Geoduck RRBS Library Prep - part 2
Prepping remaining 76 RRBS libraries for geoduck juvenile OA acclimatization study.
20161206
Chose remaining 76 samples from 88 sample set for full timepoint coverage of geoduck ocean acidification study.100ng was used as the starting amount of DNA for each sample and the volume of water in each reaction was adjusted as necessary. 0.5% unmethylated lambda DNA was spiked in (w/w DNA) to determine conversion efficiency by estimating the error rate at which a C count occurs at an unmethylated C position.
Step 1 MSPI DNA Cutting
MSPI restriction endonuclease in NEBuffer2
- MspI - 25,000U (NEB cat: R0106L)
- NEBuffer2 10x (NEB cat: B7002S)
Reaction Mix
- Samples were mixed as follows to a total reaction volume of 30µl. Samples were incubated at 37°C starting at 15:00
- Lambda DNA (581ng/µl) was diluted 1:1160 for a concentration of 0.5ng/µl and 1µl added to each sample
-
Unmethylated lamda phage DNA (Promega cat: D1501)
- 3µl NEBuffer2
- 1µl MSPI 20U/µl
- 16µl DNA (100ng)
- 10µl of H20
- 30µl total
Date | EPI.Tube.Num | Tank | Treatment | TimePoint | Homogenization | DNA.Extraction | DNA.QC | DNA.Conc.ng.µl | DNA.vol.µl | DNA.amount.µg | vol for 100ng | lambda.0.5% | Water.µl | NSBuffer2.µl | MSPI.µl |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
16-Mar-16 | EPI_41 | Time0 | Field | Day0 | 20160912 | 20161025 | 20161026 | 13.6 | 140 | 1.904 | 7.4 | 1 | 17.6 | 3 | 1 |
16-Mar-16 | EPI_42 | Time0 | Field | Day0 | 20160912 | 20161028 | 20161028 | 79 | 140 | 11.06 | 1.3 | 1 | 23.7 | 3 | 1 |
16-Mar-16 | EPI_43 | Time0 | Field | Day0 | 20160912 | 20161025 | 20161026 | 17.2 | 140 | 2.408 | 5.8 | 1 | 19.2 | 3 | 1 |
16-Mar-16 | EPI_44 | Time0 | Field | Day0 | 20160912 | 20161025 | 20161026 | 14.8 | 140 | 2.072 | 6.8 | 1 | 18.2 | 3 | 1 |
17-Mar-16 | EPI_45 | Tank11 | Low | Day1 | 20160912 | 20161028 | 20161028 | 43.1 | 140 | 6.034 | 2.3 | 1 | 22.7 | 3 | 1 |
17-Mar-16 | EPI_46 | Tank11 | Low | Day1 | 20160912 | 20161028 | 20161028 | 21.2 | 140 | 2.968 | 4.7 | 1 | 20.3 | 3 | 1 |
17-Mar-16 | EPI_47 | Tank12 | Super.Low | Day1 | 20160912 | 20161028 | 20161028 | 57.6 | 140 | 8.064 | 1.7 | 1 | 23.3 | 3 | 1 |
17-Mar-16 | EPI_48 | Tank12 | Super.Low | Day1 | 20160912 | 20161028 | 20161028 | 12.6 | 140 | 1.764 | 7.9 | 1 | 17.1 | 3 | 1 |
17-Mar-16 | EPI_49 | Tank13 | Ambient | Day1 | 20160912 | 20161025 | 20161026 | 63.4 | 140 | 8.876 | 1.6 | 1 | 23.4 | 3 | 1 |
17-Mar-16 | EPI_50 | Tank13 | Ambient | Day1 | 20160912 | 20161028 | 20161028 | 8.21 | 140 | 1.1494 | 12.2 | 1 | 12.8 | 3 | 1 |
17-Mar-16 | EPI_51 | Tank14 | Low | Day1 | 20160912 | 20161025 | 20161026 | 14.6 | 140 | 2.044 | 6.8 | 1 | 18.2 | 3 | 1 |
