Waste Type
Detection Parameters12
Frequency for All Wells
Frequency for Subtitle D Wells4
Municipal solid waste
Alkalinity
Chloride
Field conductivity (at 25°C)
Field pH
Field temperature
Groundwater elevation
Hardness (Total, Ca + Mg)
Semi-annual
Semi-annual
VOC scan2 Volatile Organic Compounds (VOCs)3
Annual
Semi-annual
Municipal solid waste combustor residue
Alkalinity
Boron
Cadmium
Chloride
Field conductivity (at 25°C)
Field pH
Field temperature
Groundwater elevation
Hardness (Total, Ca + Mg)
Lead
Selenium
Sulfate
Semi-annual
Semi-annual
1 The color, odor, and turbidity shall be recorded for all samples in accordance with ss. NR 507.17 (1) (b) and 507.26 (1), but do not need to be reported in electronic format.
12 Additional parameters are required if other waste types are accepted at the landfill. See Table 2.
23 Refer to ch. NR 507 Appendix III for a list of the individual volatile organic compounds VOCs required for a VOC Scan.
4 The monitoring interval for Subtitle D Wells during the active life and proof of owner financial responsibility portion of the perpetual long-term care period shall be no less frequent than annual.
Table 1A
DETECTION GROUNDWATER MONITORING FOR
CCR WELLS AT CCR LANDFILLS1
Waste Type
Detection Parameters12
Monitoring Frequency
Coal combustion residuals
Alkalinity
Boron
Calcium
Chloride
Fluoride
Field conductivity (at 25°C)
Field pH
Field temperature
Groundwater elevation
Hardness (Total, Ca + Mg)
Total Dissolved Solids (TDS)
Sulfate
Semi-annual
1 The color, odor and turbidity shall be recorded for all samples in accordance with ss. NR 507.17 (1) (b) and 507.26 (1), but do not need to be reported in electronic format.
  12 Groundwater samples collected at CCR wells must shall be unfiltered.
Table 2
DETECTION GROUNDWATER MONITORING FOR LANDFILLS ACCEPTING
WASTE TYPES OTHER THAN MUNICIPAL SOLID WASTE1
Waste Type
Detection Parameters
Frequency for All Wells
Paper mill sludge
Ammonia nitrogen
Alkalinity
Chloride
COD
Dissolved Organic Carbon (DOC)
Field conductivity (at 25°C)
Field pH
Field temperature
Groundwater elevation
Hardness (Total, Ca + Mg)
Nitrate + Nitrite (as N)
Sulfate
Semi-annual
Fly or bottom ash12
Alkalinity
Boron
COD
Field conductivity (at 25°C)
Field pH
Field temperature
Groundwater elevation
Hardness (Total, Ca + Mg)
Sulfate
Semi-annual
Foundry waste
Alkalinity
COD
Field conductivity (at 25°C)
Field pH
Field temperature
Fluoride
Groundwater elevation
Hardness (Total, Ca + Mg)
Sodium
Semi-annual
Demolition waste
Demolition monitoring requirements are listed in ch. NR 503
Other solid waste
As specified in writing by the department
1 The color, odor and turbidity shall be recorded for all samples in accordance with ss. NR 507.17 (1) (b) and 507.26 (1), but do not need to be reported in electronic format.
  12 Detection monitoring parameters apply to all wells monitoring CCR landfills that are not defined as CCR wells under s. NR 500.03 (26y).
Table 3
BASELINE AND ASSESSMENT GROUNDWATER MONITORING
PUBLIC HEALTH AND WELFARE PARAMETERS1
All Wells
Additional Parameters for Subtitle D Wells
Additional Parameters for CCR Wells
Arsenic
Barium
Cadmium
Chromium
Copper
Fluoride
Lead
Manganese
Mercury
Nitrate + Nitrite (as N)
Selenium
Silver
Sulfate
Zinc
Antimony
Beryllium
Cobalt
Nickel
Thallium
Vanadium
Antimony
Beryllium
Cobalt
Lithium
Molybdenum
Thallium
Ra-226 and Ra-228, combined12
1 The color, odor and turbidity shall be recorded for all samples in accordance with ss. NR 507.17 (1) (b) and 507.26 (1), but do not need to be reported in electronic format.
12 The maximum contaminant level (MCL) for combined radium is 5 pCi/L under s. NR 809.50 (1) (a).
Table 4
DETECTION LEACHATE MONITORING
FOR ALL LANDFILLS1,2
Municipal Solid Waste and Municipal Solid Waste
Combustor Residue
Paper Mill Sludge
Fly or Bottom Ash
Foundry Waste
The volume of the leachate removed shall be recorded at least monthly and reported to the department semi-annually.
Leachate head levels shall be sampled quarterly and reported to the department semi-annually, unless otherwise required by s. NR 507.21 (3) (b).
