ACIS QE Contamination
Introduction
The effective low-energy ACIS QE is lower now than it was at launch. This problem is thought to be associated with the deposition of one or more materials on the ACIS detectors or optical blocking filters. Since the depth of these contaminants is growing with time, the effective low-energy QE is becoming lower as time passes. A correction for this contamination is incorporated when creating ACIS response files.
The ACIS QE contamination model also accounts for spatial variations in the contamination on the ACIS optical blocking filters. The contamination is expressed as a function of time, energy, and ACIS chip coordinates. For imaging analysis of extended sources or point sources far off-axis, there is a significant change in instrument and exposure maps when the calibration is applied.
The response tools are designed to incorporate corrections for ACIS contamination via ARDLIB and a CALDB contamination file. The necessary calibration files have been available since CALDB 2.26 (2 February 2004) and most recently updated in CALDB 4.8.5 (07 November 2019).
The version N0013 model is the result of recent (2018 through mid-2019) ACIS monitoring and modeling—of the blazar Mkn 421 and galaxy cluster Abell 1795, and supplemented by calibration observations of the supernova remnant 1E 0102-72.3—indicates that the N0011/N0012 contamination model, which describes the accumulation of the contaminant leveling off in 2017, disagreeing with this trend and suggests the resumption of the rapid rate of accumulation observed prior to 2016.
To learn about the previous versions of the contamination model, particularly the version N0011/N0012 models, can be found.
The overall affect of the contaminant build-up is best illustrated using the convolved spectra from Abell 1795—a stable source observed annually for calibration purposes since the start of the mission—demonstrating the loss of ACIS-S effective area over time.
ACIS-S Time-Evolution
Technical Details
As the Chandra mission proceeds, the contamination on the ACIS Optical Blocking Filters (OBF) for ACIS-I and ACIS-S continues to evolve, with a marked increase in the rate of accumulation since the middle of 2009 and a slow down in more recent years, beginning in 2016.
The contamination model was developed on top of the systemmatic procedure—using observations of standard sources A1795 and Mkn 421, on ACIS-I and ACIS-S separately— and supplemented with observations of the astronomical calibration source 1E 0102-72.3. New enhancements in the temporal model adds additional complexity to the layers of several model components (C, O, and F) known to dominate the chemical composition of the contaminating layer on the ACIS OBF introduced in the N0011 and N0012 contamination models for ACIS-I and ACIS-S, respectively. The spatial model introduced in N0010, gives more consistent results at off-axis pointings on both ACIS-I and ACIS-S. The issues with the lack of knowledge on the contamination layer optical depth at high CHIPY locations on ACIS-S3 caused problems in prior models, but the spatial model allows for asymmetry in the ACIS-S CHIPY contamination layer to provide better fits.
For both ACIS-I and ACIS-S, the new models only have a minor affect on the pre-2005 EAs; and while the contamination is negligible above 2.0 keV, but near the O-K absorption edge at 0.535 keV, the difference between the N0009 and N0010 models is not insignificant, so the new contamination model will affect low-energy source modeling results for observations after 2005, especially analysis where a significant portion of the considered spectrum is below 1.0 keV.
In the N0013 contamination model, based on observations from 2015-2018, it appeared that the accumulation of the contaminant was uniform across the optical blocking filters, but the recent observations since mid-2018 suggests a higher accumulation rate at the detector edges so that the spatial component has been revised to predict significantly higher optical depths at the edges compared to the prior contamination model.
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Spatial Contamination Model (center S3)
The temporal component has been revised to describe the accumulation of the contaminant with a power-law instead of a flattening model, making a notable change in the effective area below 1 keV, particularly on ACIS-I. This is based on several data points between 2016-2018 where starting in late-2017, calibration observations started to show that the predictive component of the N0010 contamination model was over-estimating the rate of accumulation on the OBF and the affects of contamination, considerably reducing the effective area of data products generated with the model across the 0.06-3.0 keV energy range compared to the true effective area. This leveling off of the contaminant build up in 2017, particularly on the ACIS-I OBF, was introduced as a modification of the N0010 contamination model in the time-dependent model for ACIS-I in the N0011 model and ACIS-S in the N0012 model—introduced in June and October 2018, respectively—and propagated into the predictive regime of the models. However, observations taken since mid-2018 through 2019 indicates that the contaminant resumed accumulating at a rapid rate on ACIS-I, resulting in the temporal model change in the N0013 contamination model.
