PFAS impermeable concrete
The production of a PFAS impermeable cementitious product using a cementitious slurry with specific additives addresses the leaching issue of PFAS from traditional cementitious materials, effectively preventing contamination and enhancing environmental safety.
Patent Information
- Application Number
- PCT/AU2024/050852
- Authority / Receiving Office
- WO · WO
- Patent Type
- Applications
- Current Assignee / Owner
- Priority Date
- 2023-08-09
- Filing Date
- 2024-08-09
- Publication Date
- 2025-02-13
AI Technical Summary
Existing cementitious materials are porous and alkaline, allowing Per- and Polyfluoralkyl Substances (PFAS) to leach out and contaminate the environment, posing significant health and environmental risks.
A method for producing a substantially PFAS impermeable cementitious product by forming a cementitious slurry with cement, water, aggregate, and additives such as siliceous pozzolans, plasticizers, and crystalline growth water-proofing compounds, resulting in a product with a coefficient of permeability of at or below 10^-8 m/s.
The method effectively prevents the permeation of PFAS into the cementitious product, creating an impermeable barrier that reduces the risk of PFAS contamination in environments at risk.
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Figure AU2024050852_13022025_PF_FP_ABST
Abstract
Description
PFAS IMPERMEABLE CONCRETEFIELD
[0001] The present invention relates to concrete and like cementitious products configured for use in environments in which contamination by Per- and Polyfluoralkyl Substances (‘PFAS’) is increased risk. The present invention additionally relates to a method for installing the concrete and like cementitious products in areas at risk of PFAS contamination.BACKGROUND
[0002] PFAS are a family of chemicals found in a wide variety of consumer and retail products. Thousands of different types of PFAS are known, some being more widely used and understood than others. Many PFAS are resistant to heat, water, grease and oil and have therefore been used in a variety of applications including in stain- and water- resistant fabrics, cleaning products, paints and firefighting foams.
[0003] Recent studies suggest that at least some PFAS are bio-accumulative, and that the bio-accumulation of PFAS within humans and animals can have serious adverse health effects, potentially including carcinogenic effects even at relatively low concentrations. Additionally, PFAS can be chemically quite stable as well as soluble, such that PFAS levels in the environment, including in soil and groundwater, can increase over time which in turn increases the risk of health effects, and impact to the environment.
[0004] As mentioned above, PFAS have historically been used in aqueous film forming foams (AFFF) used for firefighting. During a fire, such as an inflammable liquid fire, firefighting foams can often be used quite liberally to douse the fire. The result is that following a fire, sites where foams have been used historically can be contaminated with PFAS. Therefore, sites where chemical fires can occur, or have occurred, such as: fire response training facilities, airports, military facilities, fuel refineries and storage facilities, ports, and chemical plants have become quite contaminated over time.
[0005] PFAS may leach from such facilities into underlying soil, groundwater, and nearby surface water receptors. Concrete, bitumen, and other commonly used structural materials are porous, and allow PFAS that have previously leached into the matrix of the material to slowly leach out to contaminate the nearby environment. It has further been generally understood that PFAS will leach under alkaline conditions as generally present within cementitious materials.
[0006] Further, PFAS are understood to be capable of travel over long distances via surface water, groundwater and other mechanisms such as wind transport of contaminated soils, and will bioaccumulate in food sources such as fish. Given the above, PFAS represent a significant health risk to the community such that PFAS contamination management remains a significant issue. Recent examples of such risks include the town of Katherine, NT, where PFAS contamination from the Tindal RAAF Base has contaminated groundwater and the Katherine River, which the town relies on for its drinking water supply.
