Evaluation of droplet digital PCR for characterizing plasmid reference material used for quantifying ammonia oxidizers and denitrifiers
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DNA reference materials of certified value have a critical function in many analytical processes of DNA measurement. Quantification of amoA genes in ammonia oxidizing bacteria (AOB) and archaea (AOA), and of nirS and nosZ genes in the denitrifiers is very important for determining their distribution and abundance in the natural environment. A plasmid reference material containing nirS, nosZ, amoA-AOB, and amoA-AOA is developed to provide a DNA standard with copy number concentration for ensuring comparability and reliability of quantification of these genes. Droplet digital PCR (ddPCR) was evaluated for characterization of the plasmid reference material. The result revealed that restriction endonuclease digestion of plasmids can improve amplification efficiency and minimize the measurement bias of ddPCR. Compared with the conformation of the plasmid, the size of the DNA fragment containing the target sequence and the location of the restriction site relative to the target sequence are not significant factors affecting plasmid quantification by ddPCR. Liquid chromatography–isotope dilution mass spectrometry (LC–IDMS) was used to provide independent data for quantifying the plasmid reference material. The copy number concentration of the digested plasmid determined by ddPCR agreed well with that determined by LC–IDMS, improving both the accuracy and reliability of the plasmid reference material. The reference value, with its expanded uncertainty (k = 2), of the plasmid reference material was determined to be (5.19 ± 0.41) × 109 copies μL−1 by averaging the results of two independent measurements. Consideration of the factors revealed in this study can improve the reliability and accuracy of ddPCR; thus, this method has the potential to accurately quantify DNA reference materials.
KeywordsPlasmid DNA reference material Droplet digital PCR Isotope dilution mass spectrometry Ammonia oxidizer Denitrifier
DNA reference materials of certified value have a critical function in many analytical processes involving nucleic acid analysis. Many important challenges have contributed to the need for accurate and reliable DNA reference materials, for instance legislative requirements for analysis of genetically modified organisms (GMOs). qPCR techniques have been used for quantification of GMOs in several studies [1, 2]. However, qPCR is unable to quantify the GM content, usually the ratio of the transgenic gene copy number to the endogenous gene copy number, without a DNA reference standard containing the target gene. The JRC’s Institute of Reference Material Measurement (IRMM) and the American Oil Chemists’ Society (AOCS) have developed more than 40 different kinds of GM reference material. Other examples of applications requiring DNA reference material include clinical applications, scene-of crime genotyping, and microbial contamination of food. All of these tests could benefit greatly from more accurate and reliable DNA reference material.
In environmental microbiology, many studies focus on the distribution and abundance of specific functional microbial groups involved in nitrification and denitrification [3, 4, 5]. Nitrification and denitrification are essential, microbe-driven processes in the global nitrogen cycle. Ammonia oxidization, the first and rate-limiting step of nitrification, is performed by ammonia oxidizing bacteria (AOB) and ammonia oxidizing archaea (AOA) . For both the AOA and AOB, the amoA gene encoding the a-subunit of ammonia monooxygenase has been widely used as a functional marker for investigating their distribution and abundance in natural environments [6, 7]. Denitrification is the enzymatic, stepwise reduction of nitrate and nitrite to the gases nitric oxide (NO), nitrous oxide (N2O), and nitrogen gas (N2). Nitrous oxide (N2O) and nitric oxide (NO) are intermediate products in the denitrification pathway. N2O, with a global warming potential approximately 296 times higher than that of carbon dioxide, is an important greenhouse gas . The nosZ gene, encoding the catalytic subunit of N2O reductase, and the nirS/K gene, encoding nitrite reductase, are widely used as functional markers for studying the abundance of bacteria able to metabolize N2O and NO, to better understand the main causes of N2O and NO emissions [9, 10, 11].
Real-time quantitative PCR (qPCR) is the most popular approach used to target the above functional genes to quantify the abundance of the functional groups [9, 10, 12]. However, an external standard or a calibrant is needed to quantify the environmental sample when using qPCR. In the absence of a certified DNA reference material, one usually develops one’s own plasmid standard [12, 13] or extracts genomic DNA from pure culture , and quantifies the standard DNA concentration by measuring absorbance at 260 nm by use of a UV spectrophotometer. UV spectrophotometry is an established method for measuring nucleic acids; however, common contaminants of DNA extracts, for example proteins, RNA, and salts, can increase absorbance at 260 nm, resulting in overestimation of DNA concentration. Moreover, UV spectrophotometers cannot distinguish between single-stranded DNA and double-stranded DNA in solution, nor between target DNA and other, potentially contaminating sources of DNA or RNA. Thus, this method has limitations that may contribute to inaccuracy of DNA concentration estimates, and use of such a DNA standard to quantify the abundance of functional microbial groups in the environmental sample will result in inaccurate information. This will lead to incomparability of results from different research groups.
