United States
Environmental Protection
Agency
Municipal Environmental Research EPA-600/2-80-135
Laboratory August 1980
Cincinnati'OH 45268
Research and Development
Porous Pavement
Phase I
Design and
Operational Criteria
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RESEARCH REPORTING SERIES
Research reports of the Office of Research and Development, U.S. Environmental
Protection Agency, have been grpuped into nine series. These nine broad cate-
gories were established to facilitate further development and application of en-
vironmental technology. Elimination of traditional grouping was consciously
planned to foster technology transfer and a maximum interface in related fields.
The nine series are: I
1. Environmental Health Effects Research
2. Environmental Protection Technology
3. Ecological Research
4. Environmental Monitoring
5. Socioeconomic Envirohmental Studies
6. Scientific and Technical Assessment Reports (STAR)
7. Interagency Energy-Environment Research and Development
8. "Special" Reports
9, Miscellaneous Reports
This report has been assigned to the ENVIRONMENTAL PROTECTION TECH-
NOLOGY series. This series describes research performed to develop and dem-
onstrate instrumentation, equiproent, and methodology to repair or prevent en-
vironmental degradation from point and non-point sources of pollution. This work
provides the new or improved technology required for the control and treatment
of pollution sources to meet environmental quality standards.
This document is available to the'public through the National Technical Informa-
tion Service, Springfield, Virginid 22161.
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EPA-600/2-80-135
August 1980
POROUS PAVEMENT
PHASE I - DESIGN AND OPERATIONAL CRITERIA
BY
Elvidio V. Diniz
Espey, Huston & Associates, Inc.
Albuquerque, New Mexico 87110
Grant No. R806338
Project Officer
Hugh Masters
Storm and Combined Sewer Section
Municipal Environmental Research Laboratory (Cincinnati)
Edison, New Jersey 08817
This study was conducted in cooperation with
The City of Austin, Texas
MUNICIPAL ENVIRONMENTAL RESEARCH LABORATORY
OFFICE OF RESEARCH AND DEVELOPMENT
U.S. ENVIRONMENTAL PROTECTION AGENCY
CINCINNATI, OHIO 45268
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DISCLAIMER
This report has been reviewed by the Municipal Environmental Research
Laboratory, U.S. Environmental Protection Agency, and approved for publication.
Approval does not signify that the contents necessarily reflect the views and
policies of the U.S. Environmental Protection Agency, nor does mention of trade
names or commercial products constitute endorsement or recommendation for use.
ii
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FOREWORD
The Environmental Protection Agency was created because of increasing
public and government concern about the dangers of pollution to the health and
welfare of the American people. Noxious air, foul water, and spoiled land are tragic
testimony to the deterioration of our natural environment. The complexity of the
environment and the interplay between its components require a concentrated and
integrated attack on the problem.
Research and development is that necessary first step in problem solution and
it involves defining the problem, measuring its impact, and searching for solutions.
The Municipal Environmental Research Laboratory develops new and improved
technology and systems for the prevention, treatment, and management of waste-
water and solid and hazardous waste pollutant discharges from municipal and
community sources, for the preservation and treatment of public drinking water
supplies, and to minimize the adverse economic, social, health, and aesthetic effects
of pollution. This publication is one of the products of that research; a most vital
communications link between the research and the user community.
The development of porous pavement is a recognition of the interplay between
two components of our physical environment—water and earth. Porous pavement
utilization attempts to sustain physical processes ongoing under natural conditions.
A reorientation of urban land use from exclusion of infiltration of surface water to
enhancement of infiltration can be successful with regard to both the short and long
term impact of urban development,,
Francis T. Mayo, Director
Municipal Environmental Research
Laboratory
i 11
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ABSTRACT
The overall objective of this research was to determine factors which
influence runoff and water quality from areas using various porous pavement
designs. The resulting information will be used to develop design criteria for
potential porous pavement construction.
The first phase of this project, as reported herein, was to accumulate all
available design, construction, and operational data for existing porous asphalt
pavement areas, this report summarizes these data. Phase II of thf project will
compare the runoff and water quality characteristics of porous pavement to other
kinds of conventional and experimental paving materials. Phase II results will be
presented in a separate report.
Porous asphalt pavement consists of a relatively thin course of open graded
asphalt mix over a deep base* made up of large size crushed stone aggregate. The
open graded asphalt mix has a minimum of fines (two percent or less passing the
Number 200 sieve) and consequently forms a porous matrix for water to pass through
to the gravel base and underlying ground. The water can be stored in the voids
between the large gravel in the base material until it can percolate into the subbase
or be drained through lateral drainage schemes. In this way, | ik runoff to storm
sewers or drainage channels can be reduced, ground water rechc s is enhanced, and
the cost of drainage improvements is reduced. The major cost reduction is a result
of the elimination of curbs, drains, and storm sewers which are required under
conventional drainage design. Additionally, storm water pollution and flooding can
be reduced or eliminated.
Other porous pavement types include concrete lattice blocks with grass
growing in the interstices (grasscrete) and a concrete mix with sufficient air voids
to make it porous.
The development of porous pavement is an efficient combination of two
existing highway drainage practices—open graded asphalt mix seal coats and open
graded crushed stone bases. However, the installation of porous pavement is
possible only on well drained soils or soils provided with additional relief subsurface
drainage.
Previous experience with porous pavement by various designers, contractors,
and operators, has been evaluated and reduced to specific design and operational
criteria which are presented herein. A set of sample specifications is included in
Appendix A to this report.
A brief discussion of the advantages, as well as, the disadvantages of porous
pavement utilization, a brief history of the development and previous uses of open
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graded asphalt friction courses, and a generalized computer program applicable to
the design of all porous and non-porous parking areas are included in this report.
This report is submitted in fulfillment of Grant Number R806338 by Espey,
Huston and Associates, Inc. working under a subcontract with the City of Austin,
Texas. This project is sponsored by the United States Environmental Protection
Agency. The report covers the period February 1, 1979 to August 1, 1979, and work
was completed as of the latter date.
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CONTENTS
Section
Foreword
Abstract
List of Figures
List of Tables
Abbreviations and Symbols
Acknowledgments
I. Introduction
2. Conclusions
3. Recommendations
4. Background
5. Description of Porous Asphalt Pavements
6. Advantages and Disadvantages of Porous Asphalt
Pavement Usage
Design Considerations
Computer Model for Hydrologic Design
7.
8.
References
Appendix
A. Sample Specifications for Porous Asphalt Pavement
B. Hydrologic Soil Group Classifications
Page
iii
iv
vi i I
ix
x
xi i
10
13
16
20
25
30
47
60
62
78
VI I
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Figure
I
2
3
4
5
LIST OF FIGURES
Original Open Graded Base Course Application
Porous Asphalt Paving - Typical Section
Hydrologic Model Parameters for Porous Pavement
Izzard's Dimensionless Hydrograph of Overland Flow
Triangular Approximation of Evaporation
Page
19
21
48
50
57
VI
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LIST OF TABLES
Table
I Existing Porous Pavement Areas
2 Technical Data for Existing Porous Pavement Areas
3 Owners and Designers for Existing Porous Pavement
Sites
4 Friction Coefficients for Porous Pavement Surfaces
5 Soil Strength Categories
6 Minimum Thickness of Porous Paving for Various Loading
Conditions
7 Aggregate Gradation Limits for Porous Asphalt Mixes
8 Asphalt Content for Porous Asphalt Mixes
9 Effects of Varying Asphalt Content and Mixing
Temperatures on Porous Pavement Mixes
10 Porous Pavement Design Thickness for Frost Depth
Page
4
5
7
28
34
35
36
38
40
42
ix
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LIST OF ABBREVIATIONS AND SYMBOLS
ABBREVIATIONS
CBR
cm
EAL
FHWA
ha
kg
km
kPa
m
m2
m3
mm
MT
NAVFAC
evap
OL
'hors
°vert
USEPA
WES
—California Bearing Ratio
—centimeter
—equivalent axle load
—Federal Highway Administration
—hectare
—kilogram
—kilometer
—kilopascal
—meter
—square meter
—cubic meter
—millimeter
—metric ton
—Naval Facilities Engineering Command
—evaporative outflow
—horizontal outflow
—vertical outflow
—U.S. Environmental Protection Agency
—U.S. Army Corps of Engineers Waterways Experiment Station
SYMBOLS
a
A
C
E
E_
H
AH:
-cross sectional area of surface water
-cross sectional area of flow element
-input weir coefficient
-instantaneous evaporation
-peak evaporation rate
-total daily evaporation
-depth of dead surface storage on porous pavement
-depth of surface water at time t,
-depth of surface water at time \^
-depth of flow
-change of water depth at boundary
-rainfall intensity
x
-------
k
K
I
L
N
0
P
q
%
Q
s
S
At
a
T
v
V
V
e
V
o
w
W
Y
— inflow Into the reservoir
— lumped coefficient for effects of slope and flow retardance
—permeability of flow element
— length of overland flow
—input weir length
— input roughness coefficient
—outflow from the reservoir
—pavement perimeter
—flow rate per unit width
—equilibrium flow
—total mass flow rate
— input energy slope
—coefficient of storage of aquifer
—time increment
—beginning time of time increment
—ending time of time increment = ti
—time after rainfall has ceased
—time to equilibrium
—clock time
—aquifer transmissivity
—velocity of flow
—volume of aggregate
—equilibrium surface detention volume
—surface detention volume .
—width of flow
—total weight of surfacing mixture
—computed depth of flow
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ACKNOWLEDGMENTS
The cooperation of the City of Austin, Texas, Engineering Department, is
gratefully acknowledged. Mr. Charles Graves, City Engineer, provided grant
supervision and project guidance, and Mr. Richard Halstead maintained fiscal
control over the grant. I am particularly indebted to Mr. Troy Ulmann and Mr.
Ramon Miguez of the Watershed Management Section, for their cooperation, active
support, and sustained interest in the project.
Information on the development and initial application of porous pavement was
supplied by Mr. Edmund Thelen and Mr, Richard Hollinger of the Franklin Institute
Research Laboratories, Mr. Albert lamurri of Mirick Pearson llvonen Batcheler, Mr.
Joachim Tourbier of the University of Pennsylvania, Mr. Douglas P. Lloyd of New
Castle County, Delaware, Mr. Leonard Cannatelli of the University of Delaware,
Mr. Otto Fischer of the Klett Organization, Mr. G. F. Haack of the Department of
Housing and Construction, Perth, Australia, and Mr. Walter R. Hunzicker of Zurich,
Switzerland. All of the information and support provided by these individuals is
sincerely appreciated.
This project was conducted under the supervision of Dr. William Espey, Jr.
and Mr. Joseph Seal. Data compilation and reduction were performed by Mr. Billy
Goolsby and Mr. Craig Morton. Dr. Brent Rauhut provided guidance for porous
asphalt structural design and also developed the sample specifications presented
herein.
I would also like to acknowledge Mr. Richard Field, Chief, Storm and
Combined Sewer Section and Mr. Hugh Masters, U.S. Environmental Protection
Agency Project Officer, for their cooperation, guidance and assistance on this
project.
XI I
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SECTION I
INTRODUCTION
Porous asphalt pavement Is one alternative solution to the problem of
stormwater drainage from parking and other low traffic density areas. In operation,
this type of pavement allows incipient rainfall and local runoff to soak through the
pavement surface course of open graded asphalt concrete mix and accumulate in a
porous base consisting of large open graded gravel from which the water would
percolate into the natural ground below, if this is possible, or would drain laterally
to a sump or channel.
The October II, 1973 issue of Engineering News Record Magazine editorial-
ized on porous pavement development. Part of this editorial follows:
"Instead of pavements built of carefully graded materials topped
and sealed to be waterproof, porous soils might just as well carry porous
pavements. Let rainfall run through rather than run off. Save the cost
of curbs, gutters, drains, collectors, storm sewers, receiving basins. And
get a good skid resistant pavement surface in the process.
The idea has a freshness and simplicity about it. And if there are
flaws, they should be found In tests at experimental installations,
existing and planned. But we'll be surprised if the construction industry
does not grab this idea and run with it without waiting for the full
findings of tests. The only real danger can be misapplication, use of the
pavement on soils that are not suited for it, not porous."
In regular applications for highway and airport runway construction, the open
graded asphalt concrete mix has variously been referred to as plant mix seal coat,
open graded mix, gap graded mix, popcorn mix, or porous friction course. This
material consists of an open graded asphalt concrete mixture with a high percentage
by weight of aggregate larger than a Number 4 sieve. The material is laid to a
thickness of 3/4 to 1 inch (1.91-2.54 cm). The resulting pavement has a coarse
surface texture and a high void ratio. The coarse surface texture provides pressure
relief channels to remove water under excess pressure between the pavement and a
vehicle tire. Also, the high void ratio provides channels for dissipation of pressure
and flow beneath the vehicle tire. Finally, the high void ratio also provides
temporary storage for surface water. Consequently, hydrostatic pressure cannot
build up in the film of surface water under a vehicle tire and hydroplaning potential
is eliminated. Conjunctively, the coefficient of friction between the tire and
pavement is almost equivalent to the coefficient under dry conditions.
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The highway departments of California, Nevada, New Mexico, Utah and
Louisiana have been using plant mix seal coats because of their safety aspects for at
least the past 10 years. Application of this material to airport runways was
initiated in 1967 at Farnborough, England by the British Royal Air Force, and two
European air fields by the United States Air Force. Since 1947, the California
Highway Department has utilized open graded base courses under conventional top
paving to provide rapid drainage in problem areas.
In 1971, Franklin Institute Research Laboratories, under United States En-
vironmental Protection Agency (USEPA) sponsorship, investigated the use of a
porous base and a porous subbase in conjunction with a thicker application ot the
plant mix seal coat (I). The intent of this experiment was to investigate the
potential of delivering water to the subbase rather than removing it to a storm
water collection system. Initial installations in Delaware and Pennsylvania (2)
proved successful and subsequent installations in Texas (3) have been scientifically
instrumented and monitored.
Currently, each porous pavement design is unique; therefore, it is evaluated
and permitted by regulatory agencies only after a long analysis and review period.
This report is prepared in an attempt to standardize the design approach and yet
allow the designer sufficient latitude for individual creativity. It is expected that
the data presented in this report may be sufficient to design simple parking areas
and residential streets. However, for complex conditions, a thorough analysis by
qualified professionals is essential for the design of a porous pavement.
In general, potential as well as existing users and review agencies have
expressed a need for data on three conditions regarding porous pavement systems.
These conditions are:
1. Construction feasibility, maintenance and design life.
2. Control and management of runoff peaks and volumes.
3. Control and management of water quality degradation.
This report addresses these three issues and attempts to provide sufficient
data to indicate the desirability of porous pavement parking areas as a viable means
of drainage control and water quality enhancement.
The need to evaluate the runoff changes and water quality constituent
changes from urbanizing activities is paramount in the design of porous pavement
systems. Unfortunately, most engineering practice holds the view that all pave-
ments have to be evaluated solely from a runoff view point. Only recently has
water quality degradation become a point of concern for most practitioners and
public officials. It is anticipated that as the concern for water quality of urban
runoff becomes recognized, the need for porous pavement parking systems will
increase.