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Temporal Contamination Model (center S3)
However, the resumption of the rapid increase in the contaminant is clear after early-2018 in the N0012 temporal model trace. The N0013 temporal model becomes linear with time at about 2016 and thereafter, which fits the 2018-2019 measurements much better without compromising earlier period performance.
Prior to the N0010 model, the absorption layers of the contaminant corresponded to specific elements known to be present: C, O, and F. However, the layers actually represent the different spectral absorption models of the components of the contaminant. The details of the absorption model depend on the chemical bonding of the molecules that comprise the material, but there are at least two different model components with different C:O:F ratios, implying the molecules are unlikely to have the same bonding structure.
The near edge structure of the absorption model is particularly sensitive to these types of bonds and the transmission grating spectra show that the F-K and O-K near edge structures are time-dependent. To avoid excess absorption near the edge, an additional layer each of F and O, having no near edge structure, were added. These simple, Henke-like edges have been assigned different time dependencies than the versions of the F and O opacities that have clear structure near the edges.
ACIS-I3 contamN0013 Effective Areas
The effective area traces for 2000, 2005, 2010, and 2015 show only small apparent changes between the N0012 and N0013 contamination models, but for the year 2019, there is considerably more contamination affect in this soft band for the newer model, reflecting source spectra observed through 2019.
ACIS-S3 contamN0013 Effective Areas
The ACIS-S aimpoint effective area versus time, plotted for May 15th (mid-cycle date) of years 2000, 2005, 2010, 2015, 2017, 2019 (~current date), and 2022 (predictive), for the current (version N0012, dashes) and new (N0013, solid) contamination file shows that there are retroactive changes to the resulting effective areas, they are not significant for purposes of fitting/derived parameters. However, as of mid-2018, the new file begins to significantly deviate from the current model.
Additional technical information is available from:
- The Update to the ACIS Contamination Model memo (8 January 2010)
- The Contamination on the ACIS OBF and Changes in the Low Energy QE page
- The ACIS Spatial Contamination Effects memo (19 January 2005) (PDF)
- The Spatial structure in the ACIS OBF contamination memo (20 April 2004) (PDF)
-
The Composition
of the Chandra ACIS contaminant paper (August 2003)
H. L. Marshall, A. Tennant, C. E. Grant, A. P. Hitchcock, S. O'Dell, P. P. Plucinsky
Applying the Correction
The following CIAO response tools automatically take the contamination into account:
As well as the scripts which use them:
- specextract (calls mkwarf and mkarf)
- fullgarf (calls mkgarf)
- fluximage (calls mkinstmap)
- merge_obs and flux_obs (calls mkinstmap)
Each of the tools contains an ardlibparfile parameter with the value"ardlib.par." The location of the calibration file is specified in the ardlib.par file by a set of 10 parameters (one per CCD):
unix% plist ardlib | grep CONTAM AXAF_ACIS0_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS1_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS2_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS3_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS4_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS5_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS6_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS7_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS8_CONTAM_FILE = CALDB Enter ACIS Contamination File AXAF_ACIS9_CONTAM_FILE = CALDB Enter ACIS Contamination File
If anything other than "CALDB" is returned, issue the following command so that the tool will be able to find the correct file:
unix% foreach d ( 0 1 2 3 4 5 6 7 8 9 ) foreach? pset ardlib AXAF_ACIS${d}_CONTAM_FILE="CALDB" foreach? end
You may also use "punlearn ardlib" to reset all the ardlib parameters to the default values. This will also clear out any other information that has been set, however, such as bad pixel filenames.