[0007] To date, the focus of PFAS contamination management has been on clean up I remediation of soils and the water to remove existing contamination. For example:PCT Patent Publication WO 2017 / 131972 A1 , in the name of Oxytec LLC, describes a process for the remediation of contaminated soils, ground water and waste. PFAS within the contaminated materials are treated in either in situ or in an ex situ reactor to destroy, breakdown, or defluorinated the contaminating PFAS. The PFAS are treated with a reactant such as: persulphate, oxygen, ozone, hydrogen peroxide or maltodextrin.PCT Patent Publication WO 2019 / 113268 A1 , in the name of Eminus LLC, effectively describes a froth flotation system for the decontamination of water containing PFAS contaminants. The system comprises introducing a foaming agent to the water, and injecting a gas through a diffuser into the water so as to form bubbles such that the PFAS contaminants accumulate in the bubbles which are then scooped as foam from the surface of the water.PCT Patent Publication WO 2010 / 065996, in the name of CRC Care Pty Ltd, discloses a modified clay sorbent which may be used for the sorption of PFAS. According to particular embodiments, the modified clay comprises a palygorskitet clay modified with a cationic surfactant. WO 2010 / 065996 further discloses a method of separating a contaminant such as PFAS from a contaminated sample by contacting the contaminated sample with the modified clay sorbent.US Patent Publication 2019 / 0314876 A1 , in the name of TRS Group Inc, describes a method to remediate soils containing PFAS and organic carbon, in which the soil is heated at a sufficient temperature and for a sufficient duration to reduce surface effects between the organic carbon and the PFAS to permit evaporation of the PFAS.
[0008] The above exemplified methods evince a curative rather than preventative approach to PFAS management, and may be considered impractical for larger contamination projects, since the treatments may involve specialist treatment equipment or materials, and / or a significant amount of: effort, reagents, and / or energy to treat or remove the PFAS from material requiring remediation.
[0009] DE 2015007292 A1 , in the name of SRS Deponiebau GmbH, discloses a method of containing PFAS within a cementitious material. However, this document generally teaches that PFAS will be contained within any cementitious material without any requirement for modification or configuration, which is incorrect. As noted above, PFAS is well known to leach from concrete and like cementitious materials given the porosity and alkaline nature of such materials. DE 2015007292 does teach that additives can be added to the cement binder, including fly ash or pozzolan or lime to optimize the “binding” behaviour or the intended use of the resulting product - however the amount of such additives to include is not specified, nor how the addition of these additives would optimize the binding behaviour. In summary, the disclosure of DE 2015007282 may be viewed as entirely speculative and does not provide anywhere near sufficient direction to enable a person skilled in the art to contain PFAS within a cementitious product. Those skilled in the art would recognize, knowing that PFAS generally leaches from concrete and cementitious materials, that the method taught in DE 2015007282 would not actually contain PFAS.
[0010] Sorengard, et al., “Stabilization and Solidification Remediation of Soil Contaminated with Poly- and Perfluoroalkyl Substances (PFASs)”, Journal of Hazardous Materials 367 (2019) 639-646 teaches a method of containing PFAS within a cementitious material. According to the method taught, a sorbent is added to the cementitious product while forming the slurry so as to absorb the PFAS within the sorbent, thereby containing the PFAS within the cementitious material. While the cementitious binder used for experiments, including to produce a control product, included fly ash and granulated blast-furnace base slag, test results showed that cementitious products not including activated carbon or Rembind® did not contain short chain PFAS due to the high-water solubility of those short chain PFAS. Moreover, and as would be understood by those in the art, the addition of sorbents has a negative effect on strength properties of the resultant cementitious material. As a result, Sorengard enables cementitious materials of low compressive strength in the range of 3-5MPa. More generally, Sorengard teaches toward use of activated carbon-based sorbents to improve the containment of PFAS (specifically short-chain PFAS, which are otherwise not contained) within a cementitious product, notwithstanding the negative effects the addition of this material would be understood to have on resulting mechanical strength.
[0011] It is an object of the present invention to provide a pre-emptive or preventative means for managing the risk of PFAS contamination in areas that are at risk of PFAS exposure, which overcomes one or more of the deficiencies with the existing art, or at least provides a viable alternative.