17-Mar-16 | EPI_52 | Tank14 | Low | Day1 | 20160912 | 20161025 | 20161026 | 9.82 | 140 | 1.3748 | 10.2 | 1 | 14.8 | 3 | 1 |
17-Mar-16 | EPI_53 | Tank15 | Ambient | Day1 | 20160912 | 20161025 | 20161026 | 27.4 | 140 | 3.836 | 3.6 | 1 | 21.4 | 3 | 1 |
17-Mar-16 | EPI_54 | Tank15 | Ambient | Day1 | 20160912 | 20161025 | 20161026 | 15 | 140 | 2.1 | 6.7 | 1 | 18.3 | 3 | 1 |
17-Mar-16 | EPI_55 | Tank16 | Super.Low | Day1 | 20160912 | 20161025 | 20161026 | 12.4 | 140 | 1.736 | 8.1 | 1 | 16.9 | 3 | 1 |
17-Mar-16 | EPI_56 | Tank16 | Super.Low | Day1 | 20160912 | 20161025 | 20161026 | 21.4 | 140 | 2.996 | 4.7 | 1 | 20.3 | 3 | 1 |
29-Jul-16 | EPI_151 | Ambient | Ambient | Day135 | 20160909 | 20161004 | 20161006 | 11.8 | 140 | 1.652 | 8.5 | 1 | 16.5 | 3 | 1 |
29-Jul-16 | EPI_152 | Ambient | Ambient | Day135 | 20160909 | 20161004 | 20161006 | 16.8 | 140 | 2.352 | 6 | 1 | 19 | 3 | 1 |
29-Jul-16 | EPI_153 | Ambient | Ambient | Day135 | 20160909 | 20161025 | 20161026 | 22.4 | 140 | 3.136 | 4.5 | 1 | 20.5 | 3 | 1 |
29-Jul-16 | EPI_154 | Ambient | Ambient | Day135 | 20160909 | 20161025 | 20161026 | 19.5 | 140 | 2.73 | 5.1 | 1 | 19.9 | 3 | 1 |
29-Jul-16 | EPI_159 | Low | Low | Day135 | 20160909 | 20161004 | 20161006 | 21.4 | 140 | 2.996 | 4.7 | 1 | 20.3 | 3 | 1 |
29-Jul-16 | EPI_160 | Low | Low | Day135 | 20160909 | 20161004 | 20161006 | 10.8 | 140 | 1.512 | 9.3 | 1 | 15.7 | 3 | 1 |
29-Jul-16 | EPI_161 | Low | Low | Day135 | 20160909 | 20161028 | 20161028 | 24.9 | 140 | 3.486 | 4 | 1 | 21 | 3 | 1 |
29-Jul-16 | EPI_162 | Low | Low | Day135 | 20160909 | 20161007 | 20161010 | 12.5 | 140 | 1.75 | 8 | 1 | 17 | 3 | 1 |
29-Jul-16 | EPI_167 | Super.Low | Super.Low | Day135 | 20160908 | 20160930 | Pass | 13.2 | 190 | 2.508 | 7.6 | 1 | 17.4 | 3 | 1 |
29-Jul-16 | EPI_168 | Super.Low | Super.Low | Day135 | 20160908 | 20160930 | Pass | 6.18 | 190 | 1.1742 | 16.2 | 1 | 8.8 | 3 | 1 |
29-Jul-16 | EPI_169 | Super.Low | Super.Low | Day135 | 20160908 | 20161007 | 20161010 | 14.8 | 140 | 2.072 | 6.8 | 1 | 18.2 | 3 | 1 |
29-Jul-16 | EPI_170 | Super.Low | Super.Low | Day135 | 20160908 | 20161007 | 20161010 | 11.2 | 140 | 1.568 | 8.9 | 1 | 16.1 | 3 | 1 |
8-Aug-16 | EPI_175 | Bin1 | Low-Ambient | Day145 | 20160908 | 20160930 | Pass | 19.6 | 190 | 3.724 | 5.1 | 1 | 19.9 | 3 | 1 |
8-Aug-16 | EPI_176 | Bin1 | Low-Ambient | Day145 | 20160908 | 20160930 | Pass | 7.84 | 190 | 1.4896 | 12.8 | 1 | 12.2 | 3 | 1 |
8-Aug-16 | EPI_181 | Bin2 | Ambient-Ambient | Day145 | 20160908 | 20161004 | 20161006 | 40.8 | 140 | 5.712 | 2.5 | 1 | 22.5 | 3 | 1 |
8-Aug-16 | EPI_182 | Bin2 | Ambient-Ambient | Day145 | 20160908 | 20161004 | 20161006 | 20.8 | 140 | 2.912 | 4.8 | 1 | 20.2 | 3 | 1 |
