fundamentals of engineering supplied-reference handbook - Ventech!
fundamentals of engineering supplied-reference handbook - Ventech!
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.