Granular filter media

1. A granular material for removing contaminants from water comprising:

aggregate and at least two remediation materials in contact with said aggregate;

wherein each of said remediation materials is either in contact with the aggregate via different contact mechanisms or is in contact with the aggregate via the same contact mechanism and the contact mechanism is selected from the group consisting of the remediation material absorbed into the aggregate, the remediation material coated on the surface of the aggregate, the remediation material dusted on the surface of the aggregate, and combinations thereof.

2. The granular material of claim 1 , wherein each remediation material is in contact with the aggregate via different contact mechanisms.

3. The granular material of claim 1 , wherein each remediation material is in contact with the aggregate via the same contact mechanism.

4. The granular material of claim 1 , comprising at least three of said remediation materials, wherein at least two remediation materials are in contact with the aggregate via the same contact mechanism and at least one remediation material is in contact with the aggregate via a different of said contact mechanisms.

5. The granular material of claim 1 , wherein the aggregate size is 150 μm to 4 inches, 150 μm to ⅜ inch, or ⅛ inch to 4 inches.

6. The granular material of claim 1 , wherein the absorption of the aggregate is 0 to 40%, 0 to 9%, 0 to 3%, 2 to 20% or 5 to 40%.

7. The granular material of claim 1 , wherein the remediation material is selected from the group consisting of calcium hydroxide, ferric chloride, colloidal activated carbon, colloidal silver, photocatalytic titanium dioxide, sulfur, sodium sulfide, and permanganate when the remediation material is impregnated within the aggregate.

8. The granular material of claim 1 , wherein the remediation material is selected form the group consisting of Portland cement, hydrated lime, limestone powder, calcium sulfo-aluminate cement, fly ash, high sodium fly ash, high carbon fly ash, sodium sulfide, elemental sulfur, blast furnace slag, photocatalytic titanium dioxide, and gypsum, when the remediation material is coated on the aggregate.

9. The granular material of claim 1 , wherein the remediation material is selected from the group consisting of limestone powder, sepiolite, attapulgite, activated sepiolite, activated attapulgite, photocatalytic titanium dioxide, heat treated gypsum, elemental sulfur, zero valent iron, activated carbon, and persulfate when the remediation material is dusted on the aggregate.

10. The granular material of claim 1 , wherein the remediation material is coated on the aggregate and delayed ettringite has formed.

11. The granular material of claim 1 , wherein the remediation material is coated on the aggregate and meta-stable ettringite, secondary ettringite, or combinations thereof has formed.

12. The granular material of claim 1 , wherein the granular material comprises free aqueous calcium in combination with e aq − , HO − and O − generated by radiation of the granular material.

13. A method for making granular material for removing contamination from water comprising:

providing an aggregate; and

adding at least two remediation materials to the aggregate by one or more of the following processes:

(a) adding a solution of said remediation material to the aggregate and (i) allowing said remediation material to absorb into the aggregate or (ii) applying a vacuum to absorb the remediation material into the aggregate;

(b) adding a powder of said remediation material and water to the aggregate and mixing to form aggregate coated with said remediation material; or

(c) adding a powder of said remediation material to the aggregate and mixing to form aggregate dusted with said remediation material.

14. The method of claim 13 , wherein the coated aggregate is formed, further comprising placing the coated aggregate in an oven at 80° C. or greater for 24 hours to cause delayed ettringite formation.

15. The method of claim 13 , further comprising the steps of drying the resulting aggregate/remediation material and heating the dried media at 50° C. or greater for 24 hours.

16. The method claim 13 , further comprising activating the resulting aggregate/remediation material with alpha radiation, beta radiation, gamma radiation, or x radiation.

17. A method for filtering contaminated water comprising placing the granulated material, a substance, or the combination in the path of surface water or subsurface water flow.

18. The method of claim 17 , wherein the granulated material, the substance or the combination is placed in a location to capture water from agricultural tiles, agricultural fields, livestock facilities, golf courses, construction sites, urban areas, snow melt, rainfall, runoff from nuclear sites, other drainage, and docks.

19. The method of claim 17 , wherein the granulated material, the substance, or the combination is contained in a filter.

20. A soil amendment comprising the granular material of claim 1 that has been subjected to a contaminated water flow and crushed.

21. The soil amendment of claim 20 , wherein the granular material has been used to filter agricultural runoff, preferably runoff containing nitrate and phosphate, prior to being crushed.

22. A method of removing contaminants in water comprising using the substance of claim 1 in a water contaminant removal process in a public water works or groundwater treatment facility.

23. The method of claim 22 , wherein the substance is added as flash mix, coagulant, flocculant, or combinations thereof, or added to a flash mix basin.

24. A method for reclaiming heavy or rare earth metals comprising reclaiming the metals from the granular media of claim 1 that has been subjected to a contaminated water flow.