There is a need for an accurate and traceable method that can be used for characterization of DNA certified reference material, for effective comparison of quantitative measurements, quality control in laboratory routine analysis, and method validation. Digital PCR (dPCR) is a relatively new technology, requiring no external calibrators, for measuring the absolute and relative copy numbers of target DNA [14, 15]. Digital PCR (dPCR) transforms the exponential, analogue signal of classic PCR into a linear, digital signal, retaining the single-molecule sensitivity of PCR. Single molecules are isolated by dilution and individually amplified by PCR; each product is then analyzed separately. This is achieved by partitioning a sample before PCR amplification. The distribution of target DNA molecules among the partitions follows Poisson statistics, and at the so-called limiting dilution most reactions contain either one or zero target DNA molecules [16, 17, 18]. An absolute target sequence quantity can be estimated [16, 17]. Droplet digital PCR (ddPCR) is a droplet-based form of dPCR that has recently been commercialized. Pinheiro  reported it has high accuracy and precision for quantifying genomic DNA concentration. However, little information is available regarding use of ddPCR for quantifying plasmid DNA.
Another accurate and traceable nucleic acid quantification approach is liquid chromatography–isotope dilution mass spectrometry (LC–IDMS) [20, 21]. This method overcomes the lack of DNA standards in suitable quantities by using deoxynucleotide monophosphates (dNMPs) and isotopically-labeled dNMPs (LdNMPs) as the calibrants and internal standards, respectively. Additionally, this approach provides full traceability to the International System of units (SI). IDMS has been well established elsewhere as providing highly reliable quantitative trace analysis [22, 23]; thus, it has become the method of choice for the quantification of analytes in primary standards for many national measurement institutes.
In this study, we constructed a plasmid containing the amoA gene of AOA (A-amoA) and AOB (B-amoA), and the nosZ and nirS genes of denitrifiers. Droplet digital PCR (ddPCR) was evaluated for characterization of the plasmid reference material. The dynamic range and factors involved in ddPCR measurement accuracy and bias were investigated. Additionally, LC–IDMS was used to provide independent data for comparison of the ddPCR result. The results reveal the DNA copy number concentration measured by ddPCR is comparable with LC–IDMS for quantifying the mass concentration.
Material and methods
Soil characteristics and sampling
Soil was collected from the field in cotton–spring maize (Triticum aestivum L.) rotation at the Chinese academy of agriculture science, PingGu, Beijing, China in May 2012, before the cotton planting. The soils were coarse loam. The soil pH was 6.1, as determined by a 1:1 soil:water suspension. The total organic C concentration was 1.02 g kg−1, and the total N concentration was 0.99 g kg−1, as determined by combustion (Leco CNS-1000). Soil was frozen at −20 °C to limit biological activity. At the start of the experiment, soil was thawed at room temperature, homogenized, and passed through a 2-mm sieve.
DNA extraction and purification
Total soil genomic DNA was extracted and purified by using a MOBIO DNA extraction kit (MOBIO Laboratories Inc., Carlsbad, CA) according to the manufacturer’s instructions. 0.25 g soil mixed with solution C1 was vortexed in the Power Bead tube at maximum speed for 10 min, then centrifuged at 10,000 g for 30 s at room temperature. The supernatant was transferred to a clean 2 mL collection tube and mixed with 250 μL solution C2. The mixture was then centrifuged at 10,000 g for 1 min, and 600 μL of the supernatant was transferred to a new 2 mL collection tube. 200 μL solution C3 was added to the tube, which was then incubated at 4 °C for 5 min, and then centrifuged at room temperature for 1 min at 10,000 g. 750 μL of the supernatant was pipetted into a clean 2 mL collection tube and mixed with 1200 μL solution C4. Approximately 675 μL was loaded into a spin filter (provided in the kit) and centrifuged at 10,000 g for 1 min. The flow-through was discarded, an additional 675 μL supernatant was added to the spin filter, and centrifugation was repeated. 500 μL solution C5 was added to the filter to wash the DNA, and the mixture was then centrifuged for 30 s at 10,000 g. The flow-through was discarded, and 100 μL DNA-free PCR-grade water was loaded into the center of the filter membrane to dissolve the DNA. The spin filter was placed in a clean 2 mL collection tube and centrifuged at room temperature for 30 s at 10,000 g. Finally, the dissolved DNA was stored at −20 °C, ready for any downstream application.
