Comparison of OilCage to Current Technology

 

1.    How does its oil absorption compare to Meltblown Polypropylene?

2.    How is it more useful?

3.    Is it less friable or more enduring?

4.    Is the foam less expensive?

5.    Is it less toxic to wildlife?

6.    Is it cleaner burning as a wicking agent?

7.    Is it made on location?



Question 1. How does its oil absorption compare to Meltblown Polypropylene?

In this comparison I am using an analysis of commercially available polypropylene absorbent booms as the standard to which OilCage can be compared.? The analysis was done by E. Schrader and reported in the Environmental Geology and Water Sciences Journal.[1]? Quoting from that article:


?Essentially, all polypropylene, non-woven fibers have the same average tendency to sorb liquid hydrocarbons onto fiber surfaces, depending upon such parameters as available surface, fabric loft, and surface treating of fibers. However, the handling and packaging of these textiles varies considerably among the boom suppliers and are the major controlling factors in results of the performance testing.?


Like the polypropylene fiber, OilCage is made from a CH2 polymer, but it is a foam. Thus it does not have some of the issues associated with fibers such as shedding of fibers, loose packing (that can result in separation that allows oil to flow through the boom) or the tendency of the fibers to lump up.? To compare the tests done in the article to tests done on OilCage the experimental conditions must be noted.

 

Table 1. Experimental Parameters.

 

Parameter

E. Schrader Tests

OilCage

Oil

Diesel fuel (API ~32), Light Crude ( 28), Heavy Crude (API 16)

Mobile Velocite Oil No 10,?? machining oil (API 32.6)

Temperature

50? and 70?

Room Temperature

Water

Salt

Tap

 

The type of water is different but I noticed no difference in oil absorption between salt water and tap water and the same is stated in the article, so please excuse that difference.? The direct comparisons then are the diesel fuel tests at 70? and the relevant test is total absorption.? 6 booms were tested.? The results for total absorption are shown below and range from 612% to 974%.

 

Table 2. Oil Absorption of Commercial Booms

boom weight (lbs)

gallons of diesel fuel

weight of fuel (lbs)

% weight increase

Ergon

10.6

13.3

94.43

891%

10.6

11.9

84.49

797%

10.6

12.2

86.62

817%

Average

835%

ICI

10

8.6

61.06

611%

10

8.9

63.19

632%

9.8

8.2

58.22

594%

Average

612%

SPC

11.4

12

85.2

747%

10.8

10.6

75.26

697%

11

10.9

77.39

704%

Average

716%

JV

8.4

10.2

72.42

862%

9

10.3

73.13

813%

9

11.6

82.36

915%

Average

863%

3M

9.4

13.8

97.98

1042%

10.6

14

99.4

938%

9.8

13

92.3

942%

Average

974%

Matarah

9.6

10.5

74.55

777%

9.6

9.7

68.87

717%

9.6

10.5

74.55

777%

Average

757%

 

The absorption of OilCage foams is dependent upon the density of the foam.? The maximum oil absorption is observed for ~40 mg/cm3. Lower density foams absorb as much and at a faster rate, but are not physically robust.? Higher density foams are very physically robust, even machinable, and still absorb five times their weight in oil. Figure 1 shows a comparison of OilCage and the data for booms listed above. Please note that OilCage does not absorb water.? This is not always true for the booms. It is specifically noted that the 3M boom absorbed about 5% water and the weight of the water was included in the absorbed oil weight.

 

Figure 1. Oil Absorption comparison for OilCage and Commercial Booms

 

As noted above, the density of the OilCage foam determines the maximum oil absorption.? It also determines the rate of absorption.? Lower density foams absorb faster as shown in the graph below. The 10 mg/cm3 foam absorbs very rapidly (fully saturated in 25 minutes) but after saturation the weight of the oil will crush foam.? This makes this density unsuitable for applications where it will be lifted from the water fully saturated. See Figure 2.

 


Figure 2. Time of Oil Absorption Of OilCage At Various Densities

 

Question 2. How is it more useful?