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The study reported herein investigated all of the available data from existing
porous pavement sites. This data included the engineering design, hydrology,
pavement design, construction methods, operation and maintenance of the site and
problems encountered in construction and maintenance. All of this information was
condensed in Tables 1, 2, and 3, and personal observations were added where
appropriate. However, the only scientifically instrumented porous pavement area is
at The Woodlands site in Texas (USEPA Grant No. S802433). This data compilation
should prove useful in evaluating the need for and designing porous pavements in
other areas of the United States.
The list of existing porous pavement areas presented in Table 1 is not
comprehensive and only indicates those areas for which data were readily available.
Numerous other porous pavement areas have been designed and constructed, but
researching these was beyond the scope of this study.
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TABLE 1
EXISTING POROUS PAVEMENT AREAS
Number
Location
1A
IB
2
3
4A
4B
5*
6*
7
8*
9
11*
13
14
15
South College Avenue Parking Lot. Newark, Delaware
Orchard Road Parking Lot. Newark, Delaware
Marine Sciences Center. Lewes, Delaware
Woodlands, Texas
Bryn Mawr Hospital. Bryn Mawr, Pennsylvania
Bryn Mawr Hospital, Lot No. 2. Bryn Mawr, Pennsylvania
Havertown Hospital. Havertown, Pennsylvania
Newton, Savings Association Parking Lot, Washington
Crossing, Pennsylvania
Trave lodge. Tampa, Florida
Salisbury State College. Sal isbury,. Maryland
Powell Ford Park. New Castle County, Delaware
Coney Island Housing Project. North of Nathans, New York
Korman Interplex. Philadelphia, Pennsylvania
Bell Telephone Company, West Goshen Township,
Chester County, Pennsylvania
Bell Telephone Company. Newtown , Pennsylvania
Hollywood Hospital . Perth, Austral ia
Hamersley Headquarters Telecom. Perth, Australia
Zurich Hilton. Zurich,. Switzerland
^Identified existing sites for which data were not aval 1 able
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TABLE 2 (continued)
Porous Pavement
Site
Asphalt Mix
Thickness
inches
Base
Thickness
inches
Drains
Installed
Remarks/
Comments
1A
IB
2
3
4A
4B
7
9
12
2.5
2.5
2.5
2.5
2.5
2.5
2.5
2.5
1 inch - 2.54 en
1 foot M 30.48 cm
1 acre - 0.405 hectare
12
12
12
10-14
12
12
16
30 ft. trench, 15 ft. X
3 ft. L-shaped 3/4 inch
stone
45 ft. trench, 15 ft. X
3 ft. L-shaped 3/4 inch
stone
30 ft. trench, 15 ft. X
3 ft. 3/4 inch stone
5-4" drains to nearby
creek
Asphalt was laid on hot day,
trouble with rolling, trouble
with trucks disturbing subbase,
had to regrade.
Northwest Corner
Southwest Corner
Pavement Failed
40 ft. trench 6.5 ft. X
3 ft. in end of lot
6V layers of 2" stone 5' back
from end of lot
Breakdown of asphalt by large
trucks parking, water ponding
In place for 5 years, excellent
condition water runs off end of
lot
Mud from heavy equipment plugged
porous pavement lot, fork lifts
gouge pavement
13
14
15'
4.0
2.0
2.0
8-20
than crushed rock
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SECTION 2
CONCLUSIONS
Porous pavements can be an effective means of reducing the increase in runoff
rates and volumes, and water quality degradation, resulting from urbanization
and/or other land use changes. The design of porous pavements has to be undertaken
with extreme care, particularly in areas where the natural soils do not have
sufficient permeability to naturally drain the stored runoff within a reasonable time.
The use of porous pavements is presently limited to parking lots only. Ideally,
these parking lots should be located on soils which have very low runoff potential or
which have a high percolation rate. Because all runoff from the site as well as
adjacent areas are effectively retained, it may be assumed that the entire area
contributing to the porous pavement has been removed from the surface hydrologic
regime. Consequently, the increase in runoff rates and volumes by urbanization is
offset by a reduction in drainage area.
The net downstream effect of porous pavements can range anywhere from a
reduction of runoff rates and volumes to below natural levels, or to the total
elimination of runoff from the immediate area. In either case, the effect
downstream can be quite substantial; in the case of storm sewers, the sewer
requirements may be reduced or eliminated, thereby providing substantial cost
reductions; and in the case of combined sewers, the number of overflows will be
reduced or eliminated, thereby providing direct benefits to the receiving water. In
both cases, the cost of additional drainage facilities is reduced; and, consequently,
the incremental additional cost of porous pavement systems may be recovered.
The water quality of urban runoff has been shown to be severely polluted in
some instances, but in all instances the runoff is at least partly contaminated. It is
obvious that just the infiltration and velocity reductions in porous pavements will
result in some suspended particulate removal and some chemical pollutant reduc-
tion. Preliminary data at The Woodlands site also indicate that nutrients can be
reduced to safely disposable forms and concentrations of some heavy metals can
also be reduced. In any case, the removal of water from the surface runoff regime
prevents the introduction of pollutants into the receiving water and creating
problems in downstream areas. ,
If it is known, or the possibility exists, that water infiltrating into the ground
could reach a water supply aquifer, adequate precautions should be taken to
determine that the surface runoff is not still contaminated when it reaches the
aquifer. If there is a possibility of adversely affecting the aquifer, the porous
pavement area should be designed to be sealed off from the aquifer recharge zone.
10
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If, on the other hand, the surface runoff Is designed to be cleaned before it reaches
the aquifer, then the infiltration of runoff into the porous paving and into the
natural ground should be encouraged in order to enhance the water supply from that
aquifer.
Another cost reduction can be realized in the elimination of curbs and gutters
around the parking lot. Porous pavements will operate more efficiently and there is
less chance of debris accumulation on the parking lot if curbs are eliminated. The
removal of curbs is also aesthetically desirable.
The removal of surface water from porous pavement surfaces proves to be a
distinct advantage under wet road conditions when it has been found that porous
pavements are approximately 15 percent more resistant to skids. This expected
result was evaluated by testing at The Woodlands, Texas site (4).
A review of the size gradations recommended by various highway authorities
and the Franklin Institute Research Laboratories for composition of the aggregate in
porous pavements indicates that a minimum of two percent passing the Number 200
sieve was required to provide stabilization of the coarse aggregate fraction.
Consequently, the following size gradation is recommended for the open graded
asphalt mix.
Sieve
Size
fe"
3/8"
# 4
# 8
# 16
# 200
Gradation
Recommended
100
90-100
35-50
15-32
2-15
0-3
The total asphalt cement content for the mix is suggested to be between 5.5
and 6.0 percent. However, the actual percentage is a function of the source and
type of aggregate. The exact percentage must be determined in the field,
particularly if the characteristics of the aggregate are not known from previous
experience. Also, dry aggregate should be used to avoid vapor release after the
aggregate is coated. Insulated covers must be used on all loads during haul to
prevent the asphalt from crusting on the surface of the load. Also, medium to light
weight vibratory rollers are somewhat better for compaction of the open graded
asphalt mix. A set of sample specifications is included in Appendix A to this report.
The design of porous pavement goes contrary to the classical requirements of
high density and low air voids in the surface course and base course of conventional
asphalt paving. Also, the idea of exclusion of water from the base course as in
classical design has to be reevaluated in the case of porous pavement.
11
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A two-inch (5.08 cm) top gravel course was found to be desirable to stabilize
the top of the gravel reservoir underlying the open graded asphalt mix. The gravel
reservoir is designed to control the total volume of runoff computed for the area
based on a preselected design storm and a hydrologic analysis of the area. Because
the length and width of the base reservoir are generally limited by the dimensions of
the parking lot, the only variable dimension can be the depth. If sufficient depth
cannot be obtained due to physical limits, additional relief drainage structures such
as french drains and pipe drains may be installed. In this case, the cost of such
structures can be quite expensive, and consequently, conventional drainage schemes
may become cost-competitive and viable alternatives. If the subbase does not drain
at a sufficient rate, relief drainage structures may be incorporated or additional
excavation or replacement with material having more desirable drainage charac-
teristics may be contemplated.
^ The total thickness of the base reservoir should be the largest depth
requirement for the bearing strength of the wet subbase, the hydrologic storage
requirements, or the frost depth for the site. In most cases, the hydrologic depth
requirement and the bearing strength of the soil are dependent upon the area
contributing to the porous pavement site; consequently, the frost depth may be the
governing or limiting factor (except in the case of very weak supporting soils). A
deep base may also be required to support heavy traffic loads.
The initial costs of porous asphalt can go as high as 35 to 50 percent above the
cost of conventional paving. However, the major reason for this difference is the
new ^ technology involved in porous pavement production, primarily in gradation
requirements and the narrow limit on asphalt cement content in the hot mix. If
curbs, gutters or storm sewers are not required, the total cost of the parking lot can
be comparable to or cheaper than a conventional parking lot, especially if the
aggregate source for the asphalt mix as well as for the base reservoir are easily
available. Therefore, it is anticipated that with the construction of additional
porous pavement areas, technology transfer should be facilitated. Also, construc-
tion crews will become more familiar with the process, and contractors will be able
to bid lower on porous pavement jobs.
The hydrologic design for porous pavements has been adopted onto a computer
program, PORPAV, which is available as a stand-alone program or as a subroutine
within the USEPA Storm Water Management Model. Both versions can be used to
determine the storage requirements for a given area, size, design storm, and
permeability and void ratios of the component parts and existing soil.
For most efficient operation of porous pavements it is desirable that the
subbase not be compacted or be only minimally compacted. This v/ill retain the
original permeability of the soil which can be substantially reduced after
compaction.
12
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SECTION 3
RECOMMENDATIONS
The design of porous pavement parking lots is just emerging from the
experimental phase. Most porous pavement users and designers would agree that
further research and test demonstration . pavement areas must be installed. Al-
though existing porous pavements have performed more than adequately and have
required minimal maintenance, some questions stjll remain. These include quanti-
fication of runoff and water quality changes, the long-term effects of continuous
saturation of the subgrade, maintenance and potential for plugging, aggregate
gradation and asphalt content in the hot mix, construction material types, and the
economic efficiency of using this type of pavement under existing regulations. Also,
the operation of porous pavements under snow and ice conditions should be
evaluated in detail.
Instrumented porous pavement systems would be desirable. This instrumen-
tation should provide information on rainfall, drainage, soil moisture, and water
quality effects; the data provided should be continuous during the progress of a
storm, thereby allowing an evaluation of dynamic changes in runoff and water
quality. Toward this end, a detailed analysis is being undertaken in Phase II of this
study. Phase II includes the evaluation of porous pavement and comparison to
various other pavement types. The data to be collected should prove helpful in
identifying the drainage and water quality benefits to be derived by porous
pavements for a variety of rainfall events. Also, presently unpredictable problems
may be uncovered.
The following paragraphs discuss specific recommendations in regard to future
analyses that may be conducted for porous pavement systems:
I) A detailed evaluation of runoff and water quality with respect to
porous pavement must be conducted. It would be desirable to determine these
characteristics under various rainfall intensities and climates. At present, the only
site thus observed is at The Woodlands, Texas. It would be interesting to determine
if pavement infiltration rates can be exceeded by naturally occurring rainfall
intensities because pavement environmental factors may affect the pavement
infiltration rate. Also, factual data is required for all climates in order to prove
porous pavement is truly effective world-wide. Particular attention must be paid to
winter conditions - the effects of freezing, de-icing materials, and maintenance
(snow removal, etc.). The Naval Civil Engineering Laboratory has surveyed five
porous friction courses in Great Britain and West Germany. Although the evalu-
ations were favorable in regard to service life in cold climates, similar efforts for
comparison purposes should be undertaken in the United States, particularly in the
mid-western and mountainous parts of the nation.
13
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2) Another aspect of porous pavement evaluation is the duration of
base saturation and its effect on pavement life and load bearing capacity. Because
existing conventional pavements may have saturated bases for extended periods as a
result of infiltration through pavement surface cracks, it seems that base and
subbase saturation should not be a problem, particularly since pavement strength is
based on saturated conditions. Although conventional roadway base material has a
critical water content limit, in large graded base material, where load transfer is
basically independent of water content, the load-bearing capacity of the base may
not be substantially affected. However, the subbase may lose some strength. This
loss in strength may be related to the proportion of granular materials in the
subbase. It would be desirable to investigate this loss of strength characteristic for
various subbase materials. Only site condition evaluation can determine the design
adequacy under a non-uniform dynamic traffic loading situation. Also, if the gravel
tends to become embedded in the saturated subbase during pavement loading, the
efficacy of a more stable but permeable membrane (filter cloth) or sand layer must
be investigated.
3) A third and conjunctive area of interest is the change in water
quality as runoff moves through the surface course into the base course and finally
into the subbase. These changes may also depend on the detention time in the base.
If any correlation between detention time, base and subbase chemical composition,
and water quality can be determined, the design of porous pavement systems for
water quality would be vastly improved. As a result of rapid introduction of
polluted runoff into the subbase, the effects on soil chemistry and biology as well as
ground water must be considered. Anaerobic bacteria culture in the base may allow
biological water treatment processes to be introduced into porous pavement
systems. One major problem will be the assurance of bacteria medium survival
during dry periods between storms, If this approach proves successful, the
efficiency of porous pavement systems with regard to water quality control will be
greatly increased.
4) The question of porous pavement surface clogging by urban dirt and
sand is of concern to most users. The feasibility of pavement clogging and the
efficiency of currently available equipment to restore premeability should be
investigated in order to provide maximum life expectancy of the pavement.
Existing data indicate that the surface of porous pavement is not easily clogged
under general use, but accidental spills of cloggable material do result in reduced
pavement permeabilities which can be restored with vacuum cleaning and hosing
with a water jet. In extreme cases, additional drain holes may be required to be
drilled in the pavement surface course.
5) Loss of cementitious properties in the asphalt or polishing of base
gravel by certain pollutants in runoff, e.g., acidic rain or spilled gasoline, must be
investigated. The results of this effort will provide means of identifying critical
localities or undesirable pollutants for which adequate precautions must be taken. If
a certain pollutant is found to be undesirable, porous pavement systems designed for
-------
this area should be located away from runoff carrying these pollutants. Another
phase of this investigation should address the feasibility of using an impermeable
liner between the base and subbase. This results in storage of runoff for future
treatment or disposal and consequently the effects of long-term contact with
polluted runoff must be evaluated.
6) A standard set of construction specifications should be developed
for open graded porous pavement mix design and construction. However, the
specifications should be flexible enough to allow certain design changes if needed.
Also, the design procedure and guide specifications for porous pavement as supplied
in this report should be investigated and utilized whenever possible.
7) The aggregate gradation and asphalt content for the porous pave^
ment and porous friction course mixes should be standardized so as to provide
greater acceptability by the design engineer and contractor. Standardization should
be on a regional or local basis because of material availability and construction
methods. This approach will allow a more standard pavement structural design and
will obviate the need to conduct a Jorge series of tests for each project.
Furthermore, as engineers and contractors gain experience in this type of pavement
construction, and as research on the design of mixes provides for an optimum design,
the cost of designing and installing porous pavement lots will probably be reduced.
The development of asphalt additives, e.g., neoprene, or other binding agents to
improve porous pavement service life and performance must be evaluated. As the
acceptability of porous pavements increases, these new materials may become
evident by exposure to different paving materials.
8) Asphalt hot mix plants should be reorganized to provide uniform
stockpiles and desirable aggregate cold feed in order to assure that the aggregate
will have the desired properties identified in the specifications.
