MICROWAVE PROCESSING UNIT FOR PAVEMENT RECYCLING AND ASPHALT PAVEMENT PRODUCTION

Abstract
An asphalt plant for producing a high performance hot mix asphalt product, comprising: RAP material, emulsion added to the RAP, and low energy microwave heating system for processing the RAP emulsion mix.
Description
BACKGROUND OF THE INVENTION

1. Field of the Invention


The present invention is in the technical field of asphalt production. More particularly, the present invention relates to the use of microwave energy in the production of asphalt products.


2. Background


Prior art asphalt production plants have remained virtually unchanged for decades (see FIG. 1). Asphalt cement and aggregate are combined in a mixing facility where they are heated, proportioned, and mixed to produce the desired paving mixture. Hot-mix asphalt (“HMA”) facilities may be permanently located (also called “stationary” facilities), or it may be portable and moved from job to job. Hot-mix facilities may be classified as either a batch facility or a drum-mix facility; both can be either stationary or portable. Batch-type hot-mixing facilities use different size fractions of hot aggregate which are drawn in proportional amounts from storage bins to make up one batch for mixing. The combination of aggregates is dumped into a mixing chamber called a pugmill. The hot liquid asphalt, which has also been weighed, is then thoroughly mixed with the aggregate in the pugmill. After mixing, the material it is then emptied from the pugmill into trucks, storage silos, or surge bins. The drum-mixing process heats and blends the aggregates with asphalt all at the same time in the drum mixer. Typically $500-$700 or more of natural fuels are burned for every hour of production. When mixing is complete, the hot-mix is then transported to the paving site and spread with a paving machine in a partially compacted layer to a uniform and even surface layer. While still hot, the paving mixture is further compacted by heavy rolling machines to produce a smooth pavement surface.


Heat used in the production of hot-mix asphalt is one of the main targets in efforts to reduce the energy profile and environmental impact of such facilities. Prior art facilities consume large amounts of energy and produce substantial amounts of pollutants. In recent years the development of WMA or warm mix asphalt was developed as a solution, but this solution suffers from a number of drawbacks. While hot-mix asphalt is produced at 350 to 400 degrees, WMA is produced at 300 degrees, which still requires enormous energy and produces only incrementally less pollutants. While these mixes show slight promise more information is needed to draw definitive conclusions regarding their effectiveness and performance as pavemet, but WMA does not does not fundamentally solve the underlying problems associated with asphalt production.


Another problem with current asphalt production, especially with hot-mix asphalt, is it is produced using very little recycled pavement material (“RAP”). As RAP is harvested from roadways or parking lots only a small amount will be used in new HMA production. Current nationwide standards show new HMA to contain anywhere from 20% to 35% of RAP in the HMA mix design. In most cases higher amounts of RAP causes a decline in new HMA performance. As the years go by RAP piles continue to grow faster than material can be utilized in HMA. In several regions RAP is used as base material for roadways.


Thus, a need exists for an improved asphalt product and method of producing asphalt that does not suffer from the drawbacks and disadvantages of the prior art.


SUMMARY OF THE INVENTION

An object of the present invention is to provide an improved apparatus and method for an asphalt plant for producing a high performance hot mix asphalt product, comprising, RAP material, emulsion added to the RAP, and low energy microwave heating system for processing the RAP emulsion mix. These and other objects of the present invention will become apparent to those skilled in the art upon reference to the following specification, drawings, and claims.





BRIEF DESCRIPTION OF THE DRAWINGS


FIG. 1 is a drawing of a prior art asphalt plant.



FIG. 2 is a depiction of the steps of a process of producing high performance hot mix asphalt (“HMA”) in accordance with the present invention. The drawing on the left depicts recycled asphalt pavement (“RAP”) material (up to 100%) from roadways or parking lots; the drawing in the center depicts a sized and injected engineered emulsion, which can constitute about 5% of the product; and the drawing on the right depicts a fused high performance HMA.



FIG. 3 is a block flow diagram of LEAP Process.



FIG. 4 is a drawing of a portion of a microwave heating system used in accordance with the present invention.



FIG. 5 is a floor plan.



FIG. 6 is a floor plan.



FIG. 7 is a rendering of a LEAP plant.



FIG. 8 is a floor plan.



FIG. 9 is a graph of LEAP Rut Test Results.





DETAILED DESCRIPTION OF THE INVENTION

The present invention comprises a plant for producing a low energy asphalt pavement, which utilizes tested and designed equipment having a low energy heating system using microwave technology and manufacturing process (“LEHS”) for using up to 100% recycled asphalt pavement (“RAP”) to convert it into high performance hot mix asphalt (“HMA”) that out performs prior art asphalt products of any type. LEHS uses very little energy and generates virtually untraceable amounts of pollution when compared to current existing methods of producing HMA.


