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Table H3
Contaminated and Cap Material Volumes and Mound Dimensions
Tot Vol, m3
Apron Vol, M3
Footprint, m2,
Max thick, m
( yd 3)
(yd3)
Project
% Total
(acres)
(ft)
Contaminated
Port Elizabeth/
448,000
52,000
11.6
1,470,000
2.40
Newark
(586,000)
(68,000)
(363)
(8.0)
Generic No. 1
96,600
49,900
51.7
785,400
0.9
(Figure H1)
(126,300)
(65,300)
(194)
(3.0)
Generic No. 2
96,600
49,900
51.7
785,400
0.9
(Figure H2)
(126,300)
(65,300)
(194)
(3.0)
Cap
Port Elizabeth/
1,870,000
1,040,000
55.6
1,470,000
1.8
Newark (1 m cap
(2,445,900)
(1,360,300)
(363)
(5.91)
over entire project)
Generic No. 1
847,200
140,400
16.6
1,097,000
0.9
(Figure H1) (0.9 m
(1,108,100)
(183,600)
(271)
(2.95)
cap over entire
project)
Generic No. 2
347,800
15,100
4.3
885,800
0.9
(Figure H2) (0.9 m
(454,900)
(19,750)
(219)
(2.95)
cap over main
mound, 0.3 m cap
over apron)
extends a distance of 15 to 30 m beyond the expected edge of the contaminated
material.
For sites with significant currents (say 30-50 cm/sec and greater) some loss of
cap material will probably be experienced. The Seattle District has documented
that for small sites (100 to 150 m overall dimensions) this "volume lost," which
is a actually cap material that is moved beyond the edge of the contaminated
sediment, can be from 10 to 20 percent of the estimated volume required based
on a flat cap over the contaminated sediment footprint (Parry 1994).
For a fine-grained cap, the volume lost to consolidation will have to be taken
into account for the erosion layer. An estimate of the amount of consolidation
over time will be required and the additional thickness added to account for
potential erosion. Note that the reduced cap thickness from consolidation may
not be a problem from a chemical isolation standpoint due to advection of con-
taminants. The reduced cap thickness from consolidation is somewhat compen-
sated for by the reduced void ratio and permeability, creating more tortuous
paths for the contaminants to diffuse through.
H10
Appendix H Level-Bottom Capping Projects
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