9) The economy of porous pavement usage relative to conventional
paving must be evaluated because this aspect will be of major concern to most
owners and developers of porous pavement systems. In particular, if all aspects of
porous pavement need not be considered, e.g., areas where urban runoff water
quality is not of concern, then the cost comparison to conventional paving may not
be as complete or as valid, especially at present when construction experience leans
heavily toward conventional paving.
10) Public awareness of the porous pavement approach to runoff and
water quality control must be encouraged because most people do not generally
recognize any difference between porous and conventional asphalt pavements which
are similar in appearance. Increased public acceptance of proven porous pavement
systems will result in rapid responses to public demand by local government officials
and planning and designing communities.
15
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SECTION 4
BACKGROUND
The Federal Water Pollution Control Act Amendments of 1972 (PL 92-500) set
forth the requirements to insure "fishable and swimmable water" throughout the
nation by 1983 and to eliminate any polluting discharge into these waters by 1985.
Section 208 of this Act provides for areawide water quality management planning
which has subsequently been authorized under various sections of the Federal Clean
Water Act of 1977 (PL 95-217).
The accumulation and analysis of water quality data from urban areas by
various investigators (5, 6, 7) has indicated that storm water runoff is a major non-
point source of pollution. Structural measures to alleviate this problem have often
been the solution; however, former USEPA Administrator Russel E. Train (8) and
other proponents of non-structural measures, specifically land use controls, have
been recognized and appreciated in recent years. The primary objective of land use
controls is not exclusion of specific uses, but rather inclusion of land use practices
which do not degrade the receiving water quality. The installation of porous
pavements in urban areas is one significant land use practice which can be used to
meet the water quality objectives of PL 92-500.
A second set of Federal legislation which affects land uses in urban areas is
Section 1302 of the National Flood : Insurance Act Amendments of 1968, which
encourages state and local governments to "make appropriate land use adjustments
to restrict the development of land, which is exposed to flood damage..." This
objective was enforced by the Flood Disaster Protection Act of 1973 (PL 93-234) by
requiring states and local governments, as a condition for future Federal financial
assistance, to participate in the flood insurance program and to adopt adequate
flood plain ordinances with effective enforcement provisions.
The enforcement of these ordinances is contingent upon a stable hydrologic
regime; however, Brater (9), Espey, Morgan and Masch(IO), McPherson (11), and
others have indicated increased runoff rates and peak discharges after urbanization
which result in downstream land which originally experienced no flood hazard
becoming flood-prone. Therefore, upstream land use practices impact upon down-
stream areas, and, in recognition of this fact, numerous municipalities have enacted
legislation to prevent increases in runoff rates, and sometimes volumes, from
development sites.
The use of porous asphalt pavement for runoff control and water quality
enhancement is a relatively recent development. Open graded (large size aggregate
16
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only and therefore porous) asphaltic mix was initially develope'd and tested for
safety applications as friction courses on conventional paving.
Porous friction courses 3/4 to 1 inch (1.91-2.54 cm) thick are used on
conventionally paved and impermeable surfaces with the objective being to remove
surface water from the pavement and still maintain a dry base strong enough to
sustain design traffic loads.
Porous friction courses allow drainage through the voids in the mix, and if
adequate transverse grades are provided, out to the shoulders. The rapid removal of
surface water results in minimum pressure build-up under moving vehicle tires and
consequently, increased wet skid resistance and elimination of hydroplaning, as
previously described.
The elimination of hydroplaning and the improved wet skid resistance by
application of open graded asphaltic mix to conventional paving encouraged the
highway departments of California, Nevada, New Mexico, Utah, and Louisiana to
incorporate open graded friction courses in their highway design. The aforemen-
tioned safety features also instigated the use of porous friction courses for airport
runways; initially at Farnborough, England in 1967, by the British Royal Air Force,
and by the United States Air Force at two military air fields in Europe. In 1971, the
United States Naval Facilities Engineering Command installed a porous friction
course on the main runway at Hensley Airfield at the Naval Air Station in Dallas,
Texas. Concurrently, the United States Air Force Weapons Laboratory constructed
test strips of 8 different porous friction courses at Kirtland Air Force Base in
Albuquerque, New Mexico (12). Subsequent applications of porous friction courses
include Peace Air Force Base, New Hampshire; airports at Salt Lake City, Denver,
Greensboro (North Carolina); and several more state highway departments, including
Colorado, Kentucky, and Pennsylvania.
In all of these early investigations, emphasis was placed on removing surface
water laterally through the asphalt bound open graded matrix. Although the rate of
runoff was also affected, this aspect was not investigated. The total design for this
system also required a permanently sealed and prepared base and, therefore, the
runoff volume of the paved area was unchanged by addition of the open graded
overlay.
On the other hand, the use of an open graded base course was first
incorporated into highway design in 1947 on United States Highway 99, near Red
Bluff, California. 7.1 miles (11.4 km) of this highway were constructed with a
3/4-inch (1.91 cm) conventional asphalt concrete wearing course over an open
graded asphaltic concrete binder course, 2.4 inches (6.10 cm) thick, underlain by a
6-inch (15.24cm) cement treated base and a gravel subbase. After 10 years of
service under heavy truck traffic, this road was still in very good condition and has
required minimum maintenance (13).
17
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Since 1966, the United States Forest Service has been using permeable
materials to repave forest roads in the Pacific Northwestern states. This pavement
consists of 4 to 10 inches (10.2-25.4 cm) of crushed rock, held together with asphalt
binder and a thin chip seal wearing course. Most of these roads carry large numbers
of heavy logging trucks rather successfully because the water drains into the
pavement and, because of the generally steep grades, water drains away from the
roadway very quickly (14).
This concept of using an open graded gravel base between an existing prepared
subbase and a conventional asphalt concrete or concrete wearing course has been
developed and applied to several areas in California. The theory behind this concept
is to rapidly remove any water that percolated into the open graded base. This
removal is achieved by means of drain pipe collectors which discharge into adjacent
roadside ditches. This approach is based on the idea that the best solution for
pavement drainage is to install an artificial drain system under the wearing course
to prevent saturation of the underlying subbase layers of soil. Water filtering
through the cracks in the pavement is rapidly discharged horizontally through the
gravel base so it does not stand on the subgrade long enough to saturate and weaken
it. A total pavement thickness of 8 to 10 inches (20.3-25.4 cm) was found to be
sufficient for highway design. A typical cross-section of an installation near
Redwood City, California is shown in Fig. I (14). This installation was constructed
in 1970.
During 1970 and 1971, the Franklin Institute Research Laboratories in Phila-
delphia, Pennsylvania, under contract with the USEPA, attempted to combine the
porous friction course and the porous base concepts and thereby control runoff and
enhance water quality. They investigated the use of an open graded asphalt mix
underlain by a gravel base course and a minimally compacted subbase as a potential
solution (1). The successful test results suggested a unique approach to meeting the
requirements of the Federal Water Pollution Control and Flood Disaster Protection
Acts. Several applications of this technology, generally referred to as porous
asphalt, are now in operation mainly on the eastern coast and Gulf of Mexico regions
of the United States, as listed in Table I.
18
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SECTION 5
DESCRIPTION OF POROUS ASPHALT PAVEMENTS
In general, porous pavement is composed of four layers:
1. Minimally compacted subbase consisting of undisturbed existing'
soil or, in the case of unsuitable base soils, an imported and
prepared base course. Auxiliary drainage structures (French
drains, pipe drains, etc.) may also be required.
2. Reservoir base course consisting of I to 2 inches (2.54-5.08 cm)
diameter crushed stone aggregate. The thickness of this layer is
determined from runoff storage needs and frost depth consider-
ations as described later in this report.
3. Two inches (5.08 cm) of fe-inch (1.27 cm) crushed stone aggregate
to stabilize the reservoir base course surface.
4. Porous asphalt concrete surface course whose thickness is based on
bearing strength and pavement design requirements. In most
applications, 2fe inches (6.35 cm) has been found to be sufficient.
A typical porous asphalt pavement cross-section is presented in Fig. 2.
following descriptions are adapted from Thelen and Howe (15).
The Subbase
The
AH soils under roads may become wet, but they must drain in order to
maintain their bearing strength. Because soils under porous pavement will get wet,
they must be permeable to water; they must not heave due to freezing or thawing,
and they must not swell or substantially lose their strength when wet. Most soils
can meet these requirements if proper drainage is available. In current practice it
is very important that the subbase under conventional pavement remain dry and that
pavements often may be wet due to cracks in the pavement, percolation through the
shoulders, and capillarity from ground water. However, base strength is essentially
retained because free water can drain away, leaving the soil particle structure
intact. Soil strengths, as defined by the California Bearing Ratio, are measured on
wet soils because soil wetness is anticipated.
The contaminants on a road surface can range from random spills and
pesticides to engine fuel residues. In a storm sewer or street system, they are
typically collected in the initial runoff and discharged at one point in a receiving
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stream; in the porous pavement system they are delivered to the soil over the entire
area of the pavement.
It Is expected that contaminated water will tend to be purified as it passes
through the soil, as a result of absorption of contaminants by soil particles, bacterial
action, and dilution. On the other hand, water passing through soil may leach out
minerals and pick up bacteria.
At the Franklin Institute Research Laboratories, preliminary tests indicated
that aerobic bacteria can live in the soil under porous pavement; these could act like
sewage treatment plants to digest organic contaminants. At The Woodlands, Texas
site (4), aerobic digestion was discovered, with ammonia in the runoff being con-
verted to nitrites and nitrates. Further reduction was not possible due to
faulty drainage of the subbase. However, the nitrogen in the runoff from
the control pavement was mostly nitrates. Both total organic carbon and
chemical oxygen demand were much lower in the porous pavement percolate than
in the runoff, because of bacterial action in the base and subbase. The
limestone base material also raised the conductivity of the percolate which
then neutralized the carbonic acid in the rain and runoff.
Even though initial runoff had high lead concentrations, the percolate at The
Woodlands site showed practically no lead, because of faulty drainage of the
subbase, so that the percolate was diluted by storage, and because lead accumula-
tions were not significant.
The Reservoir Base Course
In conventional pavement, the base consists of stones, sand, and dust particles
packed into a dense mass and designed to transmit mechanical loads from the
hardtop to the soil below.
In porous pavement, the base consists of large-sized and graded stones, lightly
rolled into an open, interlocking structure which not only transmits mechanical
loads, but also stores runoff water which the soil cannot immediately absorb. This
water is held in the reservoir formed by voids in the rock matrix until it can
percolate into the soil. For size gradations recommended in this report, the voids
will be as high as forty percent of the total volume. Of course, if the soil has a
higher permeability rate than the rate of rainfall, a reservoir is not needed.
However, this is unlikely because maximum rainfall intensities of design storms are
generally much higher than the infiltration rates of most soils.
The aim of having a reservoir is to store runoff water for several hours to
allow it to percolate into the soil. On sloping pavements, base areas at the higher
end of the site are not credited with storage capability even though water enters the
base in these areas, because they drain laterally and do not contribute to the
percolation system at the higher end of the site.
22
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Because the base reservoir serves a purpose similar to retention basins, runoff
from roofs or other impervious and pervious surfaces could be drained into it; but
the base must be designed to have the required capacity.
The aggregate used in the base must be hard and durable. Generally it is
angular and not round. Crushed stone is the most desirable material because the
aggregate interlocks very well. Rounded gravel must be avoided for all areas where
heavy traffic is anticipated. The crushed stone should come from one of the
following rock groups:
(a) Granite
(b) Basalt
(c) Gabbro
(d) Porphyry
(e) Blast furnace slag
Limestones which are susceptible to polishing by water should be used in only special
situations where design loads are within the loading limits for this type of material.
The Reservoir Top Stabilizing Course
To assist in final grading of the reservoir base course to stabilize the surface,
a two-inch (5.08cm) layer of fe-inch (1.91 cm) crushed stone aggregate is recom-
mended. Based on previous construction experience, this stabilizer course is
necessary because construction vehicles hauling the asphalt hot mix across the
reservoir course would create ruts which consequently require constant regrading to
finished grade immediately prior to application of the hot mix.
Open Graded Asphalt Concrete Surface Course
Porous asphalt consists of a wearing course of open graded asphalt concrete
laid over a base course of uniformly sized aggregate. It differs from conventional
asphalt concrete chiefly in that it contains very little dust or sand; its void volume
typically is around 16 percent, as compared with the two to three percent void
volume of conventional asphalt concrete.
Asphalts used in asphalt concrete range from 50 to 100 penetration grade,
depending upon the ambient temperatures and viscosity characteristics desired. In
general, the grades used in a given locality for conventional asphalt concretes will
suffice for porous asphalt as well. However, the porous product is more subject to
scuffing, such as occurs when the front wheels of stationary cars with power
23
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steering are turned. It is therefore suggested by Franklin Institute Research
Laboratories that for porous asphalt, 50 to 60 penetration grade be used in the South
(Texas, Florida, etc.), 65 to 80 in the mid-Atlantic states, and 85 to 100 penetration
grade in the northern states.
The percent of asphalt should be specified between 5.5 and 6, based on the
total weight of the pavement. The lower limit is to assure adequately thick layers
of asphalt around the stones and the upper limit is to prevent the mix from draining
asphalt during transport, particularly if it is accidentally shipped at a temperature
of over 300° Fahrenheit (149° C).
To avoid damage due to photo-oxidative degradation of the asphalt (since air
and sunlight can penetrate further), the asphalt coatings on the aggregate surfaces
should be thicker than usual. In this case, the asphalt can form skins or otherwise be
mildly degraded without significant loss of cementitiousness.
The open graded asphalt concrete is similar in Marshall properties (strength
and flow) to conventional asphalt concrete. Hence, the usual thickness of base
course and paving should satisfy load requirements. The base course thickness may
have to be increased to provide greater reservoir capacity where runoff volumes
and/or soil percolation require it.
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SECTION 6
ADVANTAGES AND DISADVANTAGES OF
POROUS ASPHALT PAVEMENT USAGE
The primary design objective of porous asphalt pavements is to control runoff
rate and volume increases and water quality degradation resulting from developed
and impervious areas in deference to the requirements of the Water Pollution
Control and the Flood Disaster Protection Acts. However, numerous other primary
and secondary benefits are also realized with porous asphalt pavements. Each of
these benefits is identified and discussed in this section but the intensity of each
benefit is a site- and region-specific function and therefore a relative evaluation
was not attempted.
The advantages and/or benefits one may "reasonably expect from porous
asphalt pavements are as follows:
I) Runoff rate and volume control in areas where pervious ground is
replaced with impervious cover. The main impact is a substantial reduction of
runoff rate and volume from impervious areas. If the pavement and reservoir base
are designed adequately, all of the runoff may be detained and released at a rate
adequate to prevent increases in flood flows. Concurrently, the stored water may
be allowed to infiltrate into the natural ground.
2) Erosion control on unprotected overland flow and channel areas.
Because impervious areas generate higher rates of runoff than pervious areas, the
erosive capacity of the flow is also increased by means of increased depth of flow
and increased velocities. Consequently, overland flow and channel areas down-
stream from impervious areas would experience additional erosion and sediment
removal. However, the use of porous asphalt pavement systems would reduce or
entirely remove the excess runoff problem and therefore considerable benefits may
be derived from bank and soil protection and sediment reduction.