8-Aug-16 | EPI_184 | Bin3 | Ambient-Ambient | Day145 | 20160908 | 20161007 | 20161010 | 7.46 | 140 | 1.0444 | 13.4 | 1 | 11.6 | 3 | 1 |
8-Aug-16 | EPI_185 | Bin3 | Ambient-Ambient | Day145 | 20160907 | 20161007 | 20161010 | 18.6 | 140 | 2.604 | 5.4 | 1 | 19.6 | 3 | 1 |
8-Aug-16 | EPI_187 | Bin4 | Super.Low-Ambient | Day145 | 20160907 | 20160930 | Pass | 17.1 | 190 | 3.249 | 5.8 | 1 | 19.2 | 3 | 1 |
8-Aug-16 | EPI_188 | Bin4 | Super.Low-Ambient | Day145 | 20160907 | 20160930 | Pass | 14.5 | 190 | 2.755 | 6.9 | 1 | 18.1 | 3 | 1 |
8-Aug-16 | EPI_193 | Bin5 | Low-Ambient | Day145 | 20160907 | 20161004 | 20161006 | 9.26 | 140 | 1.2964 | 10.8 | 1 | 14.2 | 3 | 1 |
8-Aug-16 | EPI_194 | Bin5 | Low-Ambient | Day145 | 20160907 | 20161004 | 20161006 | 11.7 | 140 | 1.638 | 8.5 | 1 | 16.5 | 3 | 1 |
8-Aug-16 | EPI_199 | Bin6 | Super.Low-Ambient | Day145 | 20160907 | 20161004 | 20161006 | 21.8 | 140 | 3.052 | 4.6 | 1 | 20.4 | 3 | 1 |
8-Aug-16 | EPI_200 | Bin6 | Super.Low-Ambient | Day145 | 20160907 | 20161004 | 20161006 | 21.2 | 140 | 2.968 | 4.7 | 1 | 20.3 | 3 | 1 |
8-Aug-16 | EPI_205 | Bin7 | Ambient-Low | Day145 | 20160907 | 20160930 | Pass | 11.9 | 190 | 2.261 | 8.4 | 1 | 16.6 | 3 | 1 |
8-Aug-16 | EPI_206 | Bin7 | Ambient-Low | Day145 | 20160906 | 20160930 | Pass | 18.1 | 190 | 3.439 | 5.5 | 1 | 19.5 | 3 | 1 |
8-Aug-16 | EPI_208 | Bin8 | Low-Low | Day145 | 20160906 | 20161007 | 20161010 | 31 | 140 | 4.34 | 3.2 | 1 | 21.8 | 3 | 1 |
8-Aug-16 | EPI_209 | Bin8 | Low-Low | Day145 | 20160906 | 20161007 | 20161010 | 22 | 140 | 3.08 | 4.5 | 1 | 20.5 | 3 | 1 |
8-Aug-16 | EPI_214 | Bin9 | Super.Low-Low | Day145 | 20160906 | 20161004 | 20161006 | 13.3 | 140 | 1.862 | 7.5 | 1 | 17.5 | 3 | 1 |
8-Aug-16 | EPI_215 | Bin9 | Super.Low-Low | Day145 | 20160906 | 20161004 | 20161006 | 22.6 | 140 | 3.164 | 4.4 | 1 | 20.6 | 3 | 1 |
8-Aug-16 | EPI_220 | Bin10 | Super.Low-Low | Day145 | 20160906 | 20160930 | Pass | 48.8 | 190 | 9.272 | 2 | 1 | 23 | 3 | 1 |
8-Aug-16 | EPI_221 | Bin10 | Super.Low-Low | Day145 | 20160906 | 20160930 | Pass | 30 | 190 | 5.7 | 3.3 | 1 | 21.7 | 3 | 1 |
8-Aug-16 | EPI_226 | Bin11 | Ambient-Low | Day145 | 20160902 | 20161007 | 20161010 | 13.1 | 140 | 1.834 | 7.6 | 1 | 17.4 | 3 | 1 |
8-Aug-16 | EPI_227 | Bin11 | Ambient-Low | Day145 | 20160902 | 20161007 | 20161010 | 31.6 | 140 | 4.424 | 3.2 | 1 | 21.8 | 3 | 1 |
8-Aug-16 | EPI_229 | Bin12 | Low-Low | Day145 | 20160902 | 20160930 | Pass | 17.4 | 190 | 3.306 | 5.7 | 1 | 19.3 | 3 | 1 |
8-Aug-16 | EPI_230 | Bin12 | Low-Low | Day145 | 20160902 | 20160930 | Pass | 10.1 | 190 | 1.919 | 9.9 | 1 | 15.1 | 3 | 1 |
21-Aug-16 | EPI_235 | Bin1 | Low-Ambient | Day158 | 20160902 | 20161004 | 20161006 | 10.6 | 140 | 1.484 | 9.4 | 1 | 15.6 | 3 | 1 |