OilCage is useful in ways other than as a boom.? The boom technology is well understood and readily deployed by personnel.? OilCage is meant to be used as an adjunct to booms and to be used in situations where a boom is not useful.?? For example OilCage can assist booms by being used where the boom has segmented, where two booms meet or where rough water conditions threaten to wash the oil over a boom.? Furthermore OilCage can be deployed in ways that a boom cannot such as from an airplane, under water, or in a marsh.? Dispersal from an airplane is possible as this is a very light product that can be simply dropped from the air. An oil skimmer could later retrieve the oil soaked foam.? Underwater oil can be absorbed by OilCage foam weighted down in the water.? OilCage will not absorb water even after being submerged.? In a marsh the extreme oleophilic nature of the foam will actually pull oil from the surface of cellulosic material.? This was demonstrated by placing an oil soaked paper towel in a tray of water.? OilCage was then added.? After two days most of the oil had left the paper towel and been absorbed by the foam. (See Figure 3 for images.) This transfer of oil occurred without agitation.? OilCage is more effective with agitation so I expect this response to be faster under field conditions. To assist in the retrieval of OilCage in a marsh sheets of OilCage can be strung together on fishing line and placed into the marsh.



Figure 3.? Photos demonstrating the transfer of oil from a paper towel to OilCage foam



There are two reasons why OilCage is more oleophilic than MBPP. First, OilCage does not have an outer cover over the polypropylene fibers.? The cover can inhibit the oil from being absorbed. Second, the structure of the OilCage foam has regular cells aligned in segments.? This creates capillary forces that the pull the oil into the foam.? The fibers of MBPP are randomly distributed, often with large open areas. This does not support capillary forces throughout the matrix. Photos in Figure 4 highlight the difference in structure.



Figure 4. A comparison of fibers in MBPP sorbent (on right) to the foam structure in OilCage (on left).
In both images the reference bar is 100 microns.


 

Question 3. Is it less friable or more enduring?

OilCage is less friable. At low density it is pliable foam before and after oil absorption. I describe it as having a marshmallow modulus.? At high density it is not pliable but would still rather crush than break.

OilCage should be more enduring. The chemical structures of polypropylene and OilCage are very similar, so comparing bulk properties shows negligible differences.? However, the fine fibers of MBPP are much more prone to environmental degradation as compared to the foam structure of OilCage. Tests of this durability would be part of the environmental testing.

?Question 4. Is the foam less expensive?

OilCage could be, depending upon it disposal.? Costs for production are currently being estimated, but a large advantage of OilCage is that it is made solely of CH2 foam, with no casing or other non-polymer material.? I envision the foam being added to the recovered oil and processed with the crude at the refinery ? as one would with typical oil.? If this is done the cost of production for the foam is less than the value of the oil recovered.

Question 5. Less toxic to wildlife?

Polypropylene is very non-toxic. The polymer used to make OilCage is also CH2, but the form of the material this needs to be considered. This is shown in Table 3.? The fine fibers of the polypropylene do pose a minimal risk for humans, and fibers may look appealing to wildlife as food.? OilCage is made as thin 3 inch disks or 9x12 sheets.? Wildlife is not expected to mistake it for food. This becomes especially important if either the MBPP or OilCage have absorbed any oil as oil has documented health risks.

Table 3.? MSDS Listed Health Risks

Potential Health Hazards

Polypropylene Fiber

OilCage

Skin:

Contact with fibers may cause mechanical irrational of skin. No skin absorption has been known

Not anticipated under recommended usage conditions

Eyes:

Mechanical irritation and tissue irritation may occur

Not anticipated under recommended usage conditions

Inhalation:

Some individuals e.g. with asthma or bronchitis are likely to be intolerant of high concentrations of airborne fibers or fiber dust when

processing

Not anticipated under recommended usage conditions

Ingestion:

None known

Not anticipated under recommended usage conditions

Delayed Effects:

None known

None known

Ingredients found on one of the OSHA designated carcinogen lists:

None

None

 

Question 6. Is it cleaner burning as a wicking agent?

Again, the differences in the chemical structures of polypropylene and OilCage foam are minimal.? The differences for burning would be that OilCage does not have a cover material and that it will not have any absorbed water.? These two factors may enhance OilCage?s ability to wick oil for burning but this would need to be demonstrated in the field.

Question 7. Is it made on location?

While Sorbent Booms are typically produced at a factory and shipped to location, we are proposing that OilCage be made on shore near an oil spill.? This foam is very simple to produce requiring only a heated reaction vessel, vacuum pumps and refrigeration.? Most fishing areas have ample refrigeration; reaction vessels and pumps can readily be shipped in. We envision bringing the process to the affected area and employing personnel whose livelihood has been impacted by the oil spill.? This not only offers alternative employment but also a way for individuals to help with the clean-up and lessen their feelings of helplessness and desperation. The production requires only the commercially available polymer and solvent.? The solvent is recaptured for reuse as the foam is dried, thus there is no hazardous discharge to the environment.



[1] Remediation of Floating, Open Water Oil Spills: Comparative Efficacy of Commercially Available Polypropylene Sorbent Booms, Envir Geol Water Sci Vol 17, No. 2, 157-166.

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