3) Water quality enhancement will be evident in areas where the
runoff generated from impervious areas has the potential for becoming contamin-
ated, as in the case of industrial and commercial land use areas. If the pollution is
not toxic and depending upon its characteristics, detention in the reservoir layer and
percolation through the subbase m'ay be sufficient to reduce the pollution to
acceptable levels.
If the stormwater requires treatment for toxic or non-filterable substances, it
may be stored in porous pavement systems isolated from the natural ground by an
impermeable membrane until treatment plant capacity becomes available. Thus,
25
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treatment plant capacity does not need to be expanded. Also, detention of highly
polluted initial runoff by the porous pavement, and dilution by less polluted
subsequent runoff can result in acceptable pollution concentrations throughout the'
storm duration.
4) The need for curbs and storm sewer installation or expansion may
be avoided. In already urbanized areas, such-as established areas of most cities as
well as existing shopping centers, where the storm sewer network was designed and
Installed prior to excessive impervious cover development (parking lot expansion,
etc.), the storm sewers may become overloaded, and if parking lot or roof storage is
not a design criterion, the disposal of excess runoff becomes a problem that porous
pavements could solve. This benefit is enhanced in areas with combined sewerage
because the probability of sewer overloading and the resultant discharge of raw
sewage into the receiving water is reduced.
In areas of slight topography or with minimal soil depths, the cost of installing
storm sewers is very high because both sewer size and excavation volumes are high.
The use of porous pavements in these areas reduces both sewer size and excavation
depth, thus resulting in a net savings in drainage costs.
5) Natural drainage boundaries and patterns can be maintained.
Consequently, elaborate drainage schemes to collect and deliver runoff to a safe
conveyance will not be necessary. Instead, drainage boundaries existing prior to
development may be retained without sacrificing the finished grade of the paving.
6) The nuisance factor to pedestrian and motorist arising from
standing puddles in parking lots, streets, and detention basins will not be a problem.
Also, disease vector control (mosquitoes, etc.) may be accomplished through the use
of porous pavement systems.
7) Natural vegetation and drainage patterns can be retained by the
use of porous pavements. Consequently, the clearing of trees from large areas for
parking lots is unnecessary and secondary aesthetic benefits are also derived. This
also applies to roadside vegetation in highly developed areas where, under conven-
tional paving, the soil moisture is severely deficient.
8) Groundwater recharge may be possible with porous asphalt paving.
In water deficient areas, impermeable paving may prevent recharge to a local
aquifer and thereby reduce its safe yield. Porous paving would correct this
condition.
•"• '•••"VI1 "'-
9) The full range of safety improvements resulting from porous
pavements has been evaluated only at The Woodlands, Texas, site (4). However, as
previously discussed, the improvements to wet pavement skid resistance have been
used successfully on'road surfaces in numerous states and airport pavements in
England, New Mexico and New Hampshire. The results of sliding friction tests
26
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conducted by Hollinger (4) at The Woodlands site and the United States Air Force
Weapons Laboratory at the Dallas site (12) are presented in Table 4. As expected,
the friction coefficients for wet porous paving are significantly greater than for wet
conventional paving. Also during these tests a singular, and as yet unresolved,
anomaly was discovered at The Woodlands site - porous pavement surfaces have a
higher friction coefficient when wet than when they are dry. Hollinger also
determined that:
a) Porous asphalt pavements generate slightly less traffic noise than
conventional asphalt pavements.
b) There is no real difference in light intensity reflected from white
and yellow markings on either type of pavement. However, the
effects of glare from oncoming vehicle lights, which obscure the
reflected light from paint on a wet conventional asphalt pavement,
were not evaluated.
c) Porous asphalt pavements tend to deflect for a longer time than
conventional asphalt pavements, but the magnitude of deflection is
approximately equal.
On the negative side of porous pavement usage, the most often expressed
concern is the susceptibility of the pavement to clogging. With proper care and
maintenance, this problem should not occur and past experience supports the
veracity of this statement.
Clogging of the pavement pores generally occurs due to operational and
construction scheduling problems. For example, spills of construction materials on
finished pavements, or hillside erosion and sedimentation on finished pavements may
clog the pavement or reduce its permeability. Obviously, the solution to con-
struction-related problems with porous pavements is to finish all ground preparation
and earth work prior to installation of porous pavements. After construction, the
haulage of clogable materials across porous pavements must be conducted with
extreme care to prevent spills.
If a spill should occur, immediate vacuuming and washing with a water jet will
restore pavement permeability almost to pre-spill rates - tests conducted at The
Woodlands site indicate a permeability recovery in excess of 95 percent. However,
if the pores are clogged and the dirt is compacted or ground in by traffic to a depth
greater than 0.5 inches (1.27 cm), full permeability cannot be restored. In this case,
holes may be drilled through the clogged area to provide the necessary drainage.
The areal distribution of holes required would be a function of pavement slope and
degree of clogging.
Porous pavement surfaces can also be ineffective during the melting of snow
which has accumulated on the surface; or if rain occurs on a frozen surface.
27
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TABLE 4
FRICTION COEFFICIENTS FOR POROUS PAVEMENT SURFACES
TEST
DATE
PAVEMENT
TYPE
DRY
CONDITION
WET
CONDITION
Dallas, Texas (12)
11/71
12/75
2/76
V76
Porous asphalt
Conventional asphalt
Grooved concrete
0.76
0.7^
0.76
Woodlands, Texas (k)
Porous Asphalt old
Porous asphalt new
Conventiona1 aspha1t
Porous asphalt old
Porous asphalt new
Conventional asphalt
Porous asphalt old
Porous- asphalt new
Conventional asphalt
0.61
0.66
0.73
0.82
0.83
0.99
0. Ik
0.80
0.78
0.70
0.16
0.71
0.85
0.74
0.59
0.95
0.90
0.81
0.84
0.84
0.71
28
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A second disadvantage in the use of porous pavement results from the fact
that some existing building codes and regulations are not intended for this new type
of technology. Specifically, if conventional drainage structures (curbs, gutters,
inlets, etc.) are arbitrarily required in all parking areas, then the construction costs
of porous pavement installation become economically excessive.
A temporary drawback arises out of a lack of data to indicate the capabilities
of porous pavement to filter and purify all contaminants in runoff. Initial results at
The Woodlands site indicate a reduction of most pollutants, but the data is
insufficient for generalization. Also, it is obvious that severely polluted runoff
should be excluded from a porous pavement because of its susceptibility to clogging.
Spillage of gasoline from leaking tanks of automobiles parked on the porous
pavement lot will break down the asphalt binder to greater depths than on
conventional pavements, primarily because the pores on the open graded mix permit
excursion of the gasoline into a larger spatial volume. The solution to this problem
may be the use of tar binders rather than asphalt.
The negative aspects of porous pavements as discussed above are not insur-
mountable in most instances. Also, the advantages far outweigh the disadvantages.
Consequently, the potential for porous pavement usage is expected to increase as
the problems outlined in this section are resolved.
29
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SECTION 7
DESIGN CONSIDERATIONS
The design of a porous pavement parking area requires the same basic
procedures as for a conventional parking area. However, the drainage aspects and
the corresponding changes in load-bearing capacity of the pavement require detailed
attention. In general, the design procedure will follow 3 basic functions:
I. Determination of existing soil properties
2. Load-bearing design of pavement and subgrade
3. Hydrologic design of pavement and subgrade
In addition to these 3 basic functions, corresponding operational and maintenance
factors during and after construction must also be considered. Each of the functions
is described in the following discussion:
Determination of Existing Soil Properties
At most building sites, the location of the parking area is governed by
numerous factors, including;
a. Building aspects
b. Aesthetics
c. Convenience
d. Surface slope
During the pre-design phase, factors affecting porous pavement installation must
also be considered.
Initially, a site inspection is imperative. Environmentally critical, unique, and
undevelopable areas must be identified and adequate precautions taken to prevent
damage to these areas during and after construction. The ideal location for porous
pavement is a well-drained soil on a relatively flat slope. Desirable trees and shrubs
which will not significantly affect traffic patterns and yet provide shade and beauty
to the area must also be identified and demarcated for preservation. Predominantly
clay soils must be avoided or, if this is not possible, relief measures must be adopted
' in the design.
30
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All available soil data for the site should be acquired and inspected. The
United States Department of Agriculture Soil Conservation Service has developed
soil maps for most counties in the United States; but in some areas even more
detailed soil information may be available. The Soil Conservation Service has
classified most soils into 4 hydrologic soil groups, defined as follows:
(A) Soils having high infiltration rates, when thoroughly saturated and
consisting chiefly of deep and well-drained sand or gravel. These
soils have a high rate of water transmission and low runoff
potential.
(B) Soils, having moderate infiltration rates, when thoroughly saturated
and consisting chief ly of generally deep and well-drained soils with
moderately fine to moderately coarse texture. These soils have a
moderate rate of water transmission.
(C) Soils having slow infiltration rates when thoroughly saturated and
consisting chiefly of soils with a layer that impedes downward
movement of water, or .soils with moderately fine or fine texture.
These soils have a low rate of water transmission.
(D) Soils having a very slow infiltration rate when thoroughly saturated
and consisting chiefly of clay soils with a high swelling potential,
soils with a permanent high water table, soils with a clay pan or
clay layer at or near the surface, and shallow soils over nearly
impervious materials. These soils have a very slow rate of water
transmission and a very high runoff potential.
In the above definitions, infiltration rate is the rate at which water enters the
soil at the surface, which is controlled by surface conditions (percolation rate), and
the transmission rate is the rate at which the water moves in the soil and is
controlled by the soil horizons or layers.
Appendix B presents a list of more than 4,000 soils in the United States and
Puerto Rico compiled by the Soil Conservation Service with hydrologic soil group
classifications for each soil. These classifications are based partly on the use of
rainfall runoff data from small watersheds or infiltrometer plots. However, the
majority of the classifications are based on the judgement of soil scientists who use
physical properties of the soil in making their decisions. Each soil was classified in
a particular hydrologic group by comparing its profile with profiles of soils already
classified. It was assumed that the soil surfaces were bare, maximum swelling had
taken place, and rainfall rates exceeded surface detention and infiltration. Thus,
most of the classifications are based on the premise that similar soils (similar in
depth, organic matter content, structure, and degree of swelling when saturated)
31
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will respond in an essentially similar manner during a rainstorm having sufficient
intensities to generate runoff.
If the site inspection or other information indicates that the original soil
classification may not be correct, additional testing may be required to properly
identify the hydrologic soil group for that particular soil. Hydrologic soil groups (A)
and (B) are ideal for porous paving sites. However, potential areas in soil groups (C)
and (D) require more attention. In certain areas (low design runoff volumes), soil
groups (C) and (D) may be acceptable. However, in the general case, appropriate
external drainage measures, e.g., greater excavation and replacement with porous or
drainable fill, may be justified.
After the site is tentatively located for the best available location and
drainage conditions, core samples must be taken of the soils which will lie under the
proposed parking area. Core depth should go down to the water table or
impermeable layer of rock or clay. If this is impractical, borings should extend to a
depth sufficient to indicate no barriers to vertical seepage of water. In most cases,
a maximum depth of 20 feet (6.1 m), should be adequate, or if the water table is
intersected prior to this, down to the water table. The soil borings must be
inspected for any soil layers of reduced permeability. If bedding planes are
horizontal, the permeability in the least permeable soil must be used as the soil
design permeability.
If the soil structure shown by adjacent soil borings is not similar, steeply
sloping or vertical, bedding plants, or previously disturbed soil (compacted fill, etc.)
may be indicated. In this case, an intensive soil boring program may be necessary to
assure no impermeable lenses or layers. In general, two cores may be all that is
required on small parking areas no greater than fe-acre (0.2 hectare) in extent.
On larger areas, the cores may be taken 100 to 150 feet (30.5 to 45.7m) apart.
However, prior experience and knowledge of the site (from foundation core analysis,
etc.) may dictate a less extensive program.
The core samples are used to determine soil structures and subsurface
characteristics including permeability and barriers to the movement of ground
water. If surface sealing, from silt accumulation or compaction by traffic, is
suspected, percolation tests may be required. These tests essentially define the
surface absorption capacity and permeability of the top layer of soil. However^as
mentioned previously, the least permeable layer of soil must be used to determine
the design permeability of the soil mass.
Soil core samples must also be tested for bearing and shear strength. All
strength and drainage tests must be conducted for dry (general) and saturated
(critical) conditions. Also, susceptibility to frost heave and loss of strength under
saturated conditions must also be determined.
32
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Load Bearing Design of Pavement and Subgrade
Final design of a porous pavement system requires the determination of the
total thickness of the porous pavement from top of pavement to subbase soil. This
thickness is influenced by the bearing strength, water storage required, and frost
depth. The greatest thickness determined by each of these conditions will be the
design thickness.
Bearing strength properties of different soils have been thoroughly investi-
gated by Franklin Institute Research Laboratories. Using the California Bearing
Ratio (CBR) test, all soils can be classified into four soil strength categories, as
listed in Table 5. The design traffic intensity may be divided into 3 groups, defined
by the average daily Equivalent Axle Load (EAL) and the minimum thickness for
each strength category and traffic intensity group defined. These results are
presented in Table 6.
As described previously, the total thickness of the paving system is a
combination of the open graded base course and the surface layer of open graded
asphalt mix.
Recent studies by the Federal Highway Administration (FHWA) indicated that
variations in asphalt content have little effect on Marshall and Hveem stabilities or
flow values. However, the importance of having at least some fine aggregate to
provide a "chocking" action for the stabilization of the porous aggregate fraction
must be recognized. Also, a minimum of 2 percent passing the Number 200 sieve
must be required to control the asphalt drainage characteristics of the mixture by
effectively increasing the viscosity of asphalt cement.
The Franklin Institute Research Laboratory and the FHWA recommended
gradation limits for aggregate mix as well as gradation limits developed by the U.S.
Army Corps of Engineers' Waterways Experiment Station (WES) and U.S. Naval
Facilities Engineering Command (NAVFAC) and others are listed in Table 7 along
with the slightly modified gradation limits proposed in this report. It can be seen
from the comparison of gradations in Table 7 that the Franklin Institute Research
Laboratories gradation allows slightly larger aggregate and more fines passing the
Number 8 sieve. However, it does not require any mineral filler passing the
Number 200 sieve or fines passing the Number 16 sieve. The gradation recom-
mendation herein is essentially similar to that recommended by the Franklin
Institute Research Laboratories, except that a minimum of two percent passing the
Number 200 sieve has been included.
The reasons for favoring the Franklin Institute Research Laboratories grada-
tions are as follows:
I. The experience with existing porous asphalt parking lots has been
generally good.
33
-------
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TABLE 7
AGGREGATE GRADATION LIMITS FOR POROUS ASPHALT MIXES
Sieve
Size
1/2"
3/8"
#*»
#8
#16
#200
1/2"
3/8"
#^
#8
#16
#200
13.2 mm
9.5 mm
6.7 mm
A. 75 mm
2.36 mm
1.18 mm
0.6 mm
0.3 mm
0.15 mm
0.075 mm
Gradation
Recommended
100
90-100
35 - 50
15 - 32
2-15
2-15
Newark,
Delaware
100
90 - 100
35 - 50
15 - 32
0-15
0-3
Perth
Austral ia
100
96
66
38
22
15
13
13
5
3
Percent Passing
Frank! in
. FHWA Institute
100
100 90-100
30 - 50 35 - 50
5-15 15-32
0-15
2-5 0-3
Chester Co., Greensboro, Dallas,
Pennsylvania N. Carolina Texas
100
100 100 90 _ 100
95 - 100 97 30-55
35 38 0-22
15 ]5.7 0-12
10 6.1 0-5
2 2.0
Note:
1 inch - 2.54 cm
-------
2. The FHWS, WES, and NAVFAC mixes are aimed at a thin overlay
over existing pavements, whereas the Franklin Institute Research
Laboratories mix has been placed in a thicker layer
graded base material.
over open
3. The primary objective of the FHWA open graded asphalt friction
course is removal of water from the surface of the pavement. The
objective of the Franklin Institute Research Laboratories porous
asphalt pavement, however, is to provide a porous and stable
surface over base material that essentially functions as a water
storage basin.