PCR amplification of target genes from soil DNA and plasmid construction
Primer sequence for amplification of A-amoA, B-amoA, nosZ and nirS gene from soil and construction of the plasmid standard
Sequence (5ʹ to 3ʹ)
Size of PCR amplicon (bp)
The 50 μL reaction mixture was comprised of 2 × 25 μL Taqman Environmental Master Mix 2.0 (Life Technologies), 1 μL 20 μmol L−1 forward and reverse primers, and 5 ng template DNA. The first and third round of PCR thermal cycling consisted of a 5 min activation period at 95 °C, followed by six cycles of a touch-down PCR thermal profile of 45 s at 95 °C for denaturation, 60 s at 53–58 °C for annealing, and 60 s at 72 °C extension; then 30 cycles of 45 s at 95 °C for denaturation, 60 s at 53 °C for annealing, and 2 min at 72 °C extension; and a final step of 10 min at 72 °C. The second-round PCR program consisted of a 5 min activation period at 95 °C, followed by 30 cycles of a PCR thermal profile of 45 s at 95 °C for denaturation and 60 s at 55 °C for annealing, and 2 min at 72 °C extension, and a final step of 10 min at 72 °C. All PCR amplifications were performed on a PTC-200 thermocycler (BioRad, CA).
After the third round of PCR, the integrated PCR amplicon was purified using the Gel Extraction Purification Kit (Tangen Biotech, Beijing, China), and ligated into pEASY-T3 vector and transformed to E. coli. Sequencing analysis of the cloned DNA was performed using the ABI 3730 XL Genetic Analyzer (Applied-Biosystems) by BGI Co., Ltd. (Beijing, China). Endogenous restriction enzymes BamHI and XbaI were used to digest the plasmid (pNIM-003), to check the correction of the fragment size.
Droplet digital PCR (ddPCR)
Primer and probe sequence and concentration for quantitative PCR and droplet digital PCR
Primer or probe
Sequence (5ʹ to 3ʹ)
Concentration (nmol L−1)
Product size (bp)
Enzymatic restriction of plasmid DNA
Three restriction enzymes were chosen to investigate the effect of the conformation and the size of the fragment on quantification using ddPCR. The restriction enzymatic sites are labeled in Fig. 2. BamH1 was used to linearize the plasmid, and EcoR1 to fragment the DNA target into small pieces. The combination of EcoR1 and Xba1 was used to cut the target fragment at equal distances from the forward and reverse primer. Enzymatic digestion of the mixture with either BamH1, ECOR1, or ECOR1 with Xba1 (Takara, China) was performed as follows: 10 × 2 μL buffer, 1 μL restriction enzyme, 10 μL plasmid DNA, and 7 μL ddH2O. No template control (NTC) was prepared by adding 10 μL TE0.1 (10 mmol L−1 Tris–HCl, 0.1 mmol L−1 EDTA) instead of the DNA solution, and no enzyme control (NEC) was made by pipetting 1 μL TE0.1 in place of the enzyme when preparing the enzymatic master mixture. The enzymatic time was 1 h. After the enzymatic reaction, the DNA was diluted to the appropriate concentration for the ddPCR analysis procedure described above.
For the dynamic range of ddPCR, the plasmid digested with EcoR1 was diluted to 2,177,456, 215,982, 22,315, 2078, 235, 22.7, or 2.3 copies 20 μL−1 ddPCR (from dilution 1 to dilution 7, labeled S1–S7). Dilutions were ascertained using UV measurement. Seven dilutions were made of the enzyme-digested plasmid, and each dilution had four replicates; thus, a total of 30 reactions plus two NTCs were prepared to evaluate the dynamic range. Meanwhile, undigested pNIM-003 was diluted to dilutions 1–6 (labeled as S1–S6) for use as the template in the NEC.
