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Hypothesis testing is the act of testing a hypothesis or a supposition in relation to a statistical parameter. Analysts implement hypothesis testing in order to test if a hypothesis is plausible or not.
In data science and statistics , hypothesis testing is an important step as it involves the verification of an assumption that could help develop a statistical parameter. For instance, a researcher establishes a hypothesis assuming that the average of all odd numbers is an even number.
In order to find the plausibility of this hypothesis, the researcher will have to test the hypothesis using hypothesis testing methods. Unlike a hypothesis that is ‘supposed’ to stand true on the basis of little or no evidence, hypothesis testing is required to have plausible evidence in order to establish that a statistical hypothesis is true.
Perhaps this is where statistics play an important role. A number of components are involved in this process. But before understanding the process involved in hypothesis testing in research methodology, we shall first understand the types of hypotheses that are involved in the process. Let us get started!
In data sampling, different types of hypothesis are involved in finding whether the tested samples test positive for a hypothesis or not. In this segment, we shall discover the different types of hypotheses and understand the role they play in hypothesis testing.
Alternative Hypothesis (H1) or the research hypothesis states that there is a relationship between two variables (where one variable affects the other). The alternative hypothesis is the main driving force for hypothesis testing.
It implies that the two variables are related to each other and the relationship that exists between them is not due to chance or coincidence.
When the process of hypothesis testing is carried out, the alternative hypothesis is the main subject of the testing process. The analyst intends to test the alternative hypothesis and verifies its plausibility.
The Null Hypothesis (H0) aims to nullify the alternative hypothesis by implying that there exists no relation between two variables in statistics. It states that the effect of one variable on the other is solely due to chance and no empirical cause lies behind it.
The null hypothesis is established alongside the alternative hypothesis and is recognized as important as the latter. In hypothesis testing, the null hypothesis has a major role to play as it influences the testing against the alternative hypothesis.
(Must read: What is ANOVA test? )
The Non-directional hypothesis states that the relation between two variables has no direction.
Simply put, it asserts that there exists a relation between two variables, but does not recognize the direction of effect, whether variable A affects variable B or vice versa.
The Directional hypothesis, on the other hand, asserts the direction of effect of the relationship that exists between two variables.
Herein, the hypothesis clearly states that variable A affects variable B, or vice versa.
A statistical hypothesis is a hypothesis that can be verified to be plausible on the basis of statistics.
By using data sampling and statistical knowledge, one can determine the plausibility of a statistical hypothesis and find out if it stands true or not.
(Related blog: z-test vs t-test )
Now that we have understood the types of hypotheses and the role they play in hypothesis testing, let us now move on to understand the process in a better manner.
In hypothesis testing, a researcher is first required to establish two hypotheses - alternative hypothesis and null hypothesis in order to begin with the procedure.
To establish these two hypotheses, one is required to study data samples, find a plausible pattern among the samples, and pen down a statistical hypothesis that they wish to test.
A random population of samples can be drawn, to begin with hypothesis testing. Among the two hypotheses, alternative and null, only one can be verified to be true. Perhaps the presence of both hypotheses is required to make the process successful.
At the end of the hypothesis testing procedure, either of the hypotheses will be rejected and the other one will be supported. Even though one of the two hypotheses turns out to be true, no hypothesis can ever be verified 100%.
(Read also: Types of data sampling techniques )
Therefore, a hypothesis can only be supported based on the statistical samples and verified data. Here is a step-by-step guide for hypothesis testing.
First things first, one is required to establish two hypotheses - alternative and null, that will set the foundation for hypothesis testing.
These hypotheses initiate the testing process that involves the researcher working on data samples in order to either support the alternative hypothesis or the null hypothesis.
Once the hypotheses have been formulated, it is now time to generate a testing plan. A testing plan or an analysis plan involves the accumulation of data samples, determining which statistic is to be considered and laying out the sample size.
All these factors are very important while one is working on hypothesis testing.
As soon as a testing plan is ready, it is time to move on to the analysis part. Analysis of data samples involves configuring statistical values of samples, drawing them together, and deriving a pattern out of these samples.
While analyzing the data samples, a researcher needs to determine a set of things -
Significance Level - The level of significance in hypothesis testing indicates if a statistical result could have significance if the null hypothesis stands to be true.
Testing Method - The testing method involves a type of sampling-distribution and a test statistic that leads to hypothesis testing. There are a number of testing methods that can assist in the analysis of data samples.
Test statistic - Test statistic is a numerical summary of a data set that can be used to perform hypothesis testing.
P-value - The P-value interpretation is the probability of finding a sample statistic to be as extreme as the test statistic, indicating the plausibility of the null hypothesis.
The analysis of data samples leads to the inference of results that establishes whether the alternative hypothesis stands true or not. When the P-value is less than the significance level, the null hypothesis is rejected and the alternative hypothesis turns out to be plausible.
As we have already looked into different aspects of hypothesis testing, we shall now look into the different methods of hypothesis testing. All in all, there are 2 most common types of hypothesis testing methods. They are as follows -
The frequentist hypothesis or the traditional approach to hypothesis testing is a hypothesis testing method that aims on making assumptions by considering current data.
The supposed truths and assumptions are based on the current data and a set of 2 hypotheses are formulated. A very popular subtype of the frequentist approach is the Null Hypothesis Significance Testing (NHST).
The NHST approach (involving the null and alternative hypothesis) has been one of the most sought-after methods of hypothesis testing in the field of statistics ever since its inception in the mid-1950s.
A much unconventional and modern method of hypothesis testing, the Bayesian Hypothesis Testing claims to test a particular hypothesis in accordance with the past data samples, known as prior probability, and current data that lead to the plausibility of a hypothesis.