4. The traffic levels experienced by existing pavements using each
type of gradation have been different, although the Franklin
Institute gradation originated from California experience on
highways.
The approach to mix design taken from FHWA is aimed at testing the porous
aggregate to arrive at the surface coverage capacity, which includes absorption,
superficial area, and surface roughness. All of these properties affect the asphalt
cement requirement. A simple linear relationship obtained from field experience is
then applied to arrive at the percent asphalt that should both provide the necessary
cementation between particles and leave sufficient voids (the average FHWA goal is
a minimum of 15 percent voids as compared to Franklin Institute Research
Laboratories goal of 16 percent) while not creating excess asphalt that will drain or
cause flushing.
The relatively open spaces within a porous asphalt mix require that additional
resistance to oxidation, raveling, and retention of cementitious properties is
required of the asphalt binder. Consequently, the aggregate particle must be coated
with asphalt films in the range of 3 to 4 times those of conventional asphalt
concrete. The asphalt content used in porous friction courses has generally been
approximately 6.5 percent by weight. Initially, this content was selected to
minimize the probability of excess drainage asphalt. Also, the mixing temperature
was selected to be relatively higher than the temperature used for conventional
asphalt mixes. Table 8 lists the asphalt content recommended and used by various
agencies.
The Franklin Institute Research Laboratories mix design goals are similar to
those for a porous friction asphalt course, but the approach has been one of simply
applying a narrow band of asphalt content of 5.5 to 6 percent which has proven
effective for the aggregates tested.
In a recent innovation by Husky Oil Company, the tenacity, ductility,
toughness, and low and high temperature performance of asphalt has been sig-
nificantly enhanced by the addition of neoprene. This modified asphalt contains
37
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' TABLE 8
RECOMMENDED ASPHALT CONTENT FOR
POROUS ASPHALT MIXES
Thickness
Location Inches
Newark, Delaware
New Castle Co., Delaware
Chester Co., Pennsylvania
Newtown, Pennsylvania
Perth, Austral ia
Woodlands, Texas
Greensboro, N. Carolina
Dallas, Texas
2.5!
2-5
2.5
4.0
2.0
2.5
0.75
0.63
Asphalt
Content
%
5.5
6.0
5.0
5.0
5.0
6.0
6.5
6.5
Temperature
°F
275 -
275
240 -
212 -
300
280
240
•i ' "
300
280
257
M«,^«— —•— ^^£*~"
Notet 1 inch ^ 2.54 cm
32
38
-------
1.5 percent neoprene synthetic rubber which was specially formulated by the DuPont
Company for asphalt applications, and was used as a binder for the porous friction
courses at the Salt Lake City, Utah International Airport and Stapleton International
Airport in Denver, Colorado. It has been shown that neoprene has good aging
characteristics with high resistance to deterioration from ozone, sunlight, heat, and
weathering (16).
This product was tested at varying temperatures and asphalt content in a
porous friction course mix for the Greenboro-High Point-Winston-Salem Regional
Airport. The variations investigated and the resulting asphalt mix performance are
indicated in Table 9. Based on these results, the optimum asphalt binder content
was selected to be 6.5 percent and a mixing temperature of 300° F (I49°C) at a
viscosity of 275 centistokes (16).
When design construction actually proceeds on a specific porous asphalt
pavement, it is suggested that asphalt drainage tests such as those described by
FHWA be conducted on the recommended mix to establish the sufficiency of 5.5 to
6 percent asphalt content for the specific aggregate characteristics that will be
proposed for use. This approach will be much more direct than implementing the
detailed tests recommended by the FHWA for their open graded asphalt friction
course. ^ It will also provide a more positive approach than the general assumption
that a single asphalt cement content is sufficient for all aggregates.
Some other considerations in the preparation of the open graded asphalt
concrete mix are as follows:
I. Relatively dry aggregates should be used to avoid vapor release
after the aggregate is coated.
2. Problems of crusting on the surface of the truck load during haul
may be experienced; consequently, the use of insulated covers over
the load to avoid heat loss is recommended.
3. Most types of compaction equipment have been used successfully,
but medium to light weight vibratory rollers are somewhat better.
Also, the pavement has to be sufficiently cooled before rolling in
order to retain its shape.
4. The vibrating screed on laydown equipment is probably better for
this application than the tamping screed.
5. Damage from freeze thaw on this kind of pavement is minimal.
At present, this type of pavement system is almost completely outside the
experience of most pavement engineers and pavement contractors. Because the
classical need for high density and low air voids in conventional pavement is the
39
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TABLE 9
EFFECTS OF VARYING ASPHALT CONTENT AND MIXING
TEMPERATURES ON POROUS PAVEMENT MIXES (16)
Asphalt
Content
%
6.5
6.5
\S 9 ,S
6.5
6.5
6.75
7.0
Note: °F « J..8(°c;
Mixing ;
Temperature
Deg. F
280
300
320
300
300
300
) -J- 32
Comments
Satisfactory
Smoother laydown
Bleeding in laydown
machine hopper
Satisfactory
Satisfactory
Loss of mix consistency,
individual aggregate
could be separated from
mix
-------
direct opposite of the construction goal for porous pavement systems, previous
experience of both design and construction personnel is to some extent obviated.
The porous asphalt cement layer is recommended to be 2'/2 inches (6.35 cm) in
depth and the mix is to consist of the gradation previously recommended with 5.5 to
6.0 percent asphalt content initially. In order to obtain this close limit on asphalt
content, it is proposed to specify 5.75 percent and to establish a tolerance of
0.25 percent on asphalt. Because the usual tolerance is approximately 0.5 percent,
it is not certain that this low tolerance can be obtained; however, it is believed that
it will be more nearly accepted if this type of tolerance is exercised in the
specifications.
Compaction with light equipment must be applied on a closely observed basis
to avoid over-compaction and collapsing of pores during construction. This should
be carefully organized at the time of construction. Sample specifications presented
in Appendix A have been developed by combining features of tentative specifica-
tions developed by Franklin Institute Research Laboratories and the Texas Trans-
portation Institute.
Hydro logic Design of Pavement and Subgrade
The thickness for porous pavement systems required for the storage of water
may be determined from a dynamic mass balance of inflow to and outflow from the
R^oSA,P?^ment sXstem- As described in Sections, a computer model,
PORPAV(I7), has been developed by the USEPA to perform these calculations.
However, manual calculations are also feasible but very tedious. An oversimpli-
fication, in general use, substitutes a steady-state operation for the dynamic process
of inflow, storage, and outflow from the porous pavement system. Furthermore,
some of the earlier designs ignored soil permeability and determined the total
thickness of the porous pavement system to store all runoff from the design storm.
This last approach is too conservative, and not recommended for use at this time.
A very important consideration is the relative permeability of the base to the
subbase under the porous pavement. If the initial undisturbed permeability of the
subbase can be maintained during construction, then this permeability may be
expected to be available during operation of the porous pavement system. However,
if the subbase is compacted in any way, by design or inadvertently, a substantial loss
in permeability may be expected. Some studies have indicated that even sand can
be compacted to where its permeability is comparable to that of clay (14).
Consequently, potential porous pavement areas must be treated with due care prior
to and during construction to minimize subbase compaction at the site. Traffic or
material storage activities on the site should also be excluded.
The design for frost depth must consider both loss of strength due to freeze
thaw cycling and frost penetration, particularly in soils where more than 3 percent
of the particles are smaller than 0.02 mm in diameter. Table 10 lists the Franklin
-------
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Institute Research Laboratories recommendations for frost depth design thickness
for the 3 traffic groups previously described. The local frost penetration depth at
the proposed site must also be considered. This information is generally available in
the building codes of most municipalities and used primarily in foundation design.
The design storm, contributing areas, and soil permeability selected for a
given porous pavement design will determine the storage volume required in the
base. The selection of the design storm is in most cases dictated by local drainage
regulations, but more frequent (less intense) design storms may be selected if
adequate handling of runoff from storms in excess of the design storm is considered.
If the design storm is not specified by local regulation, a prudent choice must be
made after evaluating the consequences of flooding induced or exacerbated by the
proposed development. Areally large developments tend to create major flooding
problems ^during infrequent storms, but small developments do not generally impact
the existing drainage systems and more frequent storms may be selected for these
f-t*»f~\j-t ft
areas.
The contributing area to a porous pavement system may be dictated by the
design storm and local hydrologic conditions. In areas of long duration and intense
rainfall, the contributing area will be minimum. However, in more arid areas, where
rainfall is of short duration, the contributing area can be quite extensive. Another
factor to be considered is the nature of the contributing area, because pervious
and/or grassed uphill areas will not contribute as much runoff as impervious areas.
In practice, most contributing areas are rooftops, driveways, and other impervious
ground cover. Therefore, the design storm magnitude is generally the most
important criterion for hydrologic determination of porous pavement depth.
If the design storm and contributing area are pre-defined for a given drainage
area, and if the base storage capacity is physically or economically limited, drainage
relief measures may be incorporated into the system. These relief measures can
range from french drains and perforated pipe drains to underground cisterns.
However, the drain discharge must be properly disposed of, to the most convenient
drainageway, if only peak reduction of runoff is desired, or to a retention pond if
both peak and volume reduction are desired.
When the subbase permeability is relatively low (hydrologic soil group (C) or
(D)), a very thick base may be required to store the water, and residence time in
the base may be sufficiently long to develop undesirable side effects, like freezing
or anaerobic or septic water conditions. One solution would be to provide a relief
drain as described above, or, as in the case of The Woodlands, Texas site, a portion
of the subbase may be replaced with sand and drains located in the sand. On the
other hand, if a drainage channel is available nearby, a buried trench filled with the
same type base material as the porous pavement may be installed from the base
reservoir side to the channel, thereby providing an underground connection and flow
conduit.
-------
When the site is level, the rdin falling at a given spot stays in the reservoir
until it can percolate into the ground. However, when the site is sloped, the water
in the reservoir tends to flow to the lower areas, leaving the upper parts of the
reservoir empty and useless. Thus,; the low parts of the base should be thicker, to
hold more water, and the higher parts not thicker than necessary to handle the
mechanical loads.
The proposed slope df the pprous pavement should be reduced as much _ as
possible in order to utilize the base storage volume more efficiently. On any sloping
porous pavement or on a horizontal porous pavement with an artificially induced
hydraulic head at one end, e.g., inflow at one end only, a substantial flow may be
expected through the relatively open base course, and in the case of certain
pavements water may drain out of the pavement at the low end because lateral
movement is much faster than infiltration. This condition could be avoided by
reducing the slope, increasing the depth of the base course in the downstream
direction, and installing relief drains as previously described, or terracing the area
using cut-off walls under the pavement and concrete curbs on top of it. The latter
option is particularly effective on very steep slopes or very large areas where site
leveling would not be practical or economical.
Porous pavement, layed out on an existing low or moderate slope with
adequate base storage capacity, is the most ideal, aesthetic, and economical
solution because grading a site to be level can be very expensive. Also, the exposed
slopes draining onto the porous pavement must be stabilized to prevent eroded
materials from washing onto the pavement and clogging the pores.
Operation and Maintenance During and After Construction Activities
In general, operation and maintenance during and after construction of porous
pavements is minimal and most existing sites remain functional as designed.
However, one loss of porosity failure has been experienced at Bryn Mawr Hospital
near Philadelphia, Pennsylvania. The reason for this failure is discussed below.
Other failures could result from poor construction supervision, or lack of experience
with this product.
Experience with porous friction courses has indicated several other potential
problem areas. These include "cool down" time to allow the asphalt binder to set
prior to the regular operations on new construction. This problem was recognized at
the North Carolina Airport (16). Another problem can be the use of these porous
friction courses on steep (by Interstate Highway standards) grades, where heavy
trucks are required to brake. In this instance, the pores collapse and the gravel
aggregate may even come apart, resulting in a loss of pavement.
The porous asphalt will lose its porosity as a result of several factors, the most
important of which are listed below:
-------
I. Eroded soil and detritus being washed onto the pavement.
k
2. Construction materials being deposited or tracked in by construc-
tion equipment.
3. Washing of construction equipment, especially concrete trucks,
onto the pavement.
4. Finishing of concrete structures on, or adjacent to, the pavement.
5. Collapsed pores due to constant vehicle braking at the same spot
(entrance, exit, curves, etc.).
6. Collapsed pores resulting from rolling of hot open_ graded mix
before it is sufficiently cooled to resist the roller. Also, the
temperature of the hot mix at the site should not be so high that
the asphalt will drain away, thereby causing a loss of cemen-
tiousness.
It is obvious that with careful attention to construction scheduling, and close
supervision of site operations, as well as a regular maintenance program, all of these
problem areas can be avoided. Also, if a spill should occur, immediate corrective
measures should be taken. Vacuuming and jet spray washing will generally restore
the original pavement permeability.
Also, the use of curbs should be avoided because these can prevent wind
removal of site-generated or airborne influx materials (trash and leaves) common to
most parking lots. This factor is the major reason for the failure of the Bryn Mawr
lot.
Furthermore, Franklin Institute Research Laboratories have determined that
at some locations interficial surface tension of water on asphalt will cause the
pavement to temporarily become unable to absorb water. However, after the
pavement is thoroughly wet, full permeability will be restored.
In order to prevent any loss of permeability during the life cycle of the parking
lot, a regular maintenance program which includes vacuuming and jet spray washing
should be implemented. If substantial amounts of wind-borne materials are
expected to accumulate on the pavement surface and be washed into the base by
runoff, additional storage should be provided within the base for these materials.
The volume required for this type of storage must be determined from site
conditions and expected environmental conditions.
The greatest hazard to loss of porosity in porous pavement occurs during the
construction phase. During that time, an extensive portion of the area is not
protected from erosion and/or construction equipment. Therefore, special pre-
-------
cautions must be taken to prevent construction equipment from depositing or
tracking dirt onto the pavement, and to prevent sediment from adjacent hillsides
being washed onto the pavement. If this should occur, immediate vacuuming and jet
spray washing should be conducted.
To prevent sediment from being deposited on the pavement, sediment trap
fences or diversion ditches may be. installed around the pavement area. The
sediment fence could be filter material or fabric anchored in the ground and
supported by vertical stakes adequately spaced behind the fabric to support the
water pressure. A diversion ditch should be designed to have sufficient capacity to
remove all of the expected runoff and be able to maintain its grade below that of
the pavement. Also, the design velocity should not exceed the non-erodible velocity
for the channel lining material.
If at all possible, the installation of the porous pavement lot should be delayed
to be the last construction activity on the site. This approach would necessarily
involve additional soil erosion areas; during construction and these would require
further controls. However, the integrity of the porous pavement would be retained
at a much less diligent effort. Also, some protection may be necessary immediately
after construction. Once vegetation is established and most areas are stabilized,
the runoff should be devoid of excess sediment material.