In general the process comprises the steps shown in FIG. 2.


The process starts with RAP material recovered from roadways, parking lots or other paved surfaces. The process can use varying amounts of RAP including up to 100% RAP, which allows for maximum reuse or recycling of product. An emulsion is added to the product, as describe in more detail below, the emulsion can constitute about 5% of the product (or variations therefrom). After processing as described below, a fused high performance HMA product is produced.


The RAP raw used for production, and tested as described below, came from several different climatic zones of the United States and represented the multiple variations of pavement that are present in the field. The injection process can use conventionally available engineered asphalt emulsions at a rate of 4% to 8%. The finished material has strength characteristic twice that of the best HMA currently in production, and at least as much flexibility to resist cracking as with prior art HMA.


The production process utilizes a much smaller footprint than existing pavement HMA manufacturing plants. The production process utilizes substantially less energy, reduces the processing temperatures, and produces substantially less pollution, and unlike prior art asphalt production facilities these advantages allow the production facility to be placed inside an enclosed building opening up better strategic plant placement reducing trucking making the process and product more economical. The facility, without the prior art environmental and other problems, can be located closer to the points of use of the product, which tend to be in densely populated areas that previously would not be suitable locations for an asphalt plant. Also, an enclosed plant can operate in cold and inclement weather, which is not possible or practical for outdoor facilities. In colder climates, the energy demands needed to heat the product and the use of open flames made it impossible to operate indoors and extremely expensive to operate in cold weather; so much so that asphalt plants in colder climates close during the winter. The present invention substantially eliminates these and other problems.



FIG. 3 describes the general flow of the process of producing HMA in accord with the present invention. The steps thereof are described herein below. The low energy asphalt production (“LEAP”) process of the present invention process involves RAP receiving, RAP sizing and engineered emulsion injection, ambient temperature I-RAP (RAP injected with emulsion) storage, processing through the low energy microwave heating system (“LEHS”), and storage and shipping of the final HMA product.


The LEAP standard HMA mix design is based on weight, and is to utilize about between 4 to 8 percent emulsion, about between 96 to 92 percent RAP, and optional addition about 1 percent lime, corresponding to an 85 tons per hour (“TPH”) RAP feed rate, 4.5 TPH of emulsion, and 0.9 TPH of lime. Incoming RAP can be stored inside or outside the facility. Storing inside prior to processing will reduce moisture content on the feedstock from approximately 4 to 7 percent moisture at the time of delivery to minimum quantities at the time of use. Excess water, if any, is driven off within the microwave heating section and does not impact the final product quality.


RAP Receiving


LEAP receives RAP via end dump trucks through a truck sized garage door opening in the side of the processing building; the incoming material is moved with a front end loader, conveyor or similar device. RAP is piled in a corner of the building forming multiple connected piles designed preferably for combined storage of approximately 20,000 tons of material. Incoming RAP is to be graded by source. LEAP intends to utilize RAP from highways or other public projects to the extent practical to limit the amount of incoming aggregate that is outside typical HMA DOT specifications. Should it become necessary to utilize RAP from multiple sources, LEAP intends to from multiple piles to facilitate multiple mix designs.


RAP Grinding and Emulsion Blending


RAP is to be ground using nominal 250TPH throughput grinding and blending unit, which are commercially available from Nesbitt Contracting or Caterpillar Corporation, which is designed to size RAP to between one and a-quarter inch and one-half inch size depending on final mix design. The crushing/injection unit includes a screen on the incoming RAP that allows material of one and one half inch or less in size to enter the grinding section. Oversized material that will not pass through the incoming screen is sent to a crushing section to be reduced in size and then returned to the incoming screen. Water is added to the RAP prior to grinding to control dust and minimize heat generation within the grinding machine. Output from the grinding section is sent to two parallel pug mills, which have the ability to blend or inject up to two different grades of the liquid engineered emulsion with the ground RAP. Solid and liquid material is blended within a pug mill using the opposing paddles on two parallel shafts; the paddles simultaneously mix the material and push the mixture from the inlet to the outlet of the mill. The RAP-emulsion blend, known as intermediate or injected RAP (“I-RAP”), is to be conveyed from the outlet and piled on either side of the crushing/injection unit, production is sized such that the I-RAP material can be produced at approximately 3 times the rate of the heating process (described below). I-RAP can be stored at ambient temperature for up to 8 weeks prior to processing into HMA.