Preparation of standards and isotopically-labeled internal standards for LC–IDMS
The dNMP standards (approximately 10 mg) were weighed on a six-figure calibrated analytical balance and dissolved in 10 g water. Detailed information about the purity and certificate of the dNMP standard was described in our previously published paper . A mixed stock standard solution containing the desired concentrations of each dNMP was prepared gravimetrically. The concentration of dNMP in the stock standard was corrected for purity. A mixed stock standard containing 4.5 μg g−1 dAMP, 6.3 μg g−1 dCMP, 8.0 μg g−1 dGMP, and 5.4 μg g−1 dTMP was prepared. These concentrations correspond to the amount of dNMP in the plasmid DNA solution (assuming total digestion of the plasmid DNA to its constituent dNMPs). The preparation of the LdNMPs was nearly the same as that for the natural dNMPs. A final mixed stock solution of LdNMPs containing 7.0 μg g−1 dAMP, 14.0 μg g−1 dCMP, 14.3 μg g−1 dGMP, and 9.9 μg g−1 dTMP was prepared. The mixed solution was used to prepare the calibration and sample blends for the IDMS experiments. The isotopic purity of the LdNMPs was stated to be higher than 98 % by the certificate provided by the manufacturer.
Sample (diluted plasmid DNA) and calibration blend solutions were prepared by gravimetrically adding equal amounts of the LdNMP standard to the plasmid DNA sample and the mixed dNMP standard. Briefly, 50 μL LdNMP solution and 50 μL dNMP standard were weighed and mixed as the calibration blend; 50 μL plasmid DNA sample and 50 μL LdNMP solution were weighed and mixed to form the sample blend.
Ultrasonic treatment and digestion of the target sample
For the ultrasonic treatment, 100 μL sample blend or calibration blend was sheared by a Covaris S2 system (Covaris, Applied Biosystems, Carlsbad, CA, USA), in a 1.5-mL tube on the 1.5 tray (Covaris, Applied Biosystems). The conditions of the ultrasonic treatment for plasmid were: intensity, 5; treatment time, 25 min . The duty cycle and the number of cycles per burst were 10 % and 200, respectively.
The digestion master mixture consisted of 5 μL phosphodiesterase I (0.02 U μL−1) and 5 μL digestion buffer containing 300 mmol L−1 Mg(Ac)2, 10 mmol L−1 ammonium acetate, and 100 mmol L−1 Tris–HCl. The sample or calibration blend (50 μL) was added to this master mixture, and the final mixture was incubated at 37 °C for 1 h. This step was performed in triplicate for both the sample and the calibration blends. Blanks were prepared by adding ultraclean water in place of the sample or calibration blends when preparing the master mixture.
Liquid chromatography–mass spectrometry (LC–MS)
Parameters used for the mass spectrometry analysis
Electrospray, positive ion mode
Ion spray voltage (V)
Curtain gas (L h−1)
Ion source gas 1 (L h−1)
Ion source gas 2 (L h−1)
Declustering potential (V)
Entrance potential (V)
Collision energy (V)
Collision cell exit potential (V)
Measurement equation for the plasmid DNA mass fraction
Where wX,dNMP is the mass fraction of dNMP in the hydrolysate (ng mg−1), wX,DNA is the mass fraction of double-stranded DNA (ng mg−1), MR,DNA is the molecular weight of the plasmid pNIM-003 (3,313,860 g mol−1), NdNMP is the number of molecules in the specific nucleotide in the pNIM-003 plasmid, and MR,dNMP is the average molecular weight (hydrated) of the specific dNMP (g mol−1).
Homogeneity and stability study for the plasmid reference material
The homogeneity study of the reference value was performed under repeatability conditions, using 15 bottles randomly taken from the entire batch and tested in random order. Three subsamples were taken from each bottle and each was analyzed in triplicate. The measurements were performed by ddPCR, using the AOB PCR assay, and the minimum sample intake for ddPCR is 4 μL. ANOVA was used to assess the between-bottle standard deviation (ubb). Further information regarding the homogeneity test is in the Electronic Supplemental Material (Section 1, Homogeneity study).
The long-term stability of plasmid pNIM-003 during storage was monitored at the National Institute of Metrology, China, for one year, using ddPCR with AOB assay. The plasmid concentration was measured after 0, 1, 2, 4, 7, and 12 months storage at −70 °C, and the data was used to assess the stability over long storage times and to estimate the uncertainty contribution of the stability according to the ISO guide 35 . For detailed information please see the Electronic Supplemental Material (Section 2, Stability study).