-------
SECTION 8
COMPUTER MODEL FOR HYDROLOGIC DESIGN
The model developed In this project provides a comprehensive analysis of flow
and storage in porous pavements. Although the model is not very complex, limited
tests indicate that it can adequately quantify the hydrologic responses of a porous
pavement. Also, the effects of different pavement characteristics can be evalu-
ated. This allows for the investigation of various porous pavement systems to
determine the optimum system, particularly during planning phases of a project.
The hydrologic responses of a porous pavement may be simulated by a system
of hydraulically connected control volumes for which the inflows and outflows are
mathematically defined. The porous pavement, the base and the natural ground (or
the drain system) are considered to be sequential but internally independent storage
reservoirs.
The basic equation of continuity of conservation of mass is applied to each
reservoir:
where
0
ds
dt
- I _ o
dt~ ' u
inflow into the reservoir
outflow from the reservoir
-TT = change in storage volume
Inflows to the Porous Pavement System
As shown in Fig. 3, the porous pavement area would serve to control runoff
from contributing impervious areas. Therefore, inflow to the porous pavement
system, RUNOFF, is defined ass
where:
RUNOFF = PAY + HYD
PAV = direct rainfall onto the porous pavement
-------
LEGEND
RUNOFF FROM CONTRIBUTING
SUiAREAS, INFLOW
S$jV>« PREPARED EARTH (IF REQUIRED)
— EVAPORATION, OEVAP
STORAGE ON SURFACE, SURDEP
SURFACE RUNOFF, OSURF
HORIZONTAL OUTFLOW
THROUGH PAVEMENT, OHORP
HORIZONTAL OUTFLOW
THROUGH BASE, OHORS
,—LOCATION OF OPTIONAL
IMPERMIABLE MEMBRANE,
ISEAL
WATER TABLE OR DRAIN
WTER TABLE OR DRAIN
FIGURE 3 HYDROLOGIC MODEL PARAMETERS FOR POROUS PAVEMENTS
-------
HYD = surface runoff hydrograph from contributing areas
Contributing areas to the porous pavement will generally be developed and imper-
vious In nature. Consequently, the surface runoff hydrograph from contributing
areas is determined by use of the method developed by Izzard (18). This method,
selected for its programming ease, utilizes a dimensionless hydrograph from paved
areas as shown in Fig. 4. The key parameters in this method are time to
equilibrium, t ; equilibrium flow, q ; equilibrium surface detention volume, VG; the
intensity of rainfall, i; and the length of overland flow, L. The following equations
define these parameters:
wiL
%-43200
where:
L
w
= equilibrium flow, cfs
= rainfall intensity, inches per hour
= length of overland flow, feet
= width of overland flow, feet.
V =
e
Ll.33 jO.33
35J
where:
V = equilibrium surface detention volume, cu. ft.
k = an empirically derived, lumped coefficient for the effects of
slope and flow retardance of the pavement
V.
fe= 30 a
t = time to equilibrium, minutes
6
Using t/t values based on the computation Interval and Fig. 4, the q/q values
and the corresponding q values are determined for the rising limb of the hydrograph.
The 3 factor, defined as
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60
3 =
V
where
tQ = time after rainfall has ceased, minutes
VQ = equivalent to VG without the rainfall intensity component, cu.
TT»
is used to determine the q/q and corresponding q values for the recession limb of
the hydrograph. c
If.the duration of rainfall is greater than the time required to reach flow
equilibrium, (te
-------
where: :
K = permeability of flow element, ft/sec
a = cross-sectional area of surface water, sq ft
A = cross-sectional area of flow element, sq ft
L = thickness of flow element, ft
h I = depth of surface water at time 11, ft
h? = depth of surface water at time \<^ - 11 + A t, f t
These parameters are graphically depicted in Fig. 3.
In a porous pavement system, the cross-sectional areas of surface water and flow
elements are always equal, and so the equation is reduced to:
= 2.3
At
This equation may be rearranged to solve for r^ as follows:
. hl
where
E =
IOE
KAt
2.3L
Then, vertical seepage is equal to the change in water depth during At or,
OVERT = h, - h2
OHOR is the lateral outflow to a drain or into the natural ground as a result of
water storage in the base and pavement. This condition is analogous to bank
recharge from a rising stream. In most porous pavement systems, lateral outflow
will be negligible because OVERT »:OHOR. However if this condition is not met as
in Class C or D soils, then OHOR may be a significant factor. For a homogenous
isotropic aquifer of finite width, the influence of each increment of rise in the
stream is determined by the following set of equations (20):
d2h
dx
S dh
2 = T dt
52
-------
h(0,t) = 0 for t < 0
h(0,t)= AH. fort>0
dh(L,t)
dx
= 0
where
h
x
S
T
h(x,0) = 0
= hydraulic head or water depth, ft
= distance from boundary, ft
= coefficient of storage of aquifer
= aquifer transmissivity, cfs/ft
AH. = change in water depth at boundary, ft
L + distance to impermeable boundary or discharge point, ft.
AH. is the increase in stored water depth as a result of vertical drainage from
an upper storage volume (previous OVERT). If AH. is negative (after inflow has
ceased) water will drain back into the storage volume from the surrounding natural
ground. If AH. is 0 then OHOR = 0.
Integrate the first equation and apply boundary conditions to get:
dh
dx
S dh
T dt
The Darcy flow equation can be extended,by continuity to define net flow rate as
follows:
V = K
dx
53
-------
Q
dh
dh
where:
V
K
dh
dx
Q
A
h
w
q
T
= velocity of flow^ ft/sec
= permeability of flow element, ft/sec
= change in hydraulic grade, ft/ft
= total mass flow rate, cfs
= total flow area, sq. ft.
= depth of flow, ft.
= width of flow, ft.
= flow rate per unit width, cfs/ft
= transmissivity of flow element, cfs/ft
Then by substitution:
define:
S dh
dh
dt
h!-h;
At
forx- 1.0ft
and S is the storage coefficient of the natural ground. At a distance x from the
porous pavement boundary, the discharge per unit width is def ined\as:
q = S (-
h, - h.
At
Because the volume of flow remaining is the only item of interest, the value of x
was arbitrarily set equal to 1.0. Then, lateral outflow,
OHOR = q P At = S ( ' At 2) P At
-------
where:
= pavement perimeter, ft.
Figure 3 shows how these parameters apply to porous pavement areas. OSURF is
the surface runoff resulting from ponding on top of the porous lavement, which
occurs either because the inflow rate is greater than the porous pavement
permeability or the total storage capacity in the porous pavement system is
exceeded. The model requires a depth-storage relationship to determine when the
storage is exceeded. On a horizontal pavement, the model determines the depth-
storage relationship by use of input pavement and base depths and porosities; on a
sloping pavement, this relationship has to be independently computed and input to
the model.
The surface runoff from a horizontal pavement is defined by the weir
equation:
OSURF = CLH1'5
where?
C
L
H
h
0
= input weir coefficient
= input weir length, ft.
= h - hQ, ft.
= depth of dead surface storage on the porous pavement, ft.
= depth of flow on the porous pavement, ft.
On a sloping porous pavement, Manning's Equation is used to determine the surface
runoffs
where:
OSURF =
y!.33 S0.5
y = computed depth of flow, ft.
t = width of flow, ft,,
n = input roughness coefficient
s = input energy slope, ft/ft
55
-------
OEVAP is the volume of water lost to evaporation. This water loss is computed
during and after a storm if water remains on the surface i.e. the pavement is
flooded. Although the loss during a storm may be negligible, ponded surface water
loss after a storm may be significant particularly in arid climates.
Either monthly, weekly or daily evaporation rates may be input to the model;
the monthly and weekly rates are divided into average daily rates. The daily
evaporation rate may be increased by an input ratio to allow for heat absorption by
the dark asphalt. The model only allows for evaporation from 6 a.m. to 8 p.m., with
the maximum rate at 2 p.m. As shown in Fig. 5, a triangular distribution of
evaporation is developed by the model by use of the equation:
where:
EP = T
peak evaporation rate, in/hr
total daily evaporation, in
for 0 < t < 6, E = 0
t-«
for 14 < t < 20,
V 6
for 20 < t < 24, E = 0
C ""
where:
t = clock time, hours
C
E = instantaneous evaporation rate
Model Operation
The paths of-water flow through the porous pavement system are shown in
Fig. 3. For each computational time interval, all inflows and outflows are
accounted for. The total runoff hydrograph, in inches per computational time
interval, is either input to the model or may be computed as the sum of runoff
hydrographs from contributory areas and direct rainfall onto the pavement as
described previously.
56
-------
o
CL
§
LU
U_
O
10 r:
o
<
UJ
o:
15
X
i
a.
a.
£T
57
-------
The following sequential computational steps are -ihen performed:
I. Evaporation losses in inches per computational time interval are
computed and subtracted from the sum of the runoff depth and
previous surface storage, if any.
2. The volume of runoff after allowing for evaporation is compared to
the permeability in inches per time interval of the porous pave-
ment. In general, the permeability is much greater than the inflow
runoff rate and all of the water moves into the pavement control
volume. In those cases where the permeability has been severely
reduced and is less; than the runoff rate, the inflow into the
pavement and the excess is stored on the surface of the pavement
for later computation of surface runoff from the pavement.
3. The inflow into the pavement control volume is added to the
storage volume in the pavement and then compared to the per-
meability, in inches per computational time interval, of the base.
If the base permeability is greater than the inflow into the
pavement, then all of the flow is transferred into the base control
volume. This is true for most porous pavement systems operating
according to design. In those instances where the base per-
meability is less than the inflow volume, the inflow into the base is
computed as the vertical seepage into the base. The lateral
outflow from the pavement is also computed if an impermeable
membrane is not installed along the pavement perimeter. The
difference between the inflow into the pavement and the outflows
(vertical and lateral) from the pavement is stored in the pavement.
4. The inflow into the base control volume is added to the storage
volume in the base and then compared to the permeability in inches
per computational time interval, of the natural ground. If the
bottom is sealed with an impermeable membrane, then the per-
meability is set equal to zero, and no flow is lost to the natural
ground. The flow volume remaining in the base after vertical
seepage into the natural ground is compared to the drain capacity,
in inches per computational time interval. If the natural ground
permeability and/or drain capacity are inadequate to remove all of
the flow in the base, the vertical seepage into the natural ground
and drains, as well as the lateral outflow, if any, is computed. The
difference between the inflow into the base and the outflows
(vertical and lateral) from the base is stored in the base.
5. All stored volumes are compared to available volumes. If storage
volume in the base is exceeded, the excess is stored in the
pavement; if storage volume in the pavement is exceeded, the
-------
excess Is added to the surface storage on the pavement, if any
exists. Surface runoff is then computed either as broad channel
flow or weir flow from the pavement to an adjacent drainageway.
This computational procedure is repeated for every time interval in the inflow
hydrograph. The surface and drain outflows are stored in retrievable arrays. The
primary output objective is the surface runoff, if any. However, the other output
variables allow for a thorough examination of the hydraulic operational charac-
teristics of the porous pavement system, including the analysis of the desirability or
adequacy of the drains and the discharge rate from the drains.
59
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REFERENCES
I. Thelen, E., et al., "Investigations of Porous Pavements for Urban Runoff
Control," EPA 11034 DUY 03/72, U.S. Environmental Protection Agency,
Cincinnati, Ohio, 1972, 141 pp.
2. "When It Rains, It Pours Through the Pavement," Engineering News Record,
Oct. II, 1973, 38pp.
3. Diniz, E. V., and W. H. Espey, Jr., "Maximum Utilization of Water Resources
in a Planned Community - Application of the Storm Water Management
Model," EPA - 600/2-79-050C, U.S. Environmental Protection Agency, Cin-
cinnati, Ohio, 1979.
4. HoIIinger, R. H., "Maximum Utilization of Water Resources in a Planned
Community- Field Evaluation of Porous Paving," EPA- 600/2-79-050E,
U.S. Environmental Protection Agency, Cincinnati, Ohio, (pending publica-
tion). V
5. Diniz, E. V., "Water Quality Prediction for Urban Runoff - An Alternative.
Approach," Proceedings of the SWMM User's Group Meeting, EPA
600/9-79-026, U.S. Environmental Protection Agency, Washington, D.C.
1979. :
6. Sartor, J. D., and G. B. Boy;d, "Water Pollution Aspects of Street Surface
Contaminants," EPA-R2-72-08I, U.S. Environmental Protection Agency,
Cincinnati, Ohio, 1972.
7. Colston, N. V., Jr., and A. N. Tafuri, "Characterization and Treatment of
Urban Land Runoff," EPA - 620/2-74-096, U.S. Environmental Protection
Agency, Cincinnati, Ohio, 1974.
8. "Train Cites Need to Control Non Point Sources by Land Management,"
Clean Water Report, 1975, p. 212.
9. Brater, E. F., "Rainfall - Runoff Relations on Urban and Rural Areas,"
EPA - 670/2-75-046, U.S. Environmental Protection Agency, Cincinnati,
Ohio, I975i
10. Espey, W. H., Jr., et al., "A Study of Some Effects of Urbanization on Storm
Runoff from a Small Watershed," Technical Report HYD 07-6501, Center
for Research in Water Resources, University of Texas at Austin, 1965.
60
-------
11. McPherson, M. B., "Urban Runoff," Technical Memoir No. 18, ASCE Urban
Water Resources Research Program, 1972.
12. Jones, M. P., "Friction Overlay Improves Runway Skid Resistance," Civil
Engineering - ASCE, 1973, pp. 45-48.
13. Asphalt Institute Quarterly, October, 1957.
14. Cedergren, H. R., and K. A. Godfrey, Jr., "Water: Key Cause of Pavement
Failure?," Civil Engineering - ASCE, September, 1974, pp. 78-82.
15. Thelen, E., and L. F. Howe, "Porous Pavement," The Franklin Institute
Press, Philadelphia, Pennsylvania, 1978, 98 pp.
16. Johnson, E. A., and T. D. White, "Porous Friction Course Solves Airport
Hydroplaning Problem," Civil Engineering - ASCE, April, 1976, pp. 90-92.
17. Diniz, E. V., "Quantifying the Effects of Porous Pavements on Urban
Runoff," Proceedings of the National Symposium on Urban Hydrology,
Hydraulics, and Sediment Control, University of Kentucky, Lexington,
Kentucky, 1976.
18. Izzard, C.F. "Hydraulics of Runoff from Developed Surfaces," Proceedings
Highway Research Board, Vol. 26, pp. 129-150, 1946.
19. Taylor, D.W. "Permeability," Chapter 6 in Fundamentals of Soil Mechanics,
John Wiley & Sons, 1965.
20. Pinder, G.F., J.D* Bredehoeft, and H.H. Cooper, Jr. "Determination of
Aquifer Diffusivity from Aquifer Response to Fluctuations in River Stage,"
Water Resources Research, Vol. 5, No. 4, August 1969.
61
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APPENDIX A
SAMPLE SPECIFICATIONS FOR POROUS ASPHALT PAVEMENT
The following sample specifications are presented in this report to assist the
specification writer for whom porous pavement construction is a new area of
practice. These specifications will have to be tailored to individual area needs, but
sufficient detail is provided so that;only minimal changes will have to be made.