[0012] In certain embodiments, the present invention provides a product for use in locations at risk of PFAS contamination, such as in locations having increased risk of oil and related hydrocarbon-based fuel fires, in addition to a method of using such a product in an environment involving risk of PFAS contamination.
[0013] The reference in this specification to any prior publication, or information derived from it, or to any matter which is known, is not, and should not be taken as an acknowledgement or admission or any form of suggestion that the prior publication, or information derived from it, or known matter forms part of the common general knowledge in the field of endeavour to which this specification relates.SUMMARY
[0014] According to a first aspect of the invention, there is provided a method of producing a substantially PFAS impermeable cementitious product, the method comprising: forming a cementitious slurry, the cementitious slurry comprising: cement; water; aggregate; and allowing the cementitious slurry to cure and thereby form a cementitious product; wherein the method comprises adding one or more of: siliceous pozzolans; plasticizer(s); and crystalline growth water-proofing compound(s), in an amount sufficient to produce a cementitious product comprising a coefficient of permeability of at or below 10'8m / s, thereby substantially preventing permeation of PFAS including short-chain PFAS into the cementitious product.
[0015] According to a second aspect of the invention, there is provided a method of installing a cementitious product in a location with an increased likelihood of PFAS contamination, the method comprising: identifying a location as having an increased likelihood of PFAS contamination; and installing at the location a cementitious product, the cementitious product produced by: forming a cementitious slurry, the cementitious slurry comprising: cement; water; aggregate; and allowing the cementitious slurry to cure and thereby form a cementitious product;wherein the method comprises adding one or more of: siliceous pozzolans; plasticizer(s); and crystalline growth water-proofing compound(s), in an amount sufficient to produce a cementitious product comprising a coefficient of permeability of at or below 10'8m / s, thereby substantially preventing permeation of PFAS including short-chain PFAS into the cementitious product.
[0016] In an embodiment, the cementitious slurry is not contaminated with PFAS (other than unavoidable impurities).
[0017] In an embodiment, the aggregate comprises coarse aggregate.
[0018] In an embodiment, the coarse aggregate comprises one or more of: recycled concrete, asphalt, bitumen or gravel.
[0019] In an embodiment, the aggregate comprises fine aggregate.
[0020] In an embodiment, the fine aggregate comprises one or more of sand or soil.
[0021] In an embodiment, the water contains groundwater.
[0022] In an embodiment, the cementitious product comprises 2-20 % siliceous pozzolans by weight of cement.
[0023] In an embodiment, the cementitious product comprises 0.5-5 % of plasticizer(s) per 100 kilograms of cement.
[0024] In an embodiment, the plasticizer(s) comprises polycarboxylate ether polymer superplasticiser(s).
[0025] In an embodiment, the cementitious product comprises 0.25-3% of crystalline waterproofing admixture by weight of cement.
[0026] In an embodiment, the cementitious product is high-strength.
[0027] In an embodiment, the cementitious product constitutes a stabilized sand product.
[0028] In an embodiment, the stabilized sand product comprises approximately: 10-50% cement, 30-60% fine aggregate, and 5-30% water.
[0029] In an embodiment, the stabilized sand comprises a compressive strength of at least 6 MPa.
[0030] In an embodiment, the cementitious material constitutes a stabilized gravel product.
[0031] In an embodiment, the stabilized gravel product comprises approximately: 10-50% cement, 30-60% coarse aggregate, and 5-30% water. In an embodiment, the stabilized gravel product comprises a compressive strength of at least 6 MPa.
[0032] In an embodiment, the cementitious product constitutes concrete.
[0033] In an embodiment, the concrete comprises approximately: 10-30% cement, 10-30% fine aggregate, 20-60% coarse aggregate, and 5-30% water.
[0034] In an embodiment, the concrete comprises a compressive strength of at least 20 MPa.
[0035] In an embodiment, the concrete comprises a compressive strength of at least 32 MPa.