Low Energy Heating System (LEHS)


LEAP utilizes a microwave heating system (shown in FIG. 4) to heat the I-RAP to a pre-specified temperature prior to delivery for silo storage and/or to paving contractors. This system, known by LEAP as the Low Energy Heating System (“LEHS”), uses microwave energy of about 915 MHz to selectively heat the aggregate within the I-RAP, enabling LEAP to heat the mixture without degrading the asphalt cement within the emulsion. LEAP uses two parallel heating systems with a minimum of about 300 kW to 800 kW, each with 45 to 75 TPH of capacity, to process the I-RAP. Each LEHS system includes a minimum of four microwave transmitter units with a splitter/wave guide that directs microwave energy from each transmitter into two rotary head heating chambers, resulting in a combined eight chambers per system (16 heating chambers per facility). I-RAP is passed through the microwave heating chambers using a belt conveyor at an I-RAP depth of slightly greater than 3 inches.


The engineered emulsions designed for use with the LEHS are preferably capable of insulating and protecting the remaining asphalt binder present in the RAP from the violent heating power of the microwaves. In particular, aged RAP normally has 2.4 to 4% asphaltene binder, asphaltines are present in asphalt and the ratio of desirable maltenes to asphaltenes decreases over time due to weathering and oxidation causing the asphalt to become dry or brittle. High concentration of asphaltene has heretofore limited the usefulness of RAP such that it either cannot be used, can only be used in limited quantities resulting on an inferior dry brittle product, or the asphaltines can be burned off at temperature producing pollutants. LEAP can utilize up to 100% RAP because it can rejuvenate asphaltenes, or otherwise increase the ration of maltenes to asphaltenes resulting in a very high quality HMA product. The microwave transmitters have the ability to generate variable or constant power and the degree of heating is to be controlled by LEAP by adjusting the power and conveyor belt speed to increase or reduce the exposure time of the I-RAP within the LEHS. By varying the intensity of the power within the chamber or series of chambers different HMA mix designs can be produced with different performance characteristics.


Various exemplary layouts for the LEAS/LEAP plant are shown in FIGS. 5-8, and can accommodate up to two LEHS systems can be located in close proximity within a plant.


LEAP HMA Performance Characteristics


LEAP HMA for has been tested in comparison to Superior Performing Asphalt Pavements (“Superpave”) standard developed for the U.S. Department of Transposition, Federal Highway Commission and used for all paving projects that are funded in a whole or in part by federal funds. The principal measurement used for the evaluation of HMA is the tensile strength ratio (“TSR”) which is used to predict the durability of the HMA. Some southern states, notably Texas and Louisiana, have replaced the TSR measurement with the Hamburg Rut Test measurement as HMA laid at elevated temperatures can become brittle. The following table shows the results of testing performed on LEAP HMA against the foregoing standards.












LEAP HMA Property Testing Results per AET, Jan. 12, 2013(1)


(HMA Samples from Dec. 20, 2012 and Jan. 9, 2013)













LEAP at
LEAP at
LEAP at



Superpave HMA
230° F.
220° F.
290° F.


Property
SPWEB340B(2)
No Lime
With Lime
With Lime














Asphalt Cement or Emulsion
5.5
5.0
5.0
 5.0


Content - % by weight






TSR
80.9
73.8
75.5
 83.4


Percent Air Voids
4.0
3.0
2.8
 3.8


Hamburg Rut Test - 12.5
8,500
N/a
19,000
20,000+(3) 


millimeter depths






Bulk Specific Gravity
2.438
2.356
2.358
  2.356


Density, lb./ft3(4)
152.1
147.0
147.1
147.0


Maximum Specific Gravity
2.540
2.396
2.422
  2.396


Dry Tensile Strength, psi(5)
68.1
128.6
199.1
226.3


Soaked Tensile Strength, psi
55.1
94.9
150.3
188.8






(1)Engineering Testing Summary, Crius Corporation Asphalt Plant Air Emissions Engineering Test, Dec. 18, 2012, AET Project Number 14-01235




(2)SPWEB340B is a Minnesota Department of Transportation Superpave specification where “SP” indicates the gyratory (testing) design, “WE” indicates a wear mixture, “B” indicates <¾″ aggregate, “3” indicates the traffic level, “40” indicates 4.0 percent design air void, and the “B” indicates the virgin asphalt cement binder grade.




(3)Test halted at 20,000 cycles, the upper limit of the testable range.




(4)Lb./ft3 = pounds per cubic foot




(5)Psi = pounds per square inch.