Turning Off the Correction
It is possible to "turn off" the contamination correction, e.g. if you would like to compare results with and without it applied. To do so, the ARDLIB qualifier "CONTAM=NO" must be specified in the appropriate parameter, as given in the following table:
Tool | Parameter |
---|---|
mkarf | detsubsys |
mkgarf | detsubsys |
mkwarf | detsubsysmod |
mkinstmap | detsubsys |
There are examples in the help files on how to use the qualifier with each tool. For example, when running mkarf on an ACIS-S3 observation:
unix% pset mkarf detsubsys="ACIS-S3;CONTAM=NO"
Examining the Effects of the Correction
Comparing ARFs using Old vs. New Contamination Model
It is useful to compare ARF responses created using an older (4.7.2 or earlier) versus the newest contamination model (4.7.3) to examine the effects of the correction. One could do this by following the procedure below, which uses ACIS-S imaging observation 11800, taken in July 2010, as an example. The CIAO tool mkwarf is used to create the old and new on-axis ARF responses.
1) Find out how 'old.arf' was created using dmhistory, which will show that it was either mkarf or mkwarf (mkwarf in this example).
% dmhistory infile=old.arf tool= # dmhistory (CIAO 4.5): WARNING: Found "pixlib" library parameters # dmhistory (CIAO 4.5): WARNING: Found "ardlib" library parameters TOOL :mkwarf infile="11800_tdet.fits[wmap]" outfile="old.arf" weightfile="11800.wfef" spectrumfile="" egridspec="0.3:11.0:0.01" pbkfile="pbk0.fits" threshold="0" feffile="CALDB" mskfile="msk1.fits" asolfile="" mirror="HRMA" detsubsysmod="" dafile="CALDB" ardlibpar="ardlib" geompar="geom" clobber="no" verbose="1"
2) Re-run dmhistory, but this time, updating the mkwarf parameter file with the parameter settings returned in step 1. Check that the mkwarf parameter file was properly set by using the 'plist' command.
% dmhistory infile=old.arf tool=mkwarf action=pset # dmhistory (CIAO 4.9): WARNING: Found "pixlib" library parameters # dmhistory (CIAO 4.9): WARNING: Found "ardlib" library parameters % plist mkwarf Parameters for /home/user/cxcds_param4/mkwarf.par infile = 11800_tdet.fits[wmap] Input detector WMAP outfile = old.arf Output weighted ARF file weightfile = 11800.wfef Output FEF weights spectrumfile = Input Spectral weighting file (<filename>|NONE) egridspec = 0.3:11.0:0.01 Output energy grid [kev] pbkfile = pbk0.fits Parameter block file (threshold = 0) Percent threshold cut for FEF regions (feffile = CALDB) FEF file (mskfile = msk1.fits) Mask file (asolfile = ) Stack of aspect solution files (mirror = HRMA) ARDLIB Mirror specification (detsubsysmod = ) Detector sybsystem modifier (dafile = CALDB) Dead area file (ardlibpar = ardlib) Parameter file for ARDLIB files (geompar = geom) Parameter file for Pixlib Geometry files (clobber = no) Clobber existing outputs (verbose = 1) Tool chatter level (mode = ql)
3) After updating the CALDB to the latest version with the most recent contamination model, re-run mkwarf with these parameter settings, except for changing the outfile name to 'new.arf'. (Note that you may need to change directories or adjust the file paths depending on how things were run to create old.arf.)
% mkwarf outfile=new.arf
4) Compare the old and new ARFs by plotting them together. For this dataset, the old and new ARFs are shown below:
Comparison of old and new models
The N0012 and prior CONTAM Models
The versions N0011 and N0012 models were the result ACIS monitoring and modeling from 2015-2018 and allows for improved fits to standard extended source spectra with stable photoabsorption and other fitted parameters of their systematic models, but the degree of such a change on the results for various source models is hard to estimate without any particulars. The N0011 model is an improvement over the N0010 for the ACIS-I chips, for observations since the start of 2016, and the N0012 model is an improvement over the N0010 for the ACIS-S chips (while also incorporating the N0011 ACIS-I model). These two models were necessitated when observations made in early 2018 showed that the N0010 model overestimated the absorption affect on ACIS.
