Mich. Admin. Code R. 29.2155 - Assessing site at closure or change in service
Rule 55. Section 280.72 is amended by to read as follows:
Section 280.72.
(a) Before permanent closure or a change in
service is completed, owners and operators shall measure for the presence of a
release where contamination is most likely to be present at the UST site. In
selecting sample types, sample locations and measurement methods, owners and
operators shall consider the method of closure, the nature of the stored
substance, the type of backfill, the depth to ground water, and other factors
appropriate for identifying the presence of a release. The requirements of this
section are satisfied if 1 of the external release detection methods allowed in
section 280.43(e) and (f) is operating in accordance with the requirements in
section 280.43 at the time of closure, and indicates no release has
occurred.
(b) If contaminated soils,
contaminated groundwater, or visible NAPL as a liquid or vapor is discovered,
under subsections (a) or (c) of this section or in any other manner, then the
owners and operators shall report a confirmed release in accordance with
section 280.61 and begin corrective action in accordance with subpart F of
these rules and part 213 of 1994 PA 451, MCL 324.21301a to 324.21334.
(c) Visible or olfactory evidence of a
regulated substance in the UST excavation constitutes a confirmed release.
Positive indication from field screening instruments constitutes a suspected
release.
(d) Upon closure or a
change in service of an UST, the owners and operators shall perform a site
assessment in compliance with either of the following provisions:
(1) Two soil borings must be taken as close
as practical to the tank, but not more than 5 feet from the tank. One boring
must be taken at each end of the tank, but not more than 2 feet below the
bottom of the tank and the boring must be taken at the bottom of each end of
the tank.
(2) Upon removal of an
UST, the owners and operators shall perform a site assessment in compliance
with either of the following provisions:
(i)
One discrete sample must be taken from the excavation floor underneath the fill
pipe area for each tank removed and 1 discrete sample must be taken from the
excavation floor underneath the opposite end of the tank.
(ii) One water sample must be taken if the
entire floor of the excavation is covered with water or a 1-for-1
water-for-soil sample must be taken if the excavation is partially covered with
water.
(e)
Additional sample or samples must be taken when deemed necessary by the
department or the person who performs the site assessment.
(f) A site assessment for piping must be
performed after emptying and purging the piping run or after the removal of
piping. The site assessment shall consist of 1 discrete sample for every 30
feet of the underground piping run, starting at the dispenser location or the
furthest point from the tank and moving towards the tank.
(g) Samples must be analyzed using the
following testing methods:
(1) An appropriate
method listed in the United States environmental protection agency standard
entitled "Test Methods For Evaluating Solid Waste; Physical/Chemical Methods,"
SW-846 document.
(2) Other testing
methods determined by the department to be equally effective in assessing the
level of contamination.
(h) Copies of site assessment results must be
submitted to the department within 45 days of the sampling date, together with
the site assessment report form provided by the department. The owner and
operator shall complete the information specified on the form and shall provide
a site map that indicates the location of tanks and piping and that identifies
the depth and location of the samples taken. The site assessment report shall
also include a copy of the laboratory report that indicates the test methods
used in the analyses and the chain of custody of the
samples.
Notes
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