21-Aug-16 | EPI_236 | Bin1 | Low-Ambient | Day158 | 20160902 | 20161004 | 20161006 | 8.66 | 140 | 1.2124 | 11.5 | 1 | 13.5 | 3 | 1 |
21-Aug-16 | EPI_242 | Bin2 | Ambient-Ambient | Day158 | 20160902 | 20161028 | 20161028 | 15.5 | 140 | 2.17 | 6.5 | 1 | 18.5 | 3 | 1 |
21-Aug-16 | EPI_243 | Bin2 | Ambient-Ambient | Day158 | 20160902 | 20161028 | 20161028 | 17.2 | 140 | 2.408 | 5.8 | 1 | 19.2 | 3 | 1 |
21-Aug-16 | EPI_246 | Bin3 | Ambient-Ambient | Day158 | 20160902 | 20161025 | 20161026 | 19.4 | 140 | 2.716 | 5.2 | 1 | 19.8 | 3 | 1 |
21-Aug-16 | EPI_247 | Bin3 | Ambient-Ambient | Day158 | 20160902 | 20161028 | 20161028 | 8.23 | 140 | 1.1522 | 12.2 | 1 | 12.8 | 3 | 1 |
21-Aug-16 | EPI_250 | Bin4 | Super.Low-Ambient | Day158 | 20160901 | 20161025 | 20161026 | 28.2 | 140 | 3.948 | 3.5 | 1 | 21.5 | 3 | 1 |
21-Aug-16 | EPI_251 | Bin4 | Super.Low-Ambient | Day158 | 20160901 | 20161025 | 20161026 | 16 | 140 | 2.24 | 6.3 | 1 | 18.7 | 3 | 1 |
21-Aug-16 | EPI_257 | Bin5 | Low-Ambient | Day158 | 20160901 | 20161004 | 20161006 | 15.4 | 140 | 2.156 | 6.5 | 1 | 18.5 | 3 | 1 |
21-Aug-16 | EPI_258 | Bin5 | Low-Ambient | Day158 | 20160901 | 20161028 | 20161028 | 18.8 | 140 | 2.632 | 5.3 | 1 | 19.7 | 3 | 1 |
21-Aug-16 | EPI_264 | Bin6 | Super.Low-Ambient | Day158 | 20160901 | 20161025 | 20161026 | 8.42 | 140 | 1.1788 | 11.9 | 1 | 13.1 | 3 | 1 |
21-Aug-16 | EPI_265 | Bin6 | Super.Low-Ambient | Day158 | 20160901 | 20161025 | 20161026 | 17.5 | 140 | 2.45 | 5.7 | 1 | 19.3 | 3 | 1 |
21-Aug-16 | EPI_271 | Bin7 | Ambient-Low | Day158 | 20160901 | 20161028 | 20161028 | 39.1 | 140 | 5.474 | 2.6 | 1 | 22.4 | 3 | 1 |
21-Aug-16 | EPI_272 | Bin7 | Ambient-Low | Day158 | 20160901 | 20161028 | 20161028 | 105 | 140 | 14.7 | 1 | 1 | 24 | 3 | 1 |
21-Aug-16 | EPI_275 | Bin8 | Low-Low | Day158 | 20160825 | 20161025 | 20161026 | 15 | 140 | 2.1 | 6.7 | 1 | 18.3 | 3 | 1 |
21-Aug-16 | EPI_276 | Bin8 | Low-Low | Day158 | 20160824 | 20161025 | 20161026 | 21 | 140 | 2.94 | 4.8 | 1 | 20.2 | 3 | 1 |
21-Aug-16 | EPI_282 | Bin9 | Super.Low-Low | Day158 | 20160824 | 20161004 | 20161006 | 10.3 | 140 | 1.442 | 9.7 | 1 | 15.3 | 3 | 1 |
21-Aug-16 | EPI_283 | Bin9 | Super.Low-Low | Day158 | 20160824 | 20161028 | 20161028 | 36.6 | 140 | 0.77 | 2.7 | 1 | 22.3 | 3 | 1 |
21-Aug-16 | EPI_289 | Bin10 | Super.Low-Low | Day158 | 20160824 | 20161025 | 20161026 | 13.4 | 140 | 1.876 | 7.5 | 1 | 17.5 | 3 | 1 |
21-Aug-16 | EPI_290 | Bin10 | Super.Low-Low | Day158 | 20160824 | 20161025 | 20161026 | 7.4 | 140 | 1.036 | 13.5 | 1 | 11.5 | 3 | 1 |
21-Aug-16 | EPI_298 | Bin11 | Ambient-Low | Day158 | 20160824 | 20161028 | 20161028 | 79.9 | 140 | 11.186 | 1.3 | 1 | 23.7 | 3 | 1 |
