[Code of Federal Regulations]
[Title 40, Volume 13]
[Revised as of July 1, 2005]
From the U.S. Government Printing Office via GPO Access
[CITE: 40CFR63.7142]
[Page 49-50]
TITLE 40--PROTECTION OF ENVIRONMENT
CHAPTER I--ENVIRONMENTAL PROTECTION AGENCY (CONTINUED)
PART 63_NATIONAL EMISSION STANDARDS FOR HAZARDOUS AIR POLLUTANTS FOR
SOURCE CATEGORIES--Table of Contents
Subpart AAAAA_National Emission Standards for Hazardous Air Pollutants
for Lime Manufacturing Plants
Sec. 63.7142 What are the requirements for claiming area source status?
(a) If you wish to claim that your LMP is an area source, you must
measure the emissions of hydrogen chloride from all lime kilns, except
as provided in paragraph (c) of this section, at your plant using
either:
(1) EPA Method 320 of appendix A to this part,
(2) EPA Method 321 of appendix A to this part, or
(3) ASTM Method D6735-01, Standard Test Method for Measurement of
Gaseous Chlorides and Fluorides from Mineral Calcining Exhaust Sources--
Impinger Method, provided that the provisions in paragraphs (a)(3)(i)
through (vi) of this section are followed.
(i) A test must include three or more runs in which a pair of
samples is obtained simultaneously for each run according to section
11.2.6 of ASTM Method D6735-01.
(ii) You must calculate the test run standard deviation of each set
of paired samples to quantify data precision, according to Equation 1 of
this section:
[GRAPHIC] [TIFF OMITTED] TR05JA04.003
Where:
RSDa = The test run relative standard deviation of sample
pair a, percent.
C1a and C2a = The HCl concentrations, milligram/
dry standard cubic meter(mg/dscm), from the paired samples.
(iii) You must calculate the test average relative standard
deviation according to Equation 2 of this section:
[GRAPHIC] [TIFF OMITTED] TR05JA04.004
Where:
RSDTA = The test average relative standard deviation,
percent.
RSDa = The test run relative standard deviation for sample
pair a.
p = The number of test runs, =3.
(iv) If RSDTA is greater than 20 percent, the data are
invalid and the test must be repeated.
(v) The post-test analyte spike procedure of section 11.2.7 of ASTM
Method D6735-01 is conducted, and the percent recovery is calculated
according to section 12.6 of ASTM Method D6735-01.
(vi) If the percent recovery is between 70 percent and 130 percent,
inclusive, the test is valid. If the percent recovery is outside of this
range, the data are considered invalid, and the test must be repeated.
(b) If you conduct tests to determine the rates of emission of
specific organic HAP from lime kilns at LMP for use in applicability
determinations under Sec. 63.7081, you may use either:
(1) Method 320 of appendix A to this part, or
(2) Method 18 of appendix A to part 60 of this chapter, or
(3) ASTM D6420-99, Standard Test Method for Determination of Gaseous
Organic Compounds by Direct Interface Gas Chromatography-Mass
Spectrometry (GC/MS), provided that the provisions of paragraphs
(b)(3)(i) through (iv) of this section are followed:
[[Page 50]]
(i) The target compound(s) are those listed in section 1.1 of ASTM
D6420-99;
(ii) The target concentration is between 150 parts per billion by
volume and 100 parts per million by volume;
(iii) For target compound(s) not listed in Table 1.1 of ASTM D6420-
99, but potentially detected by mass spectrometry, the additional system
continuing calibration check after each run, as detailed in section
10.5.3 of ASTM D6420-99, is conducted, met, documented, and submitted
with the data report, even if there is no moisture condenser used or the
compound is not considered water soluble; and
(iv) For target compound(s) not listed in Table 1.1 of ASTM D6420-
99, and not amenable to detection by mass spectrometry, ASTM D6420-99
may not be used.
(c) It is left to the discretion of the permitting authority whether
or not idled kilns must be tested for (HCl) to claim area source status.
If the facility has kilns that use common feed materials and fuel, are
essentially identical in design, and use essentially identical emission
controls, the permitting authority may also determine if one kiln can be
tested, and the HCl emissions for the other essentially identical kilns
be estimated from that test.