ACIS-I3 contamN0012 Effective Areas
The effective area traces for 2000, 2010, and 2016 show only small apparent changes between the N0010 and N0011 contamination models, but for the year 2018, there is considerably less contamination affect in this soft band for the newer model, reflecting source spectra observed early in 2018. It appears that an under-correction for energies above the F-K edge, at ~0.7 keV, since 2015 caused the optical depth after 2015 to gradually rise quicker in the model than which is seen in observed data over time.
ACIS-S3 contamN0012 Effective Areas
The ACIS-S aimpoint effective area versus time, plotted for May 15th (mid-cycle date) of years 2000, 2010, 2016, 2018 (~current date), and 2019 (predictive), for the current (version N0011/N0010, solid) and new (N0012, dashes) contamination file shows that there are retroactive changes to the resulting effective areas, they are not significant for purposes of fitting/derived parameters. However, as of early 2018, the new file begins significantly to address the over-estimation of the contamination effect that has been evident in the most recent observations.
The version N0010 model was the result of ACIS monitoring and modeling and allows for improved fits to standard extended source spectra with stable photoabsorption and and other fitted parameters of their systematic models. The model was applicable to ALL ACIS observations throughout the mission, and was intended to replace all previous versions.
As the Chandra mission proceeded, the contamination on the ACIS Optical Blocking Filters (OBF) for ACIS-I and ACIS-S continued to evolve, with a marked increase in the rate of accumulation starting in the middle of 2009. While the cause of the increased accumulation is not well-understood, the deposition curve appeared as nearly-linear, monotonically increasing with time.
Time-dependence (center of chips)
The rapid increase in the contaminant indicated that ACIS-S is not ideal for very soft sources in the future, particularly below the 283 eV carbon edge.
The contamination model was developed in a systemmatic procedure, using observations of standard sources A1795 and Mkn421, on ACIS-I and ACIS-S separately. The version N0010 model includes new time-dependent and spatial variation of several model components (C, O, and F) known to dominate the chemical composition of the contaminating layer on the ACIS OBF. The spatial model, in particular, is much improved over prior models, giving more consistent results at off-axis pointings on both ACIS-I and ACIS-S. The issues with the lack of knowledge on the contamination layer optical depth at high CHIPY locations on ACIS-S3 caused problems in prior models, but the new model allows for asymmetry in the ACIS-S CHIPY contamination layer to provide better fits.
ACIS-S/LEG-1 Effective Areas
The subsequent change in ACIS-I effective areas (EAs) between the N0009 and N0010 is illustrated below.
ACIS-I Effective Areas
Similarly, the change in ACIS-S EAs are illustrated below.
ACIS-S Effective Areas
The version N0008 model was released in CALDB 4.5.9, provides a more realistic model of the contaminant—without use of an artificial "fluffium" component as in previous models—resulting in a more accurate representation and prediction of current and future effective ACIS QE. Subsequently, there is a significant loss of effective area for present and future observations using the model as compared to previous models; however, early- and mid-mission effective areas are not much affected by the new model.
The version N0009 upgrade accounts for the rapid build-up of contaminant on the optical blocking filter since early-mid 2013; but is otherwise identical to the N0008 contamination model.
Time-dependence (center of chips)
Time-dependence of the contaminant spatial pattern
At high CHIPY locations on ACIS-S3 for imaging spectroscopy, there is uncertainty in the depth of the contaminant layer found in the N0008 model. Fitting results may be compromised at these locations.
The subsequent change in ACIS-I effective areas (EAs) between the N0007 and N0008 is illustrated below.
ACIS-I Effective Areas
Similarly, the change in ACIS-S EAs are illustrated below.
ACIS-S Effective Areas
For both ACIS-I and S, the new model only has a minor affect on the early- and mid-mission EAs, except for very near the C-K, O-K, and F-K absorption edges, which do not affect fitting results significantly near the edges for mid-mission observations.
The rapid increase in the contaminant indicates that ACIS-S is not ideal for very soft sources in the future, particularly below the 283 eV carbon edge.
Information on releases prior to the version N0007 model can be found in "Prior ACIS QE Contamination and CONTAM Models".