Consequently, these specifications may have to be reduced in some cases, but
precautions must be taken to assure that a contractor understands the exact scope
of work, particularly if this is the first attempt at porous pavement construction.
ITEM A: SUBGRADE PREPARATION FOR POROUS PAVEMENT
A.I DESCRIPTION
The work covered by this item consists of scarifying, Hading, and rolling the
subgrade to obtain a uniform texture and provide as nearly as practicable a uniform
density for the top six inches of the subgrade.
A.2 CONSTRUCTION METHODS
The subgrade shall be shaped in conformity with the typical sections shown on
the plans and to the lines and grades: established by the Engineer by the removal of
existing material or addition of approved material. All unsuitable or otherwise
objectionable material shall be removed from the subgrade and replaced with
approved material. All holes, ruts and depressions shall be filled with approved
material. The surface of the subgrade shall be finished to the lines and grades as
established, and be in conformity with the typical sections shown on the plans. Any
deviation in excess of one-half (fe) inch (1.27cm) cross-section and in a length of
sixteen (16) feet (4.9m) measured longitudinally shall be corrected by loosening,
adding, or removing material, reshaping and compacting by sprinkling and rolling if
required to attain but not exceed the density of the natural subgrade. Sufficient
subgrade shall be prepared in advance to ensure satisfactory prosecution of the
work. The contractor will be required to set blue tops for the subgrade on center-
line, at quarter points and curb lines at intervals not exceeding fifty (50) feet
(15.2m).
Material removed may be utilized in the addition of material to the subgrade
if approved by the Engineer. All other material required for the completion of the
subgrade shall also be subject to approval by the Engineer.
The type of equipment used in subgrade preparation construction shall not
cause undue subgrade compaction. Traffic over subgrade shall be kept at a
62
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minimum. Where fill is required, it shall be compacted to a density equal to the
undisturbed subgrade, and inherent soft spots corrected.
A.3 MEASUREMENT
All acceptable subgrade preparation will be measured by the square yard as
the area for the entire width of the roadway plus twelve inches (30.5 cm) behind
each curb for the entire length.
A.4 PAYMENT
This item shall be paid for at the contract unit price bid for "Subgrade
Preparation for Porous Pavement," which price shall be full compensation for all
work herein specified, including the furnishing of all materials, equipment, tools,
and labor and incidentals necessary to complete the work.
Payment shall be made under:
Pay Item No. 240:
Square Yard (m2).
Subgrade Preparation for Porous Pavement - Per
ITEM B: STONE BASE COURSE FOR STORMWATER STORAGE
B.I DESCRIPTION
"Stone Base Course for Stormwater Storage" shall consist of a foundation
course for surfacing, pavement or other base courses; shall be composed of crushed
stone or gravel, and shall be constructed as herein specified in two courses in
conformity with the typical sections shown on the plans and to the lines and grades
as established by the Engineer.
B.2 MATERIAL
The material shall be crushed as necessary to meet the requirements herein-
after specified, and shall consist of durable stone or gravel, crushed and/or screened
to the required particle size. The material shall be from approved sources.
Testing of flexible base materials shall be in accordance with the following
Texas Highway Department standard laboratory test procedures:
I) Preparation for Soil Constants and Sieve Analysis TEX-IOI-E
2) Sieve Analysis TEX-110-E
3) Wet Bail Mill TEX-M6-E
63
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Unless otherwise specified on the plops, all base material will be stockpiled after
crushed; tested by the testing agency designated by the City of and
approved by the City of prior !to being hauled to the project site.
The material, when properly tested, shall meet the following requirements:
Course
Stone Base Course
Stone Top Course
Sieve Size
Ife"
5/8"
3/8"
Retained on Sieve, Percent
0
100
0
100
Max. Wet Ball Mill
50
Unless otherwise shown on plans, the maximum increase in material passing the
Number 40 sieve resulting from the Wet Ball Mill Test shall not exceed 20.
B.3 CONSTRUCTION METHODS
(I) Preparation of Subgrade
The street shall be prepared and shaped in conformity with Item 240,
"Subgrade Preparation for Porous Pavement" and the typical sections
shown on plans and to the lines and grades as established by the
Engineer. The surface of the subgrade shall be finished to line and grade
as established and in conformity with the typical section shown on plans,
and any deviation in excess ;of In inch (0.6 cm) in cross-section and in a
length^ of 10 feet (3.0m) measured longitudinally shall be corrected by
loosening, adding or removing material and reshaping. Sufficient sub-
grade shall be prepared in advance to ensure satisfactory prosecution of
the work. Material excavated in the preparation of the subgrade shall be
utilized in the construction of slopes or otherwise disposed of as
directed, and any additional material required for the completion of
slopes shall be secured from sources indicated on plans or designated by
the Engineer. Blue tops shqll be set by the contractor for subgrade on
centerline, quarter points and curb lines at intervals not exceeding
50 feet (15.2m).
(2) Stone Base Course
Immediately before placing the stone base material, the subgrade shall
be checked as to conformity with grade and section.
The material shall be delivered in approved vehicles of a uniform
capacity and it shall be the charge of the Contractor that the required
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amount of specified material shall be delivered in each 100-foot (30.5 m)
station.
Stone base course shall be laid over a dry subgrade to the depth shown in
drawings, in lifts to lay naturally compacted. The stone base course is
not to be rolled or compacted and is to be kept clean from debris, clay,
and eroding soil.
(3) Stone Top Course
This course is to be two inches in depth. Construction methods shall be
the same as prescribed for the stone base course. Blue tops shall be set
by the contractor for finished base grade on center-line and intermediate
points not exceeding 11 feet (3.4 m) between points at 50-foot (15.2 m)
intervals.
B.4 MEASUREMENT
"Stone Base Course" including the "Stone Top Course" will be measured by the
square yard (m ) at depths specified in the proposal for the area of Parking Lot as
shown on the typical sections of the plans or otherwise provided for in the contract
documents, complete irx place; by the cubic yard (m ), loose vehicle measurement;
or by the cubic yard (m ), complete in place, as indicated in the proposal.
B.5 PAYMENT
This item will be paid for at the contract unit price bid for "Stone Base
Course," which price shall be full compensation for all work herein specified,
including the furnishing, hauling, and placing of all materials, for all water required
and for all equipment, tools, labor and incidentals necessary to complete the work.
Payment will be made under:
Pay Item No. 250-A^ Stone Base Course (complete in place) - Per
Square Yard (m ), or
Per Item No. 250-B: Stone Base Course (loose vehicle measurement)-
Per Cubic Yard (m ), or
Pay Item No. 250-C: Stone Base Course (complete in place) - Per Cubic
Yard (mJ).
* This item must be verified for local requirements and site conditions.
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ITEM C: HOT MIX POROUS ASPHALT PAVEMENT '
C.I DESCRIPTION
This item shall consist of a surface course as shown on the plans, composed of
a lightly compacted mixture of mineral aggregate and asphaltic material.
The pavement shall be constructed on the previously completed and approved
subgrade and stone base course as herein specified and in accordance with the
details shown on the plans.
C.2 MATERIALS
(I) Coarse Aggregate
The mineral aggregate shall be composed of a coarse aggregate, a fine
aggregate, and if required, a mineral filler. Samples of coarse aggregate
and mineral filler shall be submitted for testing as directed by the
Engineer and approval of.both material and of the source of supply must
be obtained from the Engineer prior to delivery.
(a) Coarse Aggregate
Coarse aggregate shall be that part of the aggregate retained on
the No. 8 sieve; shall consist of clean, tough, durable fragments of
crushed stone, or crushed gravel, as hereinafter specified of
uniform quality throughout.
When the coarse aggregate is tested in accordance with Test
Method Tex-217-F* (Part I, Separation of Deleterious Material),
the amount of organic matter, clay, loam or particles coated
therewith or other undesirable materials shall not exceed two
percent and when remaining part of the sample is further tested in
accordance with Test Method Tex-127-F* (Part II, Decantation),
the amount of material removed shall not be more than two
percent.
The coarse aggregate shall have an abrasion of not more than forty
percent loss by weight when subjected to the Los Angeles Abrasion
Test, Test Method Tex-410-A*.
Unless specified otherwise, gravel shall be so crushed that seventy-
five percent of the particles retained on the No. 4 sieve shall have
more than one crushed face when tested in accordance with Test
Method Tex-413-A* (Particle Count).
66
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(b) Fine Aggregate
The fine aggregates shall be that part of the aggregate passing the
No. 8 sieve and shall consist of sand, screenings, or combination
thereof as hereinafter specified of uniform quality throughout.
Fine aggregate shall consist of durable particles, free from injur-
ious foreign matter. Screenings shall be of the same or similar
materials as specified for coarse aggregate. The plasticity index
of that part of the fine aggregate posing the No. 40 sieve shall be
not more than 6 when tested in accordance with Test Method
Tex-106-E*. Fine aggregate from each source shall meet plas-
ticity requirements.
Where stone screenings are specified for use, the stone screenings
shall meet the following grading requirements unless otherwise
shown on plans:
Passing the fe" Sieve
Passing the No. 200 Sieve
Percent by Weight
100
10-30
When authorized by the Engineer, stone screenings containing
particles larger than fe" may be used but only that portion of the
material passing the 3/8" sieve shall be considered as fulfilling the
requirements for screenings when a minimum percentage of
screenings is specified for a particular mixture.
(c) Mineral Filler
Mineral filler shall consist of thoroughly dry stone dust, slate dust,
Portland cement, fly ash or other mineral dust approved by the
Engineer. The mineral filler shall be free from foreign and other
injurious matter.
When tested by Test Method Tex-200-F* (Dry Sieve Analysis), it
shall meet the following grading requirements:
Passing a No. 30 Sieve
Passing a No. 80 Sieve, not less than
Passing a No. 200 Sieve, not less than
Percent by Weight
95 to 100
75
55
67
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(2) Asphaltic Material for Porous Asphalt Paving Mixture
Asphalt for the paving mixture shall be asphalt cement, viscosity grade
AC-20* and shall meet the requirements of the Item, "Asphalts, Oil and
Emulsions." The Contractor shall notify the Engineer of the source of
his asphaltic material pri6r to production of the asphaltic mixture and
this source shall not be changed during the course of the project except
on written permission of the Engineer.
The paving mixture shall consist of a uniform mixture of coarse
aggregate, fine aggregate, asphaltic material and mineral filler, if
required.
The grading of each constituent of the mineral aggregate shall be such as
to produce, when properly proportioned, a mixture which, when tested in
accordance with Test Method Tex-200-F* (Dry Sieve Analysis), will
conform to the limitations for master grading given below:
Passing fe" Sieve
Passing 3/8" Sieve, Retained on No. 4 Sieve
Passing No. 4 Sieve, Retained on No. 8 Sieve
Passing No. 8 Sieve, Retained on No. 16 Sieve
Passing No. 16 Sieve^ Retained on No. 200 Sieve
Passing No. 200 Siev^
Percent by Weight
100
40-65
3-35
1-20
0-10
2-5
The asphaltic material shall form from 5.5 to 6.0 percent of the mixture
by weight unless specified Otherwise on the plans.
The Engineer will designate the exact grading of the aggregate and
asphalt content, within the above limits, to be used in the mixture. The
paving mixture produced should not vary from the designated grading and
asphalt content by more 'than the tolerances allowed herein; however,
the mixture produced shall conform to the limitations for master grading
specified above.
Passing fe" Sieve, Retained on 3/8" Sieve
Passing 3/8" Sieve, Retained on No. 4 Sieve
Passing No. 4 Sieve,'Retained on No. 8 Sieve
Total Retained on No. 8 Sieve
Passing No. 8 Sieve, Retained on No. 16 Sieve
Passing No. 16 Sieve, Retained on No. 200 Sieve
Passing No. 200 Sieve
Asphalt Material
Percent
by Weight
±5
+ 5
+ 5
±5
+ 3
+ 3
±3
+ 0.25
68
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Should the paving mixture produced vary from the designated grading
and asphalt content by more than the above tolerances, proper changes
are to be made until it is within these tolerances.
Samples of the mixture when tested in accordance with Test Method
Tex-210-F* shall not vary from the grading proportions of the aggregate
and the asphalt content designated by the Engineer by more than the
respective tolerances specified above and shall be within the limits
specified for master grading.
C.3 EQUIPMENT
(I) Mixing Plants
Mixing plants that will not continuously meet all the requirements of this
specification shall be condemned.
Mixing plants may be either the weight-batching type or the continuous
mixing type. Both types of plants shall be equipped with satisfactory
conveyors, power units, aggregate handling equipment, aggregate screens
and bins and shall consist of the following essential pieces of equipment:
(a) Weight-Batching Type
Cold Aggregate Bin and Proportioning Device. The cold aggregate
bins or aggregate stockpiles shall be of sufficient number and size
to supply the amount of aggregate required to keep the plant in
continuous operation. The proportioning device shall be such as
will provide a uniform and continuous flow of aggregate in the
desired proportion to the plant.
Dryer. The dryer shall be of the type that continually agitates the
aggregate during heating and in which the temperature will be so
controlled that aggregate will not be injured in the necessary
drying and heating operations required to obtain a mixture of the
specified temperature.
The burner, or combination of burners, and type of fuel used shall
be such that in the process of heating the aggregate to the desired
or specified temperatures, no residue from the fuel shall adhere to
the heated aggregate.
A recording thermometer shall be provided which will record the
temperature of the aggregate when it leaves the dryer. The dryer
shall be of sufficient size to keep the plant in continuous operation.
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Screenings and Proportioning. The screening capacity and size of
the bins shall be sufficient to screen and store the amount of
aggregate required to properly operate the plant and keep the plant
in continuous operation at full capacity. Proper proportions shall
be made to enable inspection forces to have easy and safe access
to the proper location on the mixing plant where accurate repre-
sentative samples of aggregate may be taken from the bins for
testing. Separation of hot bin into compartments will not be
required providing uniform grading and asphalt content are con-
sistently produced in the completed mix.
Aggregate Weigh Box and Batching Scales. The aggregate weigh
box and batching scales shall be of sufficient capacity to hold and
weigh a complete batch of aggregate. The weigh box and scales
shall conform to the requirements of the Item, "Weighing and
Measuring Equipment."
Asphaltic Material Bucket and Scales. The asphaltic material
bucket and scales shall be of sufficient capacity to hold and weigh
the necessary asphaltic material for one batch. If the material is
measured by weight, the bucket and scales shall conform to the
requirements of the jtem, "Weighing and Measuring Equipment.
If a pressure type flow meter is used to measure the asphaltic
material, the requirements of the Item, "Weighing and Measuring
Equipment" shall apply.
Mixer. The mixer shall be of the pug mill type and shall have a
Capacity of not less than 20 cubic feet (0.57 rrO unless otherwise
shown on the plans. The number of blades and the position of same
shall be such as to give a uniform and complete circulation of the
batch in the mixer. The mixer shall be equipped with an approved
spray bar that will I distribute the asphaltic material quickly and
uniformly throughout the mixer. Any mixer that has a tendency to
segregate the mineral aggregate or fails to secure a thorough and
uniform mixing with the asphaltic material shall not be used. This
shall be determined by mixing the standard batch for the required
time, then dumping the mixture and taking samples from its
different parts. This will be tested by the extraction test and must
show that the batch is uniform throughout. All mixers shall be
provided with an automatic time lock that will lock the discharge
doors of the mixer -jfor the required mixing period. The dump door
or doors and the shaft seals of the mixer shall be tight enough to
prevent spilling of aggregate or mixture from the pug mill.