21-Aug-16 | EPI_299 | Bin11 | Ambient-Low | Day158 | 20160824 | 20161007 | 20161010 | 17.6 | 140 | 2.464 | 5.7 | 1 | 19.3 | 3 | 1 |
21-Aug-16 | EPI_302 | Bin12 | Low-Low | Day158 | 20160824 | 20161004 | 20161006 | 32.8 | 140 | 4.592 | 3 | 1 | 22 | 3 | 1 |
21-Aug-16 | EPI_303 | Bin12 | Low-Low | Day158 | 20160824 | 20161004 | 20161006 | 32.4 | 140 | 4.536 | 3.1 | 1 | 21.9 | 3 | 1 |
Step 1 conclusions
- no errors were seen on the PCR machine. Samples assumed to have been cut with MSPI
Step 2 Bisulfite conversion
- Removed from incubator at 09:45 on 20161207
- Proceeded with EZ DNA Methylation-Gold Kit (Catalog Nos. D5005 & D5006) EZ DNA Methylation-Gold Manual
Bisulfite conversion kit prep
-
Prepared the CT Conversion Reagent for larger DNA samples (30µl) by adding 800µl of water, 300µl of M-Dilution and 50µl of M-Dissolving
- Added 30µl of sample described in table to 120 µl of CT Conversion Reagent, mixed by flicking, and spun down
- Placed tubes in PCR machine at 10:45 and set as follows:
- 98°C for 10 min
- 64°C for 2.5 hours
- 4°C forever
-
followed protocol steps EZ DNA Methylation-Gold Manual
- Eluted in 12µl of elution buffer
Bisulfite Conversion ssDNA QC
- 1µl was used to assess fragment size on the bioanalyzer.
Expected DNA size for Gold kit (A)
Results of bisulfite converted samples
20161209
- Samples all look good except EPI-44. Will run again
- Samples 52, 53, 54, 55, 56 are as expected, samples 151, 152, 153, 154, 159, 160 are shifted to a larger proportion of smaller fragments
- Samples are shifted to a larger proportion of smaller fragments
20161211
- Samples 185, 188, 193, 200, 205, 206, 208, and 209 are shifted to a larger proportion of smaller fragments
- Samples 214, 229, 230, 235, 236, 242 are shifted to a larger proportion of smaller fragments
- Samples 243, 246, 247, 250, 251, 258, 264, 265, and 272 are shifted to a larger proportion of smaller fragments
- Sample 275 has abnormal peak around 3000
- Sample 44 was re-reun and still has strange very small fragment size
- Samples 275, 276, 282, 283, 298 are shifted to a larger proportion of smaller fragments
20161213
Step 3 Library Prep
Ilumina TruSeq DNA Methylation Library Preparation Guide
Illumina Adapter Sequences Document # 1000000002694 v01 17 February 2016 TruSeq DNA Methylation Index PCR Primers 5’ CAAGCAGAAGACGGCATACGAGAT[6 bases]GTGACTGGAGTTCAGACGTGTGCTCTTCCGATCT
- Index 1: ATCACG
- Index 2: CGATGT
- Index 3: TTAGGC
- Index 4: TGACCA
- Index 5: ACAGTG
- Index 6: GCCAAT
- Index 7: CAGATC
- Index 8: ACTTGA
- Index 9: GATCAG
- Index 10: TAGCTT
- Index 11: GGCTAC
- Index 12: CTTGTA
Illumina library prep was completed according to manufacturer’s instructions with modifications as described in red text on the protocol and listed below.