Results and discussion
Plasmid construction and verification
PCR confirmation is shown in Fig. 3. Four single-gene fragments (B-amoA, A-amoA, nirS and nosZ, in lanes 8, 9, 10, and 11, respectively), two connected-gene fragments (B-amoA–A-amoA in lane 6, nirS–nosZ in lane 7), and the four-connected-gene fragment (B-amoA–A-amoA–nirS–nosZ in lane 5) were successfully amplified using the plasmid as the template. After confirmation by restriction digestion, PCR, and sequencing, the purified plasmid was ready to be characterized, with a reference value of copy number μL−1.
Homogeneity and stability of the plasmid reference material
The result of the homogeneity testing is summarized in Table S1 (Electronic Supplementary Material). First, normal probability plots and histograms were used to establish that the data followed a normal distribution. The individual data and the bottle means from the homogeneity study measured for pNIM-003 were normally distributed. No outliers were detected for these data using the Grubbs tests (95 % confidence level). The ANOVA test indicated that the plasmid reference material is homogeneous and the relative uncertainty of the homogeneity (ubb,rel) is 0.15 %.
The result indicating a year’s long-term stability of the pNIM-003 is shown in Fig. S1 and Table S2. According to the principle of CRM for stability assessment, described in ISO guide 35, the plasmid RM is stable under the storage conditions. The relative standard uncertainty of the long-term stability (us,rel) was approximately 3 % for a shelf life of one year, and was used as the contribution to the uncertainty budget from the instability of CRMs during storage.
Enzymatic restriction effect on plasmid quantification by ddPCR
Measured copy number concentration of digested and undigested plasmid obtained using ddPCR with three different restriction endonuclease enzyme digestions
Digested plasmid copy number concentration (copies μL−1)a
Undigested plasmid copy number concentration (copies μL−1)a
(4.69 ± 0.17) × 109*
(2.05 ± 0.08) × 109†
(4.77 ± 0.16) × 109*
(2.12 ± 0.06) × 109†
EcoR1 + XbaI
(4.70 ± 0.16) × 109*
(2.31 ± 0.05) × 109†
In addition to plasmid conformation, we also considered other factors that may affect plasmid quantification by ddPCR, including the location of the restriction site relative to the target sequence and the size of DNA fragment containing the target sequence. However, there was no significant difference in the one-dimensional scatter plots for different restriction enzyme digestion (Fig. 4a). Furthermore, the T-test showed there was no significant difference in the plasmid copy number concentrations determined by ddPCR for the three different restriction enzyme treatments (Table 4). Therefore, to obtain accurate plasmid copy number concentrations using ddPCR, linearizing the plasmid using restriction enzymes is more important than the size of the DNA fragment and the location of the restriction site. Thus, EcoR1 was used to linearize the plasmid in the following study.
Dynamic range of droplet digital PCR for quantifying plasmids
The ddPCR response was linear over the dynamic range of 11–1081863 copies. The ddPCR response was linear over the dynamic range of 2.3–215 982 copies 20 μL−1 of ddPCR, covering five orders of magnitude. This is consistent with a previous study , in which the linearity range of ddPCR for quantifying lambda genomic DNA covered more than four orders of magnitude. The linearity regression of the ddPCR for quantifying pNIM-003 plasmid DNA is shown in Fig. 5c (R2 = 1). In dilution S1, there were no negative droplets (Fig. 5c), indicating an over-saturation of the droplets. Thus, it is impossible to accurately estimate the copy number of the digested plasmid in dilution S1. The number of target DNA molecules of dilution S7 in ddPCR replicates is the most variable, because the copy number concentration of dilution S7 is the lowest (2.3 copies 20 μL−1). It is interesting to note that the data points for dilution S1 and dilution S7 are not a good fit to the linear curve in Fig. 5b. Thus, to achieve higher accuracy and better precision in ddPCR measurement, the DNA concentration should be within the optimum range.