Semi-Annual Monitoring Parameters
BOD5
Biological Oxygen Demand (BOD5)
Field conductivity (at 25°C)
Field pH
Alkalinity
Cadmium
Chloride
COD
Hardness (Total, Ca + Mg)
Iron
Lead
Manganese
Mercury
Ammonia nitrogen
Total Kjeldahl nitrogen
Sodium
Sulfate
Total suspended solids
VOC scan3VOCs
Other parameters specified by waste type in this table if accepted at the landfill
BOD5
Field conductivity (at 25°C)
Field pH
Alkalinity
Cadmium
Chloride
COD
Hardness (Total, Ca + Mg)
Iron
Lead
Manganese
Mercury
Ammonia nitrogen
Total Kjeldahl nitrogen
Sodium
Sulfate
Total organic carbon (TOC)
Total suspended solids
VOC scan3VOCs
BOD5
Field conductivity (at 25°C)
Field pH
Alkalinity
Boron
Cadmium
Chloride
COD
Hardness (Total, Ca + Mg)
Iron
Lead
Manganese
Mercury
Selenium
Total suspended solids
Additional Parameters for CCR Landfills
Antimony
Beryllium
Cobalt
Fluoride
Lithium
Molybdenum
Ra226 and Ra228 combined
Sulfate
Thallium
BOD5
Field conductivity (at 25°C)
Field pH
Alkalinity
Cadmium
Chloride
COD
Fluoride
Hardness (Total, Ca + Mg)
Iron
Lead
Manganese
Mercury
Sodium
Sulfate
Total suspended solids
VOC scan3VOCs
Annual Monitoring Parameters
Semivolatile organic compound scan4 compounds (SVOCs)
Semivolatile organic compound scan4 SVOCs
Semivolatile organic compound scan4 SVOCs
Semivolatile organic compound scan4 SVOCs
1 Leachate monitoring for other solid waste not included in this table may be done as specified by the department in writing.
2 Leachate samples may not be filtered. The color, odor and turbidity shall also be noted recorded for all samples in accordance with ss. NR 507.17 (1) (b) and 507.26 (1), but do not need to be reported in electronic format.
3 Refer to ch. NR 507 Appendix III for a list of the individual volatile organic compoundsVOCs required for a VOC Scan.
4 Refer to ch. NR 507 Appendix IV for a list of the individual semivolatile organic compounds SVOCs required for a semivolatile organic compound scan.
128Section 128   NR 507 Appendix I, Table 4A is created to read:
Table 4A
LEACHATE RECIRCULATION MONITORING1
Monitoring Point Type
Parameters
Monitoring and
Reporting Frequency
Leachate collection system (per leachate drainage basin for liquid mass balance)
Volume of leachate extracted
Volume of leachate recirculated
Precipitation
Record monthly2
Leachate head well
Depth of leachate3
Elevation, leachate head
Monitor monthly in each leachate drainage basin where recirculation has been implemented
Report semi-annually
Leachate collection tank or sump
BOD5
Ammonia nitrogen
Field pH
Field conductivity (at 25°C)
Alkalinity
Hardness (Total, Ca + Mg)
Monitor quarterly
Report semi-annually
VOCs4
Monitor and report semi-annually
Gas collection system (per leachate drainage basin)
Gas volume extracted (1,000 cu ft./month)
Monitor monthly
Report semi-annually
(continues 3 years after recirculation)
Gas extraction well
Percent open interval (gas well screen)5
Depth of leachate6
Monitor and report annually
1 Leachate samples may not be filtered. The color, odor, and turbidity shall also be recorded for all samples in accordance with ss. NR 507.17 (1) (b) and 507.26 (1), but do not need to be reported in electronic format.
2 Report annually in annual report. Not reported in electronic format.
3 Measurement of leachate head on the liner, in feet.
4 Refer to ch. NR 507 Appendix III for a list of the individual VOCs required.
5 Refer to s. NR 506.07 (4r).
6 Vertical measurement of liquid in gas extraction well, in feet.
129Section 129   NR 507 Appendix I, Table 5 is amended to read:
Table 5
DETECTION LYSIMETER MONITORING
FOR ALL LANDFILLS1,2
Municipal Solid Waste
Municipal Solid Waste Combustor Residue
Paper Mill Sludge
Fly or Bottom Ash
Foundry Waste
The volumes of lysimeter fluid removed shall be recorded at least monthly and reported to the department semi-annually.
