IESNA RP-27 2-2000 Recommended Practice for Photobiological Safety for Lamps & Lamp Systems - Measurement Techniques.pdf
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1、ANS I/ I ES NA R P-2 7 2-00 Recommended Practice for Photobiological, Safety forLamps Spectroradiometry Consulting, P.O. Box 2747 La Plata, MD 20646-2747 USA (1997) Sliney, D. H. and Wolbarsht, M. L., Safety With Lasers and Other Optical Sources, Plenum, New York (1 980) 4.0 MEASUREMENT CONDITIONS 4
2、.1 Lamp Seasoning To maintain stable output during the measurement process and provide reproducible results, lamps shall be seasoned for an appropriate period of time. During the initial period of operation a lamp will change as its components come to equilibrium. If measurements are taken of an uns
3、easoned lamp, the variations with- in the measurement period and between measure- ments will be significant. As the output of a lamp gen- erally decreases over life, the seasoning time should be short to result in conservative hazard evaluations. Seasoning of lamps shall be done as stated in IESNA L
4、M-54. For the purposes of these standards, the lamp output at the end of the seasoning period is the initial output. For lamps not covered by the LM-54 standard, a study may be required to find the minimum time required to stabilize the operation of a source. 4.2 Test Environment Measurements shall
5、be made in a controlled environ- ment. The operation of sources and measurement equipment is impacted by environmental factors. Additionally, the formation of ozone in the measure- ment path may compromise accuracy and may pre- sent a safety hazard. 4.3 Temperature The ambient temperature will signi
6、ficantly influence the output of certain light sources; e.g., fluorescent lamps. The ambient temperature in which measure- ments are taken shall be maintained in accordance with the appropriate IESNA LMs noted in Section 3.1. 4.4 Drafts The characteristics of some light sources are signifi- cantly a
7、ffected by drafts. For the applicable light source, refer to the appropriate IESNA LM guides noted in Section 3.1. Other than normal convection air, air movement over the surface of test lamps should be reduced as much as possible consistent with safety considerations (ozone production). When the sy
8、stem under test provides interlocks that maintain circulation, measurements shall be performed with circulation. 4.5 Extraneous Radiation Careful checks should be made to ensure that extra- neous sources of radiation and reflections do not add significantly to the measurement results. Visually black
9、 surfaces can be highly reflective to UV and IR radiation. 2 ANSI / IESNA RP-27.2-00 Radiation from hot baffles must be considered in infrared measurements due to the large input angle subtended by baffles. Water cooled baffles and double baffles are two methods for addressing baffle heating. 4.6 La
10、mp and Lamp System Operation The lamp or lamp system shall be operated under conditions that are standardized. 4.6.1 Lamp Operation The input power to the test lamp shall be provided in accordance with the appropriate LM standard noted in Section 3.1. If no standard for the lamp type exists, the lam
11、p manufacturers recommendation for opera- tion should be used. 4.6.2 Lamp System Operation The power source for a complete lamp system shall be at the manufacturers principal specified operating voltage for the device. If the specified condition is a voltage range, the highest nominal value shall be
12、 used. The supply voltage should not vary more than plus or minus one half percent, (10.5 Yo), during the test. For AC operation, the supply frequency should not vary more than plus or minus one half percent, (k0.5 %), and the root mean square (RMS) value sum- mation of the harmonics components shou
13、ld not exceed three percent, (3 Yo) of the total. 4.6.3 Safety The systems tested are unknown in their optical haz- ard and shall be treated as hazardous unless proven otherwise. The possible formation of ozone presents a health hazard and shall be addressed for all sources with the exception of tho
14、se sources with an envelope known to block ozone forming UV. The operation of some light sources in a laboratory environment may require compromises in operation. No compromises shall be made that impact electrical safety. The sources under test may pose additional hazards (e.g., burn, explosion) wh
15、ich shall be addressed with appropriate measures. 5.0 MEASUREMENT INSTRUMENTATION 5.1 Recommended Measurement Instrumen- tation - Double Monochromator The measurement of a source for the purpose of haz- ard classification requires accuracy during calibration and testing. The detectors broad spectral
16、 response and high spectral resolution required to provide accu- rate weighting leads to stringent requirements for out- of-band stray light rejection. Calibration sources pro- vide wide spectral output, which needs to be rejected out of the pass-band. The ratio of out-of-band energy to pass-band en
17、ergy at 270 nm for tungsten halogen incandescent calibration lamps (e.g., the FEL) is 1. The double monochromator is the only instrument that provides the needed selectivity, and it is recommend- ed for hazard measurements involving UV and visible radiation. It is recognized that monochromator sys-
18、tems introduce limitations in convenience and speed. 5.1.1 Instrument Spectral Response The shape of the spectral response and the ratio of the measurement interval to the bandwidth will deter- mine whether the system is able to accurately mea- sure signals with narrow spectral extent, for example a
19、tomic emission lines. (See Kostkowski, Chapter 5.) A monochromator with perfect triangular spectral response used in a system that has a reporting inter- val that divides into the bandwidth integrally will accu- rately measure all signals regardless of their spectral shape. (See CIE 63, Section 1.8.
20、4.2.1 or Koctkowski 1997, Section 5.9.) Deviations from this may lead to errors in measured energy. The spectral response of the system is determined by a spectral scan of a nar- row isolated spectral line, e.g., filtered laser or atomic emission, using scan steps much smaller than the instruments b
21、andwidth. The resulting spectrum is a mirror image of the systems spectral response. The spectral response is what would be found by holding the instrument at a single wavelength and noting the response to a monochromatic source whose wave- length is varied around the that wavelength. (See Kostkowsk
22、i 1997, Section 4.9.) The systems ability to accurately measure the energy in a narrow band sig- nal is the sum of the spectral responses at each reported wavelength. The variation across the summed spectrum is the potential error in total mea- sured signal and shall be included in the uncertainty a
23、nalysis. The result of hazard evaluations will be influenced by the instruments characteristics. The bandwidth of the monochromator will change the weighted results of any spectrum with varying levels. All finite bandwidth instruments report signal at the wrong wavelength, leading to errors in a wei
24、ghted sum. Table 1 lists the recommended bandwidth for 2 per- cent upper bound of uncertainty in weighted sums. 3 ANSI / IESNA RP-27.2-00 Range (nm) ! Bandwidth (FWHM) 1 5 4nm Table 1. Recommended Bandwidths A more complete analysis that takes the source spec- trum into account may be used to relax
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