No permit is required for land application of the following
solid wastes under the following circumstances. (Land applications that do not
comply with these rules must have obtained a permit under rule
121.7(455B).)
(1)
Solid
wastes. Solid wastes (other than petroleum contaminated soil) may be
land applied without permit if the land application does not violate the
following:
a. Land application of sludge and
other solid waste shall be conducted in accordance with the following criteria:
(1) The maximum application rate shall not
exceed two tons per acre per year, measured on a dry weight basis. The maximum
application rate shall be reduced if soil tests indicate that a two ton per
acre per year rate would provide nutrient levels significantly in excess of
crop nutrient requirements or would provide heavy metals concentrations in the
soil at levels which may be detrimental to crop production or hazardous to
human health.
(2) The sludge or
solid waste shall be applied only to soils classified as acceptable throughout
the top five feet of soil profile. The acceptability of a soil shall be
determined using the following chart based on USDA soil classifications.
Click here
to view image
Silt-size fraction (%) U.S.D.A. textural classification
chart, Sand size particles 2-0.05 mm, silt-size particles, 0.05-0.002 mm; and
clay size particles; less than 0.002 mm.
(3) Land application sites shall have soil pH
maintained between 6.5 and 8.4 for sludges with cadmium levels up to 15 mg/kg.
The soil pH may be maintained below 6.5 but not below 6.0 if the cadmium level
is 8.0 mg/kg or the sludge has been stabilized to a pH of 10-12. If the soil pH
is below these levels, it is acceptable to use agricultural lime to increase
the pH to an acceptable level prior to land application of sludge.
(4) The department recommends that all sludge
be injected on the contour or applied to the surface and mechanically
incorporated into the soil as soon as possible but not later than 48 hours
after application.
(5) If the
sludge is applied to land on which the soil loss exceeds the soil loss limits
established by the county soil conservation district, the sludge shall be
injected on the contour or shall be applied to the surface and mechanically
incorporated into soil within 48 hours of application. The sludge shall not be
applied to ground having greater than 9 percent slope.
(6) If the sludge is applied to land subject
to flooding more frequently than once in ten years, the sludge shall be
injected or shall be applied to the surface and mechanically incorporated into
the soil within 48 hours. Information on which land is subject to flooding more
frequently than once in ten years is available from the department.
(7) Sludge application on frozen or
snow-covered ground should be avoided. If application on frozen or snow-covered
ground is necessary, it shall be limited to land areas of less than 5 percent
slope.
(8) If sludge is applied
within 200 feet of a stream, lake, sinkhole or tile line surface intake located
downgradient of the land application site, it shall be injected or applied to
the surface and mechanically incorporated into the soil within 48 hours of
application.
b. The waste
shall not be land applied or made available for land application if the waste
contains constituents in excess of the levels specified below.
|
Constituents
|
Levels
|
Cumulative Loading
Rate
|
|
Arsenic
|
41 mg/kg
|
41 kg/ha
|
36 lb/ac
|
|
Cadmium
|
39 mg/kg
|
39 kg/ha
|
34 lb/ac
|
|
Chromium
|
1200 mg/kg
|
3000 kg/ha
|
2670 lb/ac
|
|
Copper
|
1500 mg/kg
|
1500 kg/ha
|
1335 lb/ac
|
|
Lead
|
300 mg/kg
|
300 kg/ha
|
267 lb/ac
|
|
Mercury
|
17 mg/kg
|
17 kg/ha
|
15 lb/ac
|
|
Molybdenum
|
75 mg/kg
|
75 kg/ha
|
66 lb/ac
|
|
Nickel
|
420 mg/kg
|
420 kg/ha
|
373 lb/ac
|
|
Selenium
|
36 mg/kg
|
100 kg/ha
|
89 lb/ac
|
|
Zinc
|
2800 mg/kg
|
2800 kg/ha
|
2490 lb/ac
|
If the waste has other toxic constituents, the toxic
constituents shall not be in excess of levels where there is a threat to human,
animal, or plant life as determined by the department.
c. Macronutrients.
(1) The application of nitrogen available
from the waste and any other sources does not exceed the nitrogen needs of the
vegetation to be grown on the site over the next year, and
(2) The total application of phosphorus and
potassium does not exceed the acceptable agronomic application rates for the
site and crops involved.
d. The waste does not have a sodium
absorption ratio in excess of levels where there is a threat to plant life. If
high sodium absorption ratios are suspected, analytical testing may be
required.
e. Stabilized sludge. If
land applying sludge or other wastes containing pathogens, the waste must be
treated to reduce pathogen content by methods specified in 567-Chapter 67 prior
to land application.
f. The waste
does not contain a waste having direct process stream contact with the
following listed organics: Petroleum products, organic solvents, pesticides,
pharmaceuticals, polychlorinated biphenyls (PCBs). The waste does not originate
from a process which may release the previously mentioned compounds.
g. Assimilation capabilities. The waste would
not be readily present in a visual analysis of a random sample collected two
years following application.
h.