Semi-annual Monitoring Parameters
Field conductivity
(at 25°C)
Field pH
Alkalinity
Hardness (Total, Ca + Mg)
Chloride
COD
Total Kjeldahl nitrogen
Sodium
Sulfate
Other parameters specified by waste type in this table if accepted at the landfill
Field conductivity
(at 25°C)
Field pH
Alkalinity
Cadmium
Hardness (Total, Ca + Mg)
Chloride
COD
Lead
Total Kjeldahl nitrogen
Sodium
Sulfate
Field conductivity
(at 25°C)
Field pH
Alkalinity
Hardness (Total, Ca + Mg)
Chloride
COD
Total Kjeldahl nitrogen
Sodium
Sulfate
TOC
Field conductivity
(at 25°C)
Field pH
Alkalinity
Boron
Hardness (Total, Ca + Mg)
Chloride
COD
Total Kjeldahl nitrogen
Sulfate
Field conductivity
(at 25°C)
Field pH
Alkalinity
Hardness (Total, Ca + Mg)
Chloride
COD
Fluoride
Total Kjeldahl nitrogen
Sulfate
Annual Monitoring Parameters
VOC scan3VOCs
VOC scan3VOCs
VOC scan3VOCs
VOC scan3VOCs
1 Lysimeter monitoring for landfills accepting waste not included in this table shall be done as specified by the department in writing.
2 Lysimeter samples may not be filtered. When only small sampling volumes are obtained, the VOC scan analysis shall take precedence. The color, odor and turbidity shall also be noted recorded for all samples in accordance with ss. NR 507.17 (1) (b) and 507.26 (1), but do not need to be reported in electronic format.
3 Refer to ch. NR 507 Appendix III for a list of the individual volatile organic compounds VOCs required for a VOC scan.
130Section 130   NR 507 Appendix I, Table 6 is created to read:
Table 6
GAS MONITORING FOR LANDFILLS ACCEPTING
MUNICIPAL SOLID WASTE
Monitoring Point Type
Parameters
Monitoring and
Reporting Frequency
Gas extraction well1
Header pressure (inches of water)
Well head pressure (inches of water)
Gas temperature (deg. F)
Carbon dioxide (volume %)
Methane (volume %)
Oxygen (volume %)
Gas flow rate (SCFM)
Balance Gas (volume %)
Monitor monthly
Report semi-annually
Percent open interval (gas well screen)2
Depth of leachate3
Monitor and report annually
Blower / Compressor4
Header pressure (inches of water)
Gas temperature (deg. F)
Carbon dioxide (volume %)
Methane (volume %)
Oxygen (volume %)
Gas flow rate (SCFM)
Balance gas (volume %)
Gas volume extracted (1,000 cu ft./month)
Monitor monthly
Report semi-annually
Total reduced sulfur (ppmv as S)
VOCs
Monitor and report annually
Gas monitoring well (gas probe)
Methane (volume %)
Oxygen (volume %)
Monitor and report quarterly5
Site conditions
Ground conditions6
Ambient air temperature (deg. F)
Barometric pressure (mm of Hg)
Trend in barometric pressure
Monitor and report in conjunction with each gas probe monitoring event
1 The monitoring program for a temporary vertical or horizontal gas extraction well shall be the same as a permanent vertical gas extraction well. The intended use, design, and monitoring for a temporary well shall be included in the landfill's plan of operation.
2 Refer to s. NR 506.07 (4r).
3 Vertical measurement of liquid in gas extraction well, in feet.
4 Monitoring points may be shared with other licensed landfills at a facility; however, at a minimum each licensed landfill shall include a point where landfill gas quality and flow rate parameters are monitored and reported to evaluate gas collection from each licensed landfill separately.
5 The monitoring interval for gas monitoring wells during the active life and proof of owner financial responsibility portion of the perpetual long-term care period shall be no less frequent than quarterly.