[0036] In an embodiment, the method comprises casting the cementitious slurry into a precast construction element.
[0037] In an embodiment, the method comprises casting the cementitious slurry in situ in an environment where there is increased risk of PFAS contamination.
[0038] In an embodiment, the cement is Portland cement.
[0039] In an embodiment, the method further comprises optimizing the composition of the cementitious slurry for a selected purpose, the method comprising: producing cementitious product samples, the cementitious product samples varying in composition with respect to each other; performing quantitative property testing on the cementitious product samples, the quantitative property testing including: testing for water penetration and / or water permeability, and testing for PFAS penetration; selecting a composition of cementitious slurry considered optimum for a desired purpose, such selection based on results of the quantitative property testing; and producing cementitious product using the selected composition of cementitious slurry.
[0040] In an embodiment, the method further comprises testing for compressive strength.
[0041] According to a third aspect of the invention, there is provided a cementitious product which provides an impermeable barrier to PFAS, the cementitious product produced according to a first aspect of the invention.
[0042] In an embodiment, the cementitious product is a concrete product.
[0043] In an embodiment, the concrete product is a pre-cast concrete product.Throughout this specification and the claims which follow, unless the context requires otherwise:“comprise” and variations thereof such as “comprises” and “comprising”, will be understood to include the inclusion of a stated integer or step or group of integers or steps but not the exclusion of any other integer or step or groups of integers or steps;Reference to increased risk means increased risk when compared to general or typical sites for laying or installation of cementitious products; all specified percentages relate to wt / wt percentages; and“plasticizer” includes plasticizers and superplasticizers, and “plasticizers” shall be similarly construed.DETAILED DESCRIPTION
[0044] It will be convenient to further describe the invention, with reference to the following embodiments. Other embodiments are possible, and consequently, the particularity of the described embodiments is not to be understood as superseding the generality of the preceding description of the invention.
[0045] PFAS has been understood to penetrate into and leach from concrete and like cementitious materials into nearby soils and groundwater over time. The issues addressed by particular embodiments of the present invention relate to producing a cementitious material which is substantially impermeable to PFAS and a method of installing said cementitious material in areas which are at risk of PFAS contamination.
[0046] In an embodiment a cementitious product may be produced from a cementitious slurry comprising a cement (such as Portland cement); an aggregate; water; and additives including one or more of siliceous pozzolans; plasticizer(s); and crystalline growth water-proofing compound(s). It has been found that use of particular additives according to embodiments of the invention can significantly substantially prevent permeation of PFAS, thereby creating a barrier to it.
[0047] Without wishing to be bound by theory, it is believed that cementitious compositions according to embodiments of the invention may allow for: formation of non-soluble crystalline hydration products in the capillary pores of the cementitious product, thereby reducing the permeability to water and ability for water-soluble contaminants such as PFAS, to migrate through the structure; increased formation of calcium silicate hydrate gel, thereby improving concrete strength and reducing permeability; andthe filling of capillary pore / void space to increase density and further reduce permeability and the ability for water-soluble contaminants such as PFAS, to migrate through the cementitious product.Coarse aggregate
[0048] Where incorporated into the cementitious product according to embodiments of the invention, the coarse aggregate may be selected from suitable materials including natural gravels, crushed rock such as crushed granite, recycled crushed concrete, and combinations of such materials.
[0049] In addition to potential use in producing concrete products, coarse aggregate may for example be used to produce a stabilized gravel product that could be safely used in civil engineering projects where there is increased risk of PFAS contamination.Fine aggregate
[0050] Where incorporated into the cementitious product, the fine aggregate may be selected from suitable materials including sand, crushed stone, slag, recycled crushed building materials, and combinations of such materials.