The Superpave specification, and most derivative state specifications, do not permit the use of more than 25 to 50 percent RAP within the HMA mix design due to the inability of traditional batch and drum HMA plants to sufficiently heat the aggregate within the RAP to temperatures necessary to meet the minimum TSR specifications without forming excess smoke emissions and particulate matter which violates standard air permits. The HMA produced using LEAP production process meets or exceeds the min TSR specification for most states while using 100% RAP and produces virtually zero emissions or particulate matter.












Minimum TSR for Select State DOT Specifications










TSR (Minimum)
States






85%
MS (with 1% lime)



80%
VA, OR, FL, AL, NM, OK, SD,




IA, NY, GA, AR, MN



70%
CA, NV, MO, CO



60%
AZ



Hamburg Rut Test
TX, LA, UT









Several of the southern states have moved to the Hamburg Rut Test for a more robust measurement of durability of the HMA. Virgin asphalt cement had two primary chemical components, asphaltenes and maltenes. Asphaltenes are hard materials that provide the mechanical strength while maltenes are the oily fraction which functions as the sticky component in HMA. Maltenes oxidize with age or excess heat to form asphaltenes which causes the HMA to become hard and brittle. The aged or heat damaged HMA cracks under heavy loads causing failures of the road surface. The Hamburg Rut Test is performed using a wheel which passed over an HMA sample until the ensuing rut exceeds 12.5 millimeters in depth. Southern states, where summer paving temperatures can prematurely age the HMA, have been transitioning to the Hamburg Rut Test as a proxy measurement to ensure that the maltene fraction was not damaged during application. This test is an important benchmark for LEAP HMA as the asphalt cement within RAP has been aged, and traditional HMA using RAP is excess of 25 percent had a proclivity to fail early due to the relative lack of maltenes.


The graph in FIG. 9 shows the results for testing of two variations of the LEAP HMA.


LEAP Rut Test results far surpass Rut Test results for the best performing HMA product s, especially when you consider the RAP used was never designed for loading anywhere near this level (tensile <60).


The Green line represents material that was heated to 220 degrees; the purple line was heated to 290 degrees. Conventional Superpave HMA fails at 8500 passes, while the LEAP HMA exceeded 20,000 cycles in some cases without failure.


LEAP Emissions


Emission testing shown below was performed for particulate and volatile organic carbon (“VOC”) testing of the exhaust from an indoor LEHS system inside. The summary of which is included below.

  • Overview: Particulate and VOC air emission testing was conducted on a pilot scale asphalt plant on Dec. 18, 2012. Particulate emission testing was conducted according to EPA Method 5 and EPA Method 202. VOC emission testing was conducted in adherence with EPA Method 25A using a Total Hydrocarbon (THC) Analyzer. At the time of the emission test, the pilot scale asphalt plant was producing 10 Tons/Hour of asphalt.
    • A federal regulation (NSPS Subpart 1) exists for particulate matter for all Hot Mix Asphalt Plants (HMA). Currently, there is not a federal regulatory limit for VOC; VOC emissions are compared to the EPA emission factors in the table below. Detailed test results can be found in Table 1 and Table 2 which are attached to this document.














Emission Unit Tested
Pollutant
Test Result




















Federal





Standard



Cirus Pilot Scale
Particulate
≦0.04
0.0006


Asphalt Plant as
Matter
Grains/DSCF
Grains/DSCF


Tested





Cirus Asphalt Plant
Particulate
≦0.04
0.005


(Scaled up 8 times)
Matter
Grains/DSCF
Grains/DSCF




EPA Emission





Factor



Cirus Pilot Scale
VOC
0.440
0.026


Asphalt Plant as

Lbs/Hr a, b
Lbs/Hr a


Tested






a VOC is equivalent to the Total Hydrocarbons as Propane.




b This number represents the EPA emission factor for VOC emissions for a Drum Mix HMA running on natural gas.