6 Note whether the ground is frozen, wet, or dry.
_Hlk173090332Section 131   NR 507 Appendix III is amended to read:
VOLATILE ORGANIC COMPOUNDS FOR DETECTION MONITORING1
AT MUNICIPAL SOLID WASTE LANDFILLS
(See PDF for image)
Common name2
CAS RN3
Synonyms
Acetone1
67-64-1
2-Propanone
Benzene
71-43-2
Bromodichloromethane
75-27-4
Dichlorobromomethane
Bromoform
75-25-2
Tribromomethane
Carbon disulfide1
75-15-0
Carbon tetrachloride
56-23-5
Tetrachloromethane
Chlorobenzene
108-90-7
Monochlorobenzene
Chloroethane
75-00-3
Ethyl chloride
Chloroform
67-66-3
Trichloromethane
Dibromochloromethane
124-48-1
Chlorodibromomethane
1,2-Dibromo-3-chloropropane
96-12-8
DBCP
1,2-Dibromoethane
106-93-4
EDB; Ethylene dibromide
o-Dichlorobenzene
95-50-1
1,2-Dichlorobenzene
m-Dichlorobenzene
541-73-1
1,3-Dichlorobenzene
p-Dichlorobenzene
106-46-7
1,4-Dichlorobenzene
Dichlorodifluoromethane
75-71-8
Freon 12, Difluorodichloromethane
1,1-Dichloroethane
75-34-3
1,2-Dichloroethane
107-06-2
Ethylene dichloride
1,1-Dichloroethylene
75-35-4
Vinylidene chloride
cis-1,2-Dichloroethylene
156-59-2
cis-1,2-Dichloroethene
trans-1,2-Dichloroethylene
156-60-5
trans-1,2-Dichloroethene
1,2-Dichloropropane
78-87-5
cis-1,3-Dichloropropylene
10061-01-5
cis-1,3-Dichloropropene, Z-Dichloropropylene
trans-1,3-Dichloropropylene
10061-02-6
trans-1,3-Dichloropropene, E-Dichloropropylene
Ethylbenzene
100-41-4
Methyl bromide
74-83-9
Bromomethane
Methyl chloride
74-87-3
Chloromethane
Methylene bromide
74-95-3
Dibromomethane
Methylene chloride
75-09-2
Dichloromethane
Methyl ethyl ketone1
78-93-3
2-Butanone; MEK
Methyl tert-butyl ether
1634-04-4
MTBE
Naphthalene
91-20-3
Styrene
100-42-5
Ethenylbenzene
Tetrachloroethylene
127-18-4
Perchloroethylene; Tetrachloroethene; PCE
Tetrahydrofuran1
109-99-9
THF
Toluene
1,2,4-Trichlorobenzene
108-88-3
120-82-1
Methylbenzene
1,1,1-Trichloroethane
71-55-6
Methylchloroform
1,1,2-Trichloroethane
79-00-5
Trichloroethylene
79-01-6
Trichloroethene; TCE
Trichlorofluoromethane
75-69-4
Fluorotrichloromethane, Freon 11
Vinyl chloride
75-01-4
Chloroethene
Xylene (total) [see note 4]
1330-20-7
Dimethylbenzene
11. Includes the individual Volatile Organic Compounds (VOCs) necessary when a VOC VOCs scan is are required under ch. NR 507. Acetone, Carbon disulfide, Methyl ethyl ketone, and Tetrahydrofuran are exempted if EPA Method 8021 is used for the analysis.
22. Common names are those widely used in government regulations, scientific publications and commerce; synonyms exist for many chemicals.
33. Chemical Abstracts Service registry number.
44. Xylene (total): This entry includes o-xylene (CAS RN 96-47-6), m-xylene (CAS RN 108-38-3), p-xylene (CAS RN 106-42-3), and unspecified xylenes (dimethylbenzenes) (CAS RN 1330-20-7).
Note: Wisconsin DNR GEMS parameter numbers for the substances listed in ch. NR 507 Appendix III can be found at http://www.dnr.wi.gov/org/aw/wm/monitor/. https://dnr.wisconsin.gov/topic/Landfills/Data.html.
132Section 132   NR 508.04 (title), (intro.) and (3) are amended to read:
NR 508.04 Responses when a groundwater standard is attained or exceeded at any groundwater monitoring well or water supply well. If a PAL, ACL, or ES is attained or exceeded at any groundwater monitoring well or water supply well according to s. NR 140.14 and the value is confirmed, the owner or operator shall comply with subs. (1) and (2) and may be required, either by the department or under s. NR 508.05 (5), to comply with subs. (3) and (4).
(3) The owner or operator shall implement immediate or interim actions in accordance with ch. NR 708 if warranted or directed by the department. If required by the department, the owner or operator shall develop a site investigation workplan and a site investigation report in accordance with ss. NR 716.05 to 716.11 and 716.15 to 716.17. If a site investigation report is submitted under s. NR 716.15, it shall include proof of financial responsibility to comply with s. NR 520.05 (1). The department may impose additional requirements on the owner or operator based on the results of the site investigation in accordance with s. NR 716.17.
133Section 133   NR 508.05 (2), (3) (b), and (5) (a) are amended to read:
NR 508.05 (2) The department may approve an alternate assessment monitoring program if the only parameters which that are at or above the groundwater standards are the indicator parameters or the inorganic detection monitoring parameters listed in ch. NR 507 Appendix I, Table 1Tables 1 to 2.
(3) (b) Annually, the owner or operator shall sample and analyze the leachate for the parameters listed in ch. NR 507 Appendix II. Within 14 days after obtaining the laboratory reports the leachate sampling results, the owner or operator shall place the results in the operating record. Within 60 90 days after of the end of the sampling period, the owner or operator shall submit the leachate sampling results to the department.
(5) (a) Notify the clerk of each municipality within which the landfill is located and whose boundary is within 1,200 1,500 feet of the limits of filling of any sampling result which that exceeds an enforcement standard. The owner or operator shall notify the clerk Notification shall be completed for each sampling event with a confirmed ES attainment or exceedance within 14 days of receiving the sample result.
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