[0051] In addition to potential use in the production of concrete products, fine aggregate may be used to produce a stabilized sand product that could be used in earthworks and civil engineering projects where there is increased risk of PFAS contamination.Water
[0052] Water may be sourced from any suitable location for use in creating cementitious products, and according to certain embodiments be sourced from groundwater, surface water, or other collected water.Cement
[0053] According to certain embodiments, the cement may be formed from ordinary Portland Cement. In other embodiments, the cement may be formed from other hydraulic or non- hydraulic cements as known to the person skilled in the art, including Portland Pozzolana Cement Rapid Hardening Cement, Extra Rapid Hardening Cement, Low Heat Cement, Sulfates Resisting Cement, Quick Setting Cement, Blast Furnace Slag Cement. Sorel Cement, Slaked Lime, and Geopolymers.Siliceous pozzolan(s)
[0054] Siliceous pozzolans are materials which when finely divided react with calcium hydroxide in the presence of water to form compounds possessing cementitious qualities. Suitable sources of siliceous pozzolans may be artificial, such as silica fume obtained from silicon smelting, or burned organic matter residues such as rice husk ash. Alternatively, natural sources such as volcanic ashes and pumices may be utilised. According to certain embodiments the siliceous pozzolan is sourced as silica fume.
[0055] Without wishing to be bound by theory, it is believed that the addition of siliceous pozzolans strengthens the concrete by reducing the concrete porosity and increasing concrete density, while reducing water mobility within the mixture due to the increased surface area and reduced porosity of the product. Since PFAS impact in a cementitious mixture is typically present within free water (due to solubility) or absorbed to the contaminated aggregates and in the pore spaces of the concrete matrix, the addition of the siliceous pozzolans assists with reducing water movement, and thus the ability of PFAS substances to penetrate into the cementitious product.Plasticizer(s)
[0056] Plasticizers (including superplasticizers) may be utilized according to embodiments of the invention. Suitable plasticizers include polycarboxylates, polysulfonates, lignosulfonates, polyglycol esters, and carbohydrates. More specific examples of suitable superplasticizers include: sulfonated naphthalene formaldehyde condensate, sulfonated melamine formaldehyde condensate, acetone formaldehyde condensate and polycarboxylate ethers. According to certain embodiments, cross-linked melamine- or naphthalene-sulfonates, may be used.
[0057] As is known in the art, various forms of plasticizers are available and configured for particular uses. For example, BASF currently distributes polycarboxylate ether superplasticizer under its ‘MasterGlenium SKY branding’, in which: the ‘8100’ product is configured for producing precast concrete elements; the ‘8700’ product is configured for producing ready mixed concrete in hot weather; the ‘8703’ product is configured to produce a mid-range slump concrete; and the ‘8708’ product is configured to produce concrete for use in ‘shotcrete’, pumped concrete, applications. Selection of plasticizers may therefore be determined based on the proposed end-use of the cementitious product.
[0058] Without wishing to be bound by theory, it is believed that concrete plasticisers exhibit surfactant properties and function as dispersants to minimise particle segregation, assistingwith creating a homogeneous concrete / cementitious mixture, and limiting the water requirement of the resultant cementitious product. Additionally, the compressive strength of a resultant concrete increases with the decreasing water to cement ratio.Crystalline waterproofing admixtures
[0059] According to certain embodiments of the invention, a crystalline waterproofing admixture may be utilized. Such waterproofing admixtures are commonly utilized to treat existing porous concrete structures and provide a water-resistant barrier. These admixtures work by reacting with unhydrated cement particles within the concrete product to form crystals, thereby filling voids and pores otherwise found in the concrete product. Traditionally, these additives have been used to treat external surfaces of existing porous concrete structures. According to embodiments of the present invention the additive(s) is incorporated into a cementitious slurry prior to curing.