- samples eluted in 12µl post BS conversion
- 200µl of 80% ethanol used for rinsing beads
- Samples were stored at -20 for ~24h between Purify the Tagged DNA and Amplify the Library and Add an Index steps
- Library prep was started 20161213
- Library prep was finished 20161213
- Individual barcodes were used for each sample from the Illumina TruSeq DNA Methylation Index PCR Primers (10 reactions, 12 indexes Cat #: EGIDX81312)
Sample.ID | Index.Number | Index.Sequence |
---|---|---|
EPI_151 | 1 | ATCACG |
EPI_152 | 2 | CGATGT |
EPI_153 | 3 | TTAGGC |
EPI_154 | 4 | TGACCA |
EPI_159 | 5 | ACAGTG |
EPI_160 | 6 | GCCAAT |
EPI_161 | 7 | CAGATC |
EPI_162 | 8 | ACTTGA |
EPI_167 | 9 | GATCAG |
EPI_168 | 10 | TAGCTT |
EPI_169 | 11 | GGCTAC |
EPI_170 | 12 | CTTGTA |
EPI_175 | 1 | ATCACG |
EPI_176 | 2 | CGATGT |
EPI_181 | 3 | TTAGGC |
EPI_182 | 4 | TGACCA |
EPI_184 | 5 | ACAGTG |
EPI_185 | 6 | GCCAAT |
EPI_187 | 7 | CAGATC |
EPI_188 | 8 | ACTTGA |
EPI_193 | 9 | GATCAG |
EPI_194 | 10 | TAGCTT |
EPI_199 | 11 | GGCTAC |
EPI_200 | 12 | CTTGTA |
EPI_205 | 1 | ATCACG |
EPI_206 | 2 | CGATGT |
EPI_208 | 3 | TTAGGC |
EPI_209 | 4 | TGACCA |
EPI_214 | 5 | ACAGTG |
EPI_215 | 6 | GCCAAT |
EPI_220 | 7 | CAGATC |
EPI_221 | 8 | ACTTGA |
EPI_226 | 9 | GATCAG |
EPI_227 | 10 | TAGCTT |
EPI_229 | 11 | GGCTAC |
EPI_230 | 12 | CTTGTA |
EPI_41 | 1 | ATCACG |
EPI_42 | 2 | CGATGT |
EPI_43 | 4 | TGACCA |
Library Quantification
20161213 Libraries were quantified on the Qubit using the dsDNA High Sensitivity Kit
- Samples were loaded 1µl of library + 199µl of Qubit dye/buffer mix (1:200)
-
Standards were loaded 10µl of standard + 190µl of Qubit dye/buffer mix (1:200)
- Illumina indicates samples should be >3ng/µl
Sample.ID | ng/µl |
---|---|
EPI_151 | 0.242 |
EPI_152 | 0.486 |
EPI_153 | 0.580 |
EPI_154 | 0.320 |
EPI_159 | 0.356 |
EPI_160 | 0.210 |
EPI_161 | 0.226 |
EPI_162 | 0.930 |
EPI_167 | 0.808 |
EPI_168 | 0.880 |
EPI_169 | 0.500 |
EPI_170 | 0.866 |
EPI_175 | 0.552 |
EPI_176 | 0.676 |
EPI_181 | 1.18 |
EPI_182 | 0.902 |
EPI_184 | 0.956 |
EPI_185 | 0.972 |
EPI_187 | 0.976 |
EPI_188 | 1.05 |
EPI_193 | 1.74 |
EPI_194 | 0.518 |
EPI_199 | 0.464 |
EPI_200 | 0.664 |
EPI_205 | 0.312 |
EPI_206 | 0.270 |
EPI_208 | 0.408 |
EPI_209 | 0.114 |
EPI_214 | 0.350 |
EPI_215 | 1.192 |
EPI_220 | 0.888 |
EPI_221 | 0.492 |
EPI_226 | 1.71 |
EPI_227 | 0.796 |
EPI_229 | 0.808 |
EPI_230 | 0.642 |
EPI_41 | 0.314 |
EPI_42 | 0.740 |
EPI_43 | 0.252 |
- Library concentration is significantly lower than expected in the majority of the samples
Library Quality
20161214
- 1.0µl of each sample was run on the Agilent DNA High Sensitivity Kit
Illumina DNA Methylation kit expected library size on high sensitivity chip
Conclusions
- Library quality is shifted to a smaller size in libraries that are detectable.
- Given the low concentraiton and poor traces, no further chips were run and the library preps need to be redone.