70
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(b) Continuous Mixing Type
Cold Aggregate Bin and Proportioning Device. Same as for
weight-batching type of plant.
Dryer. Same as for weight-batching type of plant.
Screening and Proportioning. Same as for weight-batching type of
plant.
Aggregate Proportioning Device. The hot aggregate proportioning
device shall be so designed that when properly operated a uniform
and continuous flow of aggregate into the mixer will be main-
tained.
Asphaltic Material Spray Bar. The asphaltic material spray bar
shall be designed such that the asphalt will spray uniformly and
continuously into the mixer.
Asphaltic Material Meter. An accurage asphaltic material re-
cording meter shall be placed in the asphalt line leading to the
spray bar so that the cumulative amount of asphalt used can be
accurately determined. Provisions of a permanent nature shall be
made for checking the accuracy of the meter output. The asphalt
meter and line to the meter shall be protected with a jacket of hot
oil or other approved means to maintain the temperature of the
line and meter near the temperature specified for the asphaltic
material.
If a pressure type flow meter is used to measure the asphaltic
material, the requirements of the Item "Weighing and Measuring
Equipment" shall apply.
Mixer. The mixer shall be of the pug mill continuous type and
shall have a capacity of not less than 40 tons (36.3 Mg metric ton)
of mixture per hour. Any mixer that has a tendency to segregate
the aggregate or fails to secure a thorough and uniform mixing of
the aggregate with the asphaltic material shall not be used. The
dam gate at the discharge end of the pug mixer and/or pitch of the
mixing paddles shall be so adjusted as to maintain a level of
mixture in the pug mixer between the paddle shaft and the paddle
tips (except at the discharge end).
Truck Scales. A set of standard platform truck scales, conforming
to the Item, "Weighing and Measuring Equipment," shall be placed
at a location approved by the Engineer.
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(2) Asphaltic Material Heating Equipment
Asphaltic material heating equipment shall be adequate to heat the
amount of asphaltic material required to the desired temperature.
Asphaltic material may be heated by steam coils which shall be
absolutely tight. Direct fire heating of asphaltic material will be
permitted, provided the heater used is manufactured by a reputable
concern and there is positive circulation of the asphalt throughout the
heater. Agitation with steam or air will not be permitted. The heating
apparatus shall be equipoped with a recording thermometer with^ a
24-hour chart that will record the temperature of the asphaltic material
at the highest temperature.
(3) Spreading and Finishing Machine
The spreading and finishing machine shall be of a type approved by the
Engineer, shall be capable of producing a surface that will meet the
requirements of the typical cross-section and a surface test, when
required, and when the mixture is dumped directly into the finishing
machine shall have adequate power to propel the delivery vehicles m a
satisfactory manner. The finishing machine shall be equipped with a
flexible spring and/or hydraulic type hitch sufficient m design and
capacity to maintain contact between the rear wheels of the hauling
equipment and the pusher rollers of the finishing machine while the
mixture is being unloaded.
The use of any vehicle which requires dumping directly into the finishing
machine and which the finishing machine cannot push or propel in such a
manner as to obtain the desired lines and grades without resorting to
hand finishing will not be allowed.
Automatic screed controls, if required, shall meet the requirements of
the Item, "Automatic Screed Controls for Asphaltic Concrete Spreading
and Finishing Machines."
(4) Pneumatic Tire Rollers
The rollers shall be acceptable light pneumatic tire rollers conforming to
the requirements of the Item, "Rolling (Pneumatic Tire)," unless other-
wise specified on plans.
The tire pressure of each tire shall be adjusted as directed by the
Engineer' and this pressure shall not vary by more than 5 pounds per
square inch (34.5 kP2, kilo pascal).
72
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(5) Two Axle Tandem Roller
This roller shall be an acceptable power driven tandem roller weighing
not less than 6 tons (5.4 Mg), or more than 10 tons (9.1 Mg).
(6) Three Wheel Roller
This roller shall be an acceptable power driven three wheel roller
weighing not more than 10 tons (9.1 Mg).
(7) All Equipment shall be maintained in good repair and operating condition
and shall be approved by the Engineer.
(8) Alternate Equipment
When permitted by the Engineer, in writing, equipment other than that
specified, which will consistently produce satisfactory results, may be
used.
C.4 STOCKPILING, STORAGE, PROPORTIONING AND MIXING
(I) Aggregate Storage
If the mineral aggregates are stored or stockpiled, they shall be handled
in such a manner as to prevent segregation, mixing of the various
materials or sizes, and contamination with foreign materials. The
grading of aggregates proposed for use and as supplied to the mixing
plant shall be uniform. Suitable equipment of acceptable size shall be
furnished by the Contractor to work the stockpiles and prevent segre-
gation of the aggregates.
(2) Storage and Heating of Asphaltic Materials
The asphaltic material storage shall be ample to meet the requirements
of the plant. Asphalt shall not be heated to a temperature in excess of
that specified in the Item, "Asphalts, Oils and Emulsions." All equipment
used in the storage and handling of asphaltic material shall be kept in a
clean condition at all times and shall be operated in such a manner that
there will be no contamination with foreign matter.
(3) Feeding and Drying of Aggregates
The feeding of various sizes of aggregate to the.dryer shall be done
through the cold aggregate bin and proportioning device in such a manner
that a uniform and constant flow of materials in the required proportions
will be maintained. When specified on the plans, the cold aggregate bins
73
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shall be charged by use of a clamshell, dragline, shovel or front end
loader. The aggregate shall be dried and heated to the temperature
necessary to produce a mixture having the specified temperature.
(4) Proportioning
The proportioning of the various materials entering the asphaltic mixture
shall be as directed by the Engineer and in accordance with these
specifications. Aggregate shall be proportioned by weight using the
weigh box and batching scales herein specified when the weight-batch
type of plant is used and by volume using the hot aggregate proportioning
device when the continuous mixer type of plant is used. The asphaltic
material shall be proportioned by weight or by volume based on weight
using the specified equipment.
(5) Mixing
(a) Batch Type Mixer
In the charging of the weigh box and in the charging of the mixer
from the weigh box, such methods or devices shall be used as are
necessary to secure a uniform asphaltic mixture. In introducing
the batch into the mixer, the mineral aggregate shall be introduced
first; shall be mixed;thoroughly for a period of 5 to 20 seconds, as
directed, to uniformly distribute the various sizes throughout the
batch before the asphaltic material is added; the asphaltic material
shall then be added and the mixing continued for a total mixing
period of not less than 30 seconds. This mixing period may be
increased if, in the ppinion of the Engineer, the mixture is not
uniform.
(b) Continuous Type Mixer
The amount of aggregate and asphaltic material entering the mixer
and the rate of travel through the mixer shall be so coordinated
that a uniform mixture of the specified grading and asphalt content
will be produced. Checks on asphalt used shall be made at least
twice daily by comparing the asphalt used in ten loads of com-
pleted mix as shown on the asphalt recording meter and the design
amount for these ten loads. The acceptable percent of variation
between the asphalt used and the design amount will be as shown
on the plans or as determined by the Engineer.
(c) The Mixture produced from each type of mixer shall not vary from
the specified mixture by more than the tolerances herein specified.
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(d) The Surface Mixture from each type of mixer will not exceed a
temperature of 260 F (127° C) and shall be specified by the
Engineer. The temperature of the mixture will not be lower than
180° F (82° C) when placed on the road.
C.5 CONSTRUCTION METHODS
(I) The surfacing mixture shall not be placed when the air temperature is
below 50 F (10 C) and is falling, but it may be placed when the air
temperature is above 40° F (4° C) and rising. The air temperature shall
be taken in the shade away from artificial heat. It is further provided
that the surfacing mixture shall be placed only when the humidity,
general weather conditions and temperature and moisture condition of
the pavement surface, in the opinion of the Engineer, are suitable.
(2) Transporting the Surface Mixture
, The mixture, prepared as specified above, shall be hauled to the work in
tight vehicles with smooth dump beds that have been previously cleaned
of all foreign material. The dispatching of vehicles shall be arranged so
that all material delivered may be placed, and all rolling shall be
completed during daylight hours. In cool weather or for long hauls,
canvas covers and insulating of the truck bodies may be required. The
inside of the truck body shall be sprayed with a non-petroleum relase
agent satisfactory to the Engineer, if necessary, to prevent the mixture
from adhering to the body.
(3) Placing
The asphaltic mixture shall be dumped directly into the specified
spreading and finishing machine and spread on the approved prepared
surface in such a manner that, when properly compacted, the finished
surface will be smooth and of uniform texture and density. The
spreading and finishing machine shall be operated at a speed satisfactory
to the Engineer. During application of asphaltic material, care shall be
taken to prevent splattering of adjacent pavement, curb and gutter and
structures.
(4) Compacting
(a) As directed by the Engineer, the surface mixture shall be com-
pressed lightly and uniformly with the specified rollers and/or
other approved rollers.
(b) Compaction of the surface course shall be done while the surface is
cool enough to resist the roller used. One or two passes by the
75
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roller Is all that is required, as excess rolling could cause a
reduction in surface course porosity.
(c) The motion of the rollers shall be slow enough at all times to avoid
displacement of the mixture. If any displacement occurs, it shall
be corrected at once by the use of rakes and of fresh mixture
where required. To prevent adhesion of the surfacing mixture to
the roller, the wheels shall be kept thoroughly moistened with a
soap-water solution. Necessary precautions shall be taken to
prevent the dropping of gasoline, oil, grease or other foreign
matter on the pavement, either when the rollers are in operation or
when standing.
(5) Surface Tests
i
The surface of the pavement, after compaction, shall be smooth and true
to the established line, grade and cross-section, and when tested with a
10-foot (3.0 m) straight-edge, the maximum deviation shall not exceed
& inch (6mm) in 10 feet (3.0m), and any point in the surface not
meeting this requirement shall be corrected as directed by the Engineer.
The completed surface shall meet the approval of the Engineer for riding
surface finish and appearance.
(6) After final rolling, no vehicular traffic of any kind shall be permitted on
the porous pavement until cooling or hardening has taken place, as
directed by the Engineer, but in no case less than six hours.
C.6 MEASUREMENT
(1) The surfacing mixture ;will be measured separately by the ton of
2,000 pounds (907 kilograms, Kg) of "Asphalt" and by the cubic yard of
dry, loose "aggregate" o'f the type actually used in the completed and
accepted work in accordance with the plans and specifications for the
project. The volume of aggregate in the compacted mix shall be
calculated from the measured weights of the surfacing mixture by use of
the following formula:
V =
(W-A)
(27)K
V
W
A
K
Cubic Yards of aggregate, dry, loose
Total weight of surfacing mixture in pounds (Kg)
Weight of Asphalt in pounds (Kg) o
Unit Weight of Aggregate in pounds per cubic foot (Kg/m )
76
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The value "K" shall be the average of two or more tests determined by
the Engineer in the following manner:
At the beginning of plant operations, a specified weight of dried mineral
aggregate shall be placed in an acceptable container that will contain a
minimum volume of three cubic yards (2.3 mj). The aggregate shall be
leveled or "struck-off" and measured, to determine the volume of the
mineral aggregate, in cubic feet (mj). The unit weight of the mineral
aggregate shall be obtained by dividing the specified weight of dried
aggregate in pounds (Kg) by the measured volume in cubic feet (m ).
The value "K" is an average of two or more of the above-described tests.
The value "K" shall be .checked a minimum of one time for each
3,000 cubic yards (2,294 m ) of mineral aggregate. If, in the opinion of
the Engineer or the Contractor's representative, the value of "K" has
changed, a check test shall be made. A new value for "K" shall be
determined if the checked value of "K" varies more than two percent
(plus or minus) from the value being used.
The weight, "W," if mixing is done by a continuous mixer, will be
determined by truck scales. The weight, if batched, will be determined
on batch scales and records of the number of batches, batch designs and
weight of "Asphalt" and "Aggregate" shall be kept.
C.7 PAYMENT
(I) The work performed and materials furnished as prescribed by this item
and measured as provided under "Measurement," will be paid for at the
unit prices bid for "Asphalt" and "Aggregate," of the types specified,
which prices shall each be full compensation for quarrying, furnishing all
materials and freight involved; for all heating, mixing, hauling, cleaning
the existing pavement, placing asphalt-aggregate surfacing mixture,
rolling and finishing; and for all manipulations, labor, tools, equipment
and incidentals necessary to complete the work.
(2) All templates, straight-edges, scales and other weighing and measuring
devices necessary for the proper construction, measuring and checking of
the work shall be furnished, operated and maintained by the Contractor
at his expense.
* This item must be verified for local requirements and site conditions.
77
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TECHNICAL REPORT DATA
(Please read Instructions on the reverse before completing)
1. REPORT NO.
EPA-600/2-80-155
3. RECIPIENT'S ACCESSION NO.
4. TITLE AND SUBTITLE
Porous Pavement; Phase I
Design and Operational Criteria
5. REPORT DATE
August 1980
(Issuing Date)
6. PERFORMING ORGANIZATION CODE
7. AUTHOR(S)
Elvidio V. Diniz
8. PERFORMING ORGANIZATION REPORT NO
9. PERFORMING ORGANIZATION NAME AND ADDRESS
10. PROGRAM ELEMENT NO.
City of Austin
P.O. Box 1088
Austin, Texas 78767
35 BIG, Task No. 415225
11. CONTRACT/GRANT NO.
R806338
I 2. SPONSORING AGENCY NAME AND ADDRESS
Municipal Environmental Research Laboratory— c in.
Office of Research and Development
U.S. Environmental Protection Agency
Cincinnati. Ohio 45268 __
Oh
13. TYPE OF REPORT AND PERIOD COVERED
Final. 2/1/79 - 8/1/79
14. SPONSORING AGENCY CODE
EPA/600/14
15. SUPPLEMENTARY NOTES
Project Officer: Hugh Masters (201)321-6678, FTS 340-6678
1C. ABSTRACT
Design and operational criteria, utilization concepts, benefits and disadvantages, as
well as other characteristics of porous pavements are presented in this report. Par-
ticular emphasis is placed on porous asphalt pavements, but the criteria and design
approach are applicable to all other porous pavement types.
The_design considerations presented in this report include siting problems, load bearing
design, and hydrologic design. A brief history of porous pavement development and pre-
vious experience with porous pavement by several designers, contractors, and operators
are described.
A computer model for hydrologic performance evaluation of existing or proposed porous
pavement systems is also described in this report. Load bearing design criteria are
based on previous work conducted for porous asphalt pavements.
Appendices to this report include a sample set of specifications for porous asphalt
construction and a list of soils and their permeability classes as prepared by the U.S.
Soil Conservation Service.
17.
KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
b.lDENTIFIERS/OPEN ENDED TERMS C. COSATI Field/Group
Pavements, Pavement bases, Porous materials,
Asphalt pavements, Urban land use, Urban
planning, Design criteria
Porous pavements,
Urban runoff control,
Asphalt concrete
13B
18. DISTRIBUTION STATEMENT
Release to Public
19. SECURITY CLASS (ThisReport)
Unclassified
21. NO. OF PAGES
99
20. SECURITY CLASS (Thispage)
.Unclassified
22. PRICE
EPA Form 2220-1 (Rev. 4-77)
87
* U.S. GOVERNMENT PRINTING OFFICE: 1980-657-165/014Z
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