[0060] Commercially available examples of crystalline growth waterproofing additives include: ‘Contec CT (understood to be a powdered mixture of quartz, Portland cement, tartaric acid, sodium carbonate, and magnesium hydroxide), ‘Xypex concentrate’ (understood to be a mixture of Portland cement, silica, calcium carbonate , and calcium aluminates), and ‘BASF Masterseal 500’ (understood to be a powdered mixture of quartz, Portland cement, calcium carbonate, titanium dioxide, limestone, and gypsum).Other components, additives, admixtures
[0061] It is noted that other additives and components may be incorporated into the cementitious product as appropriate. Other additives which are expressly contemplated include: air entraining admixtures, set retarders, and water reducing, accelerating and shrinkage reducing admixtures. The use of other additives and components determined based on the proposed end-use of the cementitious product, as well as properties of materials including the aggregate used.Project work
[0062] To confirm the viability of the invention, the current inventors undertook research to provide cementitious products having desirable strength, water penetration and permeability.
[0063] The general testing procedure utilized is broadly as set out in Figure 1 , such that testing consisted of: compressive strength testing; water penetration and permeability testing.Slurry composition
[0064] Cementitious slurries were produced having compositions as set out in:Table 2, which unless otherwise specified describes the slurries by volumetric ratios (i.e. parts), andTable 3, which describes the same slurries as Table 2 in quantitative amounts added.
[0065] Tables 2 and 3 refer to use of admixtures A, B, and C, in which:Admixture A is a crystalline waterproofing admixture comprising: Portland cement, calcium hydroxide, calcium aluminates, silica sand and alkaline earth compounds.Admixture B is another crystalline waterproofing admixture comprising: Portland cement, 2,3-dihydroxylbutanedioic acid, sodium carbonate, limestone, gypsum, titanium dioxide and quartz.Admixture C comprises amorphous, reactive pozzolan, silica fume; and a polycarboxylate ether polymer superplasticizer.
[0066] Table 2 - Mix by volumeTable 3 - Mix by approx, amountsCompressive strength testing
[0067] To obtain compressive strength test results, slurries according to each of the above compositions were cast in cylindrical moulds of 100mm diameter and 200mm length. Slurry was poured into each of the moulds (ungreased) in layers, with each layer compacted bystirring to remove air voids. Following pouring, the moulds were held above 90% relative humidity at a temperature of 27° ± 2°C for 24 hours. After this period, the cast specimens were submerged in freshwater for 7 days or 28 days respectively. At least three cast specimens were produced for each slurry composition and curing period.
[0068] The compressive strength of the cured concrete casts was tested on a ‘Manual Digital Type DHR 2000 compression-testing machine, as exemplified in Figure 2A. The testing procedure for each cast specimen was as follows: the specimen was taken out of the freshwater and wiped down to remove excess water (a pre-test cylinder is exemplified in Figure 2B); the specimen was placed vertically on the platform of the compression testing machine. Uniform load application and distribution was facilitated by having pad caps at the ends of the cylinders; before the load was applied, it was made sure that the loading platforms touched the top of the cylinder; the load was then applied continuously and uniformly without shock at the rate of 2.62 kN / min. This was continued until the specimen failed (as exemplified in Figure 2C); the maximum load taken was then recorded; and the test was repeated for the remaining two specimens of a given slurry composition.
[0069] As noted above, a minimum of 3 specimens were tested for each slurry composition. The diameters of the cast cylinders were measured in 2 locations perpendicular to each other at the mid-height of the cylinder. The average of these values was taken to calculate the cross- sectional area. If the diameter measured differed more than 2%, the cylinder was not tested.
[0070] The resulting compressive strength of samples in respect of stabilized sand and 32MPa concrete is set out in Table 4 below:Table 4 - Compressive strength testingThe results of Table 4 demonstrate that cementitious products having reasonable strength characteristics for various uses, including products suitable for use in civil engineering and construction, may be produced from compositions capable of use in locations at increased risk of PFAS contamination. The results for Product C demonstrated higher compressive results than for Products A and B in relation to the specific components tests.In other embodiments, the strength characteristics of the cementitious product may be less relevant in comparison to other product characteristics.As shown in Figure 1 , the Brazilian test could be performed in addition or as an alternative to the compressive strength testing described. In the discussed project, the inventors did not perform any Brazilian tests.Penetration and permeability testing
[0071] To obtain permeability and penetration results, concrete slurries again according to each of the above compositions were cast in cylindrical moulds of 80mm diameter and 160mm length, in a manner otherwise corresponding to that described in respect of compressive strength testing. Following pouring, the cast specimens were held above 90% relative humidity at a temperature of 27° ± 2°C for 24 hours and then submerged in freshwater for 30 days.
