Regulation 11 Amendment of Schedule 1 (Criteria and Procedures for the acceptance of waste at landfills)
For paragraph 17 of Schedule 1 (criteria for waste acceptable at landfills for hazardous waste) substitute—
“Criteria for waste acceptable at landfills for hazardous waste
17.Waste shall only be accepted at a landfill for hazardous waste if—
(a)in the case of granular waste–
(i)it meets the limit values for leaching set out in Table 6;
(ii)it meets the additional criteria set out in Table 7; and
(iii)it will have either–
(aa)if it is cohesive waste, a mean in situ shear strength of at least 50kPa; or
(bb)if it is non-cohesive waste, an in situ bearing ratio of at least 5%;
(b)in the case of monolithic waste–
(i)it meets either–
(aa)the limit values for leaching set out in Table 6; or
(bb)the limit values for leaching set out in Table 8;
(ii)it meets the additional criteria set out in Table 5B;
(iii)it has a mean unconfined compressive strength of at least 1MPa after 28 days curing;
(iv)it has either–
(aa)dimensions of greater than 40cm along each side; or
(bb)a depth and fracture spacing when hardened of greater than 40cm; and
(v)where the waste was subjected to treatment to render it monolithic, prior to such treatment it met the following limit values—
(aa)Loss on Ignition of 10%; or
(bb)Total Organic Carbon of 6%.
Table 6
Components Symbol L/S = 10 l/kgf1 f2 mg/kg dry substance (a)These values must be determined using EN 12457/1 to 3 (applied, in the case of monolithic waste, to a sample which has been crushed).
(b)The Chief Inspector may include conditions in a permit authorising limit values for specific parameters (other than Dissolved Organic Carbon (DOC)) up to three times higher for specified wastes accepted in a landfill, taking into account the characteristics of the landfill and its surroundings and provided a risk assessment demonstrates that emissions (including leachate) from the landfill will present no additional risk to the environment.
(c)If the waste does not meet this value for DOC at its own pH, it may alternatively be tested at L/S = 10 l/kg and a pH of between 7.5 and 8.0. The waste shall be considered as complying with the acceptance criterion for DOC, if the result of this determination does not exceed 1,000 mg/kg.
(d)The value for Total Dissolved Solids can be used alternatively to the values for Sulphate and Chloride.
Arsenic As 25 Barium Ba 300 Cadmium Cd 5 Total Chromium Cr total 70 Copper Cu 100 Mercury Hg 2 Molybdenum Mo 30 Nickel Ni 40 Lead Pb 50 Antimony Sb 5 Selenium Se 7 Zinc Zn 200 Chloride Cl- 25,000 Fluoride F- 500 Sulphate SO42- 50,000 Dissolved Organic Carbonf3 DOC 1,000 Total Dissolved Solidsf4 TDS 100,000 Table 7
Parameter Values (a)Either Loss on Ignition or Total Organic Carbon must be used
(b)If this value for Total Organic Carbon is not achieved, a higher limit value may be permitted by the Chief Inspector, provided that the DOC value of 1,000 mg/kg is achieved at L/S = 10 l/kg at its own pH or a pH value of between 7.5 and 8.0.
Loss On Ignition (LOI) f5 10 % Total Organic Carbon (TOC) f6 6 % Acid Neutralisation Capacity (ANC) Must be evaluated Table 8
Components Symbol mg/m2f7 f8 (a)These values must be determined using EA NEN 7375:2004. Where it is appropriate for compliance testing, the Chief Inspector may specify use of a shortened version of the 64-day tank test provided for in EA NEN 7375:2004 comprising only the first four steps, and in such cases, the limit values shall be a quarter of the values in the table.
(b)The Chief Inspector may include conditions in a permit authorising limit values for specific parameters (other than DOC) up to three times higher for specified wastes accepted in a landfill, taking into account the characteristics of the landfill and its surroundings and provided a risk assessment demonstrates that emissions (including leachate) from the landfill will present no additional risk to the environment.
Arsenic As 20 Barium Ba 150 Cadmium Cd 1 Total Chromium Cr total 25 Copper Cu 60 Mercury Hg 0.4 Molybdenum Mo 20 Nickel Ni 15 Lead Pb 20 Antimony Sb 2.5 Selenium Se 5 Zinc Zn 100 Chloride Cl- 20,000 Fluoride F- 200 Sulphate SO42- 20,000 Dissolved Organic Carbon DOC Must be evaluated. ”
Annotations
Footnotes
- f1
(a)
These values must be determined using EN 12457/1 to 3 (applied, in the case of monolithic waste, to a sample which has been crushed).
- f2
(b)
The Chief Inspector may include conditions in a permit authorising limit values for specific parameters (other than Dissolved Organic Carbon (DOC)) up to three times higher for specified wastes accepted in a landfill, taking into account the characteristics of the landfill and its surroundings and provided a risk assessment demonstrates that emissions (including leachate) from the landfill will present no additional risk to the environment.
- f3
(c)
If the waste does not meet this value for DOC at its own pH, it may alternatively be tested at L/S = 10 l/kg and a pH of between 7.5 and 8.0. The waste shall be considered as complying with the acceptance criterion for DOC, if the result of this determination does not exceed 1,000 mg/kg.
- f4
(d)
The value for Total Dissolved Solids can be used alternatively to the values for Sulphate and Chloride.
- f5
(a)
Either Loss on Ignition or Total Organic Carbon must be used
- f6
(b)
If this value for Total Organic Carbon is not achieved, a higher limit value may be permitted by the Chief Inspector, provided that the DOC value of 1,000 mg/kg is achieved at L/S = 10 l/kg at its own pH or a pH value of between 7.5 and 8.0.
- f7
(a)
These values must be determined using EA NEN 7375:2004. Where it is appropriate for compliance testing, the Chief Inspector may specify use of a shortened version of the 64-day tank test provided for in EA NEN 7375:2004 comprising only the first four steps, and in such cases, the limit values shall be a quarter of the values in the table.
- f8
(b)
The Chief Inspector may include conditions in a permit authorising limit values for specific parameters (other than DOC) up to three times higher for specified wastes accepted in a landfill, taking into account the characteristics of the landfill and its surroundings and provided a risk assessment demonstrates that emissions (including leachate) from the landfill will present no additional risk to the environment.