TABLE 1







Summary of Asphalt Plant Particulate Test Results


Crius Corporation -- Plymouth, Minnesota


AET #14-01235











Parameter
Run #1
Run #2
Run #3
Average














Particulate Matter (PM) Results






Date
Dec. 18, 2012
Dec. 18, 2012
Dec. 18, 2012



Run Time
9:28-10:28
11:43-12:42
13:28-14:28



Stack Temperature, ° F.
62
71
70
68


Stack Oxygen, %
20.7
20.7
20.7
20.7


Stack Carbon Dioxide, %
0.2
0.2
0.2
0.2


Moisture, %
2.3
3.0
2.1
2.5


Stack Flow Rate, DSCFM
700
700
700
700


Isokinetic Variation, %
101.4
100.1
99.2
100.2


Filterable Particulate Emission Results






Particulate Concentration, grains/dscf:
0.0010
0.0004
0.0005
0.0006


Particulate Mass Rate, Lbs/Hr:
0.0059
0.0025
0.0028
0.0037


Organic Condensibles Emission Results






Particulate Concentration, grains/dscf:
0.0002
0.0003
0.0002
0.0002


Particulate Mass Rate, Lbs/Hr:
0.0011
0.0016
0.0013
0.0013


Inorganic Condensibles Emission Results






Particulate Concentration, grains/dscf:
0.0008
0.0008
0.0007
0.0008


Particulate Mass Rate, Lbs/Hr:
0.0050
0.0046
0.0042
0.0046


Filterable + Organic






Condensibles Emission Results






Particulate Concentration, grains/dscf:
0.0012
0.0007
0.0007
0.0008


Particulate Mass Rate, Lbs/Hr:
0.0070
0.0041
0.0040
0.0050


Total Particulate Emission Results






Particulate Concentration, grains/dscf:
0.0020
0.0014
0.0014
0.0016


Particulate Mass Rate, Lbs/Hr:
0.0119
0.0086
0.0082
0.0096
















TABLE 2







Summary of Asphalt Plant VOC Emission Test Results


Crius Corporation - Plymouth, Minnesota


Dec. 18, 2012 - AET #14-01235













Airflow
PPMv,
Lbs/
PPMv,
Lbs/


Exhaust
Rate
Ave As
Hr As
Ave As
Hr As


Location
SCFM
Propane
Propane
Carbon
Carbon










Run #1 9:29-10:28












Asphalt Plant
700
5.90
0.028
17.7
0.023


Oven Outlet












Run #2 11:42-12:41












Asphalt Plant
700
4.94
0.024
14.8
0.019


Oven Outlet












Run #3 13:28-14:27












Asphalt Plant
700
5.10
0.025
15.3
0.020


Oven Outlet












AVERAGES RUNS # 1-3












Asphalt Plant
700
5.31
0.026
15.9
0.021


Oven Outlet









The pollution testing results indicate the LEAP plant will fall well below the required emission standards for HMA production. These results demonstrate that the LEAP plants are suitable for locations that are outside the reach of conventional HMA plants in most states due to pollution and air quality regulations.


LEAP Technologies plants can be placed in almost any industrial zoning that supports trucking traffic. This significantly increases the competitive advantage over conventional asphalt plants by going where they cannot. Heretofore HMA plants, due to pollution and emission issues, had to be located remotely, and typically not near locations where the HMA product is used. This greatly increased cost associated with product use because the product has to be transported greater distances than in possible with LEAP plants.


Furthermore, because LEAP plants can be located indoors and have much reduced energy needs they can be operated year round in colder climates and at much lower operating costs. Strategic locations will reduce hauling rates and improve the economic impact to the end users.


Still further, LEAP plants have a much smaller footprint than conventional asphalt plants, providing even greater advantages.


LEAP plants can be operated at the same time or operated based on product demand. Unlike existing conventional HMA plants there is little effort to engage production, simply turn on a few switches and your production ready. The ease of production engagement allows ability to have material readily available 12 months a year, even in northern climates. Existing HMA plants in the northern regions are required to shut down during the winter months due to the high operational costs and required placement outdoors.


In the southern states or warmer climates the configurations shown below allows for the RAP to be stored outside. LEAP plants can be located within a city in a facility of 40,000 sq. ft. or larger. By bringing the entire production process inside you retain the ability to produce anytime without the high cold weather start-up costs associated with conventional HMA plants.


While the foregoing written description of the invention enables one of ordinary skill to make and use what is considered presently to be the best mode thereof, those of ordinary skill will understand and appreciate the existence of variations, combinations, and equivalents of the specific embodiment, method, and examples herein. The invention should therefore not be limited by the above described embodiment, method, and examples, but by all embodiments and methods within the scope and spirit of the invention. For example, the LEAS system could be used to modify existing asphalt plants to allow them to either reduce the level of pollution, by reducing the heat necessary, and/or to increase the amount of RAP used in the creation of HMA to perhaps as high as about 70% to 80%.

Claims
  • 1. An asphalt plant for producing a high performance hot mix asphalt product, comprising: RAP material;emulsion added to the RAP;low energy microwave heating system for processing the RAP emulsion mix.
CROSS-REFERENCE TO RELATED APPLICATIONS

The present application claims priority to and incorporates by reference the following U.S. Provisional Patent Application Nos. 61/643,010 and 61/643,046 filed on May 4, 2012, and is a continuation in part of and incorporates by reference U.S. patent application Ser. No. ______ filed on May 6, 2013.

Provisional Applications (2)
Number Date Country
61643010 May 2012 US
61643046 May 2012 US