[0072] To test permeability, a permeameter was developed incorporating a non-corrodible permeameter rig having an internal diameter of 80mm and an internal effective height of 220mm. Following insertion of a concrete sample into the rig, detachable end plates were at each end to enable transfer of pressurized water. The utilized permeameter is shown in Figure 3, which demonstrates simultaneous testing of two rigs.
[0073] The following steps were then taken to test permeability in respect of each cast specimen:0.5 cm of material were cut off each end of the cast specimen, to provide a flat face and remove any smooth / slippery finish from the core surface, and allow the cores to be inserted evenly in the geo-con rig; the cut specimen was wet and paper dried; the length (L) and weight (Wi) of the cut specimen was recorded; the core was inserted in the geo-con rig under 200 kPa, air was bled out of the water pipes, and the cores were left in place for one hour (60 mins); the cores were removed from rig after one hour, wetted and paper dried, and subsequently weighed. The weight (Wtf) was then recorded; the cores were cut into 2 sub cores as shown in Figure 3B to provide;‘cut 1 ’ - a 4-5 cm cut which was used for the Permeability T est measurements; and‘cut 2’ - a minimum of 10 cm (Critical Length) which was used for the Leaf Test;
[0074] The water penetration in the core surface was marked out using a ‘texta’ and the penetration value was taken as the deepest point of penetration to account for the worst-case scenario. The penetration was then measured using a ruler, as shown in Figure 4B. Results of the testing are set out in Table 5 below.
[0075] The Coefficient of Permeability for the constant head test was then calculated using the equation: k =, where Q (cm3) is discharge, A (cm2) is the cross-sectional area of the rig, L (cm) is the length of the core sample, and h (kPa) is the head difference between the inlet and the outlet.Table 5 - Penetration and permeability test results
[0076] The results demonstrated cementitious products having low permeability and penetration. As may be expected, water penetration was generally shown to have a direct relationship with permeability (i.e. low water penetration typically meant low water permeability). Compositions comprising additive C demonstrated lower levels of penetrationand permeability for both stabilized sand and 32MPA concrete when compared with compositions comprising additive A or additive B.
[0077] Based on permeability testing it was determined that water did not generally permeate or exit tested samples.
[0078] Due to the inherently variable nature of input materials (e.g. sands, gravels, concrete, asphalt, etc) and risk of contamination, the ideal formulation to yield a particular result (i.e. particular physical strength characteristics, permeability and penetration, etc) may vary from site to site and materials used. Nevertheless, utilizing compositions according to the present invention and testing methodologies as taught above, suitable results which include cementitious materials that are substantially impermeable to PFAS can be achieved without undue experimentation.
[0079] It will be understood to persons skilled in the art of the invention that modifications may be made without departing from the spirit and scope of the invention. The embodiments and / or examples as described herein are therefore to be considered as illustrative and not restrictive.
Claims
CLAIMS1. A method to produce a PFAS impermeable cementitious product, the method comprising: forming a cementitious slurry, the cementitious slurry comprising: cement; water; aggregate; and allowing the cementitious slurry to cure and thereby form a cementitious product; wherein the method comprises adding one or more of: siliceous pozzolans; plasticizer(s); and crystalline growth water-proofing compound(s), in an amount sufficient to produce a cementitious product comprising a coefficient of permeability of at or below 10'8m / s, thereby substantially preventing permeation of PFAS including short-chain PFAS into the cementitious product.