General public health aspects. The waste is not putrescible, or is incorporated
(or otherwise managed) to prevent runoff and odor problems.
i. Separation distance. Waste shall not be
applied within 200 feet of an occupied residence nor within 500 feet of a
well.
j. Operating requirements. A
generator who intends to dispose of its waste by land application shall:
(1) Analyze the waste to determine if any
sources exist which may contribute significant quantities of potentially
hazardous chemicals or other toxic substances. If any are found, the generator
shall inform the department of their presence and shall analyze the waste for
chemicals or substances in accordance with guidelines provided by the
department.
(2) Sample and analyze
the waste to determine whether it meets the criteria in 121.6(1).
(3) Unless rules for specific programs under
USEPA or department authority provide otherwise, or unless other methods are
approved by the department for a specific situation, samples taken and analyses
made to document contamination under this chapter shall be conducted in
accordance with the following:
1. Samples. "A
Compendium of Superfund Field Operations Methods," USEPA, Office of Emergency
and Remedial Response, Washington, D.C. 20460 (EPA/540/p-87/001, OSWER
Directive 93.55.0-14).
2. Analyses.
"Test Methods for Evaluation of Solid Waste, Physical - Chemical Methods
SW-846," USEPA, Third Edition, November 1986, as revised through December 1988.
Until the department adopts rules regarding certification of laboratories,
analyses shall be conducted at a laboratory that certifies to the department
that the approved analytical procedure has been utilized, or a laboratory which
has been approved under EPA's Contract Laboratory Program. Upon adoption of
rules by the department regarding certification of laboratories, all analyses
shall be made at a certified laboratory.
k. Land application program. All generators
intending to land apply their waste routinely shall establish and maintain in
writing a long-range program for land application of its waste. This program
shall be developed for a minimum period of five years and shall be updated
annually. A copy of this program shall be available at the facility for
inspection by the department. As a minimum this program shall contain the
following information in detail for the next calendar year and in general terms
for the following four years. The plan shall include, but not be limited to,
the following:
(1) An outline of the waste
sampling schedule and procedures which will be followed to ensure that the
waste being applied to land continues to meet the criteria in
121.6(1).
(2) A determination of
the amount of land required to allow disposal to be conducted in accordance
with the requirements of 121.6(1).
(3) An identification of the land and waste
application methods which will be used to dispose of the waste. Those areas and
application methods shall be selected as necessary to ensure that land
application can be conducted in accordance with the land application criteria
in 121.6(1).
(4) The names of the
owners and operators of all land to be used for waste disposal, and
identification of any legal arrangements made relative to use of these areas.
The programs should also outline any restrictions or special conditions which
exist regarding use of these areas for waste disposal.
(5) An overall schedule for the disposal of
the waste. This schedule should indicate the areas being used, the time of year
that disposal on each area will be conducted, and the proposed application
rates for each area.
(6) A
determination of the types and capacities of the equipment required to dispose
of the waste in accordance with the developed disposal schedule. The program
shall also outline how the required disposal equipment will be made available
and who will be responsible for conducting land disposal operations.
(7) A determination of the volumes and types
of storage and handling facilities required to allow waste disposal to be
conducted in accordance with the waste disposal schedule. The program shall
also outline how any required additional waste storage or handling facilities
will be provided.
(8) A plan to
construct or obtain any additional waste storage, handling or disposal
facilities or equipment which are required by the waste disposal
program.
l. Other
requirements.
(1) If the waste is being
supplied to other persons for land application, the generating facility shall
inform them of the applicable requirements of the waste disposal program,
567-subrules 101.3(2) and 121.6(1).
(2) If the generating facility determines
that a person being supplied waste for land application is not complying with
applicable requirements of the waste disposal program or the land application
criteria, the generating facility shall work with them to obtain compliance
with the requirements. If subsequent compliance cannot be achieved, the
generating facility shall not supply additional waste to the person.
(3) The generating facility must inform all
persons involved in waste disposal operations of the potential health hazards
associated with waste disposal, including informing them of the cautions and
recommended practices which should be followed to minimize these
hazards.
(4) The generating
facility shall maintain records of sample analysis and waste disposal
operations to document compliance with
567-121.6 (455B).
(5) If waste is applied to land subject to
use by the general public (e.g., golf courses, parks), public access to the
waste application site shall be restricted for a period of one month after
waste application. In no case shall waste be applied to areas where direct body
contact with the soil is likely (e.g., school yards, playground areas, picnic
areas).
(6) Waste shall not be
applied to land for the commercial production of human consumption food
crops.
(7) If sludge is applied to
land where crops being grown will be grazed by or fed to livestock within two
months of sludge application, or where cereal grains will be harvested within
two months of sludge application, the sludge shall be injected or shall be
applied to the surface and mechanically incorporated into the soil.
m. Notification. Before opening a
disposal site the department shall be notified in writing of the location of
the disposal operation. This notice shall also contain the legal description of
the site, the landowner, the responsible official, the quantities and type of
waste (including chemical analyses which the department may require to
adequately define the waste).