gas-filled porosity, cm 3 /cm 3 (ft 3 /ft 3 ), and<br />

η = porosity, cm 3 /cm 3 (ft 3 /ft 3 )<br />

150<br />

ENVIRONMENTAL ENGINEERING (continued)<br />

Soil Landfill Cover Water Balance<br />

∆SLC = P – R – ET – PERsw, where<br />

∆SLC = change in the amount <strong>of</strong> water held in storage in<br />

a unit volume <strong>of</strong> landfill cover (in.),<br />

P = amount <strong>of</strong> precipitation per unit area (in.),<br />

R = amount <strong>of</strong> run<strong>of</strong>f per unit area (in.),<br />

ET = amount <strong>of</strong> water lost through evapotranspiration<br />

per unit area (in.), and<br />

PERsw = amount <strong>of</strong> water percolating through the unit<br />

area <strong>of</strong> landfill cover into compacted solid waste<br />

(in.).<br />

NOISE POLLUTION<br />

P<br />

2<br />

SPL (dB) = 10 log10 ( P )<br />

SPLtotal<br />

2<br />

/ o<br />

= 10 log10 Σ 10 SPL/10<br />

Point Source Attenuation<br />

∆ SPL (dB) = 10 log10 (r1/r2) 2<br />

Line Source Attenuation<br />

∆ SPL (dB) = 10 log10 (r1/r2)<br />

where<br />

SPL (dB) = sound pressure level, measured in decibels<br />

P = sound pressure (Pa)<br />

P0<br />

SPLtotal<br />

= <strong>reference</strong> sound pressure (2 × 10 –5 Pa)<br />

= sum <strong>of</strong> multiple sources<br />

∆ SPL (dB) = change in sound pressure level with distance<br />

r1 = distance from source to receptor at point 1<br />

= distance from source to receptor at point 2<br />

r2<br />

POPULATION MODELING<br />

Population Projection Equations<br />

Linear Projection = Algebraic Projection<br />

PT = P0 + k∆t, where<br />

PT = population at time T,<br />

P0 = population at time zero,<br />

k = growth rate, and<br />

∆t = elapsed time in years relative to time zero.<br />

Log Growth = Exponential Growth = Geometric Growth<br />

PT = P0e k∆t<br />

ln PT = ln P0 + k∆t, where<br />

PT = population at time T,<br />

P0 = population at time zero,<br />

k = growth rate, and<br />

∆t = elapsed time in years relative to time zero.

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