2. A method of installing a cementitious product at a location having an increased risk of PFAS contamination, the method comprising: identifying a location as having an increased likelihood of PFAS contamination; and installing at the location a cementitious product, the cementitious product produced by: forming a cementitious slurry, the cementitious slurry comprising: cement; water; aggregate; and allowing the cementitious slurry to cure and thereby form a cementitious product; wherein the method comprises adding one or more of: siliceous pozzolans; plasticizer(s); and crystalline growth water-proofing compound(s), in an amount sufficient to produce a cementitious product comprising a coefficient of permeability of at or below 10'8m / s, thereby substantially preventing permeation of PFAS including short-chain PFAS into the cementitious product.
3. A method according to either of claims 1 or 2, wherein the aggregate has not undergone treatment to remove or reduce PFAS contamination.
4. A method according to any one of the previous claims, wherein the aggregate comprises coarse aggregate.
5. A method according to claim 4, wherein the coarse aggregate comprises one or more of: recycled concrete, asphalt, bitumen, sand or gravel.
6. A method according to any one of the previous claims, wherein the aggregate comprises fine aggregate.
7. A method according to claim 6, wherein the fine aggregate comprises one or more of sand or soil.
8. A method according to any one of the previous claims, wherein the water contains groundwater.
9. A method according to any one of the previous claims, wherein the cementitious product comprises 2-20% siliceous pozzolans by weight of cement.
10. A method according to any one of the previous claims, wherein the cementitious product comprises 0.5-5 litres of plasticizer(s) per 100 kilograms of cement.
11. A method according to claim 10, wherein plasticizer(s) comprises a polycarboxylate ether polymer superplasticizer(s).
12. A method according to any one of the previous claims, wherein the cementitious product is high-strength.
13. A method according to any one of the previous claims, wherein the cementitious product comprises 0.25-3% of crystalline waterproofing agent by weight of cement.
14. A method according to any one of claims 1 to 13, wherein the cementitious product constitutes concrete.
15. A method according to claim 14, wherein the concrete comprises approximately: 10- 30% cement, 10-30% fine aggregate, 20-60% coarse aggregate, and 5-30% water.
16. A method according to either of claims 14 or 15, wherein the concrete comprises a compressive strength of at least 20 MPa.
17. A method according to any one of claims 14 to 16, wherein the concrete comprises a compressive strength of at least 32 MPa.
18. A method according to any one of claims 14 to 17, wherein the method comprises casting the cementitious slurry into a precast construction element.
19. A method according to any one of claims 14 to 17, wherein the method comprises casting the cementitious slurry in situ.
20. A method according to any one of the previous claims, wherein the cement is Portland cement.21 . A method according to any one of the previous claims, further comprising optimizing the composition of the cementitious slurry for a selected purpose, the method comprising: producing cementitious product samples, the cementitious product samples varying in composition with respect to each other; performing quantitative property testing on the cementitious product samples, the quantitative property testing including: testing for compressive strength, testing for water penetration and / or water permeability, and testing for PFAS permeation; selecting a composition of cementitious slurry considered optimum for a desired purpose, such selection based on results of the quantitative property testing; and producing cementitious product using the selected composition of cementitious slurry.
22. A cementitious product according to any one of claims 2 and 3 to 21 (when appended to claim 2), wherein the location is one of the group consisting of: fire response training facilities, airports, military facilities, fuel refineries, fuel storage facilities, ports, chemical plants, or environmental water drainage facilities.
23. A cementitious product for creating an impermeable barrier to PFAS contamination, the cementitious product produced according the method of any one of the previous claims.
24. A cementitious product according to claim 23, wherein the cementitious product is a concrete product.
25. A cementitious product according to claim 24, wherein the concrete product is a precast concrete product.
26. A cementitious product according to any one of claims 23 to 25, when used in an area that is at increased risk of chemical fire.
Citation Information
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