Three subsamples of the plasmid diluted to the optimum concentration range were quantified using ddPCR. The measured copy number concentrations of the pNIM-003 of three subsamples are shown in Fig. S3. The concentrations of plasmid DNA in subsamples 1, 2, and 3 were determined to be 5.02 × 109 copies μL−1, 5.10 × 109 copies μL−1, and 5.03 × 109 copies μL−1, respectively, and the RSDs were 3.33 %, 3.79 %, and 3.50 %, respectively. The average copy number concentration of the three subsamples was 5.05 × 109 copies μL−1, with a relative standard deviation of 3.63 %. Those results were calculated based on the droplet volume of 0.846 nL measured in this study (Fig. S4, Electronic Supplementary Material); however, this will have been underestimated because of the inaccuracy of the droplet volume set in the software by the manufacturer (0.91 nL, personal communication from BioRad). It has been reported that the inaccuracy of the droplet volume could cause a bias in the ddPCR measurement. The droplet volume determined in this study is slightly different from that in an earlier report . This is reasonable, because the 0.865 nL droplet size in the previous study was measured on a Beta-prototype instrument. The relative expanded uncertainty of the measurement result was 3.5 % (k = 2), evaluated by combining the uncertainty of the precision factor (uM), and variability of the droplet volume, the calibration of the microscope (uVp), and the dilution factor (uD).
Quantification by isotope dilution mass spectrometry (IDMS)
The determined concentrations of plasmid DNA in three subsamples, calculated by Eq. 4, are shown in Fig. S3. The reported results were obtained from five repeat injections of each digested sample and calibration blend. The concentrations of plasmid DNA in subsamples 1, 2, and 3 were calculated as 5.35 × 109 copies μL−1, 5.34 × 109 copies μL−1, and 5.31 × 109 copies μL−1, respectively, based on the measured dAMP concentration, whereas the RSDs were 3.11 %, 2.56 %, and 3.26 %, respectively. The uncertainty for each measurement was calculated by the method of uncertainty propagation described in JCGM . The average concentration of the plasmid was 5.34 × 109 copies μL−1, with an expanded uncertainty of 2.2 × 108 copies μL−1 (k = 2).
Determining the reference value of the plasmid reference material and its uncertainty
The average plasmid DNA concentration determined by IDMS and ddPCR is shown in Fig. 7. The result obtained by correction of the droplet size was 94.7 % of the IDMS value. The result from ddPCR measurement is approximately 5 % lower than the result from IDMS measurement, but it still can be overlapped within the expanded uncertainty, suggesting the bias for each measurement system has a minimal effect on the measurement of the plasmid reference material characterization. To assign the reference value for the plasmid pNIM-003, the precision of the two sets of data was checked, revealing equal precision of the two data sets from the two methods. Thus, the average value of the two measurement results was used as the reference value for the plasmid copy number concentration, which was (5.19 ± 0.22) × 109 copies μL−1. Considering the contributions of homogeneity and stability to the uncertainty budget, the certified reference value with its expanded uncertainty (k = 2) is (5.19 × 0.41) × 109 copies μL−1 (Table S3). The reference value of the plasmid reference material is more reliable and accurate when obtained by characterizing with two totally independent approaches. Therefore, the plasmid reference material with an accurate DNA copy number concentration is suitable for method validation and for quantifying ammonia oxidizer and denitrifier.
DNA reference material with a certified value has a critical function in many analytical processes involving nucleic acids. In environmental microbiology, many studies focus on determining the distribution and abundance of ammonia oxidizers and denitrifiers in the natural environment by quantifying the functional gene, for example amoA, nirS, or nosZ. Comparability and reliability of analysis results can be achieved by using an accurate DNA reference material. Droplet digital PCR has applications in molecular genetic analysis, including DNA copy number measurement. One major advantage of ddPCR is that it is independent of DNA standards. However, for correct evaluation of data sets generated from ddPCR, it is crucial to consider sources of measurement bias. In this study, we revealed two major measurement biases when using ddPCR to quantify plasmid DNA. We demonstrated that restriction digestion of plasmid DNA into linearized plasmid DNA greatly increases amplification efficiency, and minimizes bias when measuring the true copy number. Compared with conformation of the plasmid, the size of the DNA fragment containing the target sequence and the location of the restriction site to the target sequence are not significant factors affecting plasmid quantification by ddPCR. Additionally, the droplet volume also contributes to the accuracy of the ddPCR measurement. In conclusion: consideration of the factors revealed in this study can improve the reliability and accuracy of ddPCR measurement. This gives ddPCR the potential to accurately quantify DNA reference material, which in turn underpins the quality and consistency of routine measurement. LC–IDMS, an independent DNA concentration measurement approach developed in our earlier study, was used to co-characterize the plasmid reference material with ddPCR. This will improve the accuracy and reliability of the plasmid reference material.
The project described was supported by Grant Number 31100084 from the National Science foundation of China and AKY1323-13 sponsored by National Institute of Metrology, China.
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