The result obtained indicates the posterior probability of the hypothesis. In this method, the researcher relies on ‘prior probability and posterior probability’ to conduct hypothesis testing on hand.
On the basis of this prior probability, the Bayesian approach tests a hypothesis to be true or false. The Bayes factor, a major component of this method, indicates the likelihood ratio among the null hypothesis and the alternative hypothesis.
The Bayes factor is the indicator of the plausibility of either of the two hypotheses that are established for hypothesis testing.
(Also read - Introduction to Bayesian Statistics )
To conclude, hypothesis testing, a way to verify the plausibility of a supposed assumption can be done through different methods - the Bayesian approach or the Frequentist approach.
Although the Bayesian approach relies on the prior probability of data samples, the frequentist approach assumes without a probability. A number of elements involved in hypothesis testing are - significance level, p-level, test statistic, and method of hypothesis testing.
(Also read: Introduction to probability distributions )
A significant way to determine whether a hypothesis stands true or not is to verify the data samples and identify the plausible hypothesis among the null hypothesis and alternative hypothesis.
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Published on May 6, 2022 by Shaun Turney . Revised on June 22, 2023.
The null and alternative hypotheses are two competing claims that researchers weigh evidence for and against using a statistical test :
Answering your research question with hypotheses, what is a null hypothesis, what is an alternative hypothesis, similarities and differences between null and alternative hypotheses, how to write null and alternative hypotheses, other interesting articles, frequently asked questions.
The null and alternative hypotheses offer competing answers to your research question . When the research question asks “Does the independent variable affect the dependent variable?”:
The null and alternative are always claims about the population. That’s because the goal of hypothesis testing is to make inferences about a population based on a sample . Often, we infer whether there’s an effect in the population by looking at differences between groups or relationships between variables in the sample. It’s critical for your research to write strong hypotheses .
You can use a statistical test to decide whether the evidence favors the null or alternative hypothesis. Each type of statistical test comes with a specific way of phrasing the null and alternative hypothesis. However, the hypotheses can also be phrased in a general way that applies to any test.
The null hypothesis is the claim that there’s no effect in the population.
If the sample provides enough evidence against the claim that there’s no effect in the population ( p ≤ α), then we can reject the null hypothesis . Otherwise, we fail to reject the null hypothesis.
Although “fail to reject” may sound awkward, it’s the only wording that statisticians accept . Be careful not to say you “prove” or “accept” the null hypothesis.
Null hypotheses often include phrases such as “no effect,” “no difference,” or “no relationship.” When written in mathematical terms, they always include an equality (usually =, but sometimes ≥ or ≤).
You can never know with complete certainty whether there is an effect in the population. Some percentage of the time, your inference about the population will be incorrect. When you incorrectly reject the null hypothesis, it’s called a type I error . When you incorrectly fail to reject it, it’s a type II error.
The table below gives examples of research questions and null hypotheses. There’s always more than one way to answer a research question, but these null hypotheses can help you get started.
( ) | ||
Does tooth flossing affect the number of cavities? | Tooth flossing has on the number of cavities. | test: The mean number of cavities per person does not differ between the flossing group (µ ) and the non-flossing group (µ ) in the population; µ = µ . |
Does the amount of text highlighted in the textbook affect exam scores? | The amount of text highlighted in the textbook has on exam scores. | : There is no relationship between the amount of text highlighted and exam scores in the population; β = 0. |
Does daily meditation decrease the incidence of depression? | Daily meditation the incidence of depression.* | test: The proportion of people with depression in the daily-meditation group ( ) is greater than or equal to the no-meditation group ( ) in the population; ≥ . |
*Note that some researchers prefer to always write the null hypothesis in terms of “no effect” and “=”. It would be fine to say that daily meditation has no effect on the incidence of depression and p 1 = p 2 .
The alternative hypothesis ( H a ) is the other answer to your research question . It claims that there’s an effect in the population.
Often, your alternative hypothesis is the same as your research hypothesis. In other words, it’s the claim that you expect or hope will be true.
The alternative hypothesis is the complement to the null hypothesis. Null and alternative hypotheses are exhaustive, meaning that together they cover every possible outcome. They are also mutually exclusive, meaning that only one can be true at a time.
Alternative hypotheses often include phrases such as “an effect,” “a difference,” or “a relationship.” When alternative hypotheses are written in mathematical terms, they always include an inequality (usually ≠, but sometimes < or >). As with null hypotheses, there are many acceptable ways to phrase an alternative hypothesis.
The table below gives examples of research questions and alternative hypotheses to help you get started with formulating your own.
Does tooth flossing affect the number of cavities? | Tooth flossing has an on the number of cavities. | test: The mean number of cavities per person differs between the flossing group (µ ) and the non-flossing group (µ ) in the population; µ ≠ µ . |
Does the amount of text highlighted in a textbook affect exam scores? | The amount of text highlighted in the textbook has an on exam scores. | : There is a relationship between the amount of text highlighted and exam scores in the population; β ≠ 0. |
Does daily meditation decrease the incidence of depression? | Daily meditation the incidence of depression. | test: The proportion of people with depression in the daily-meditation group ( ) is less than the no-meditation group ( ) in the population; < . |
Null and alternative hypotheses are similar in some ways:
However, there are important differences between the two types of hypotheses, summarized in the following table.
A claim that there is in the population. | A claim that there is in the population. | |
| ||
Equality symbol (=, ≥, or ≤) | Inequality symbol (≠, <, or >) | |
Rejected | Supported | |
Failed to reject | Not supported |
To help you write your hypotheses, you can use the template sentences below. If you know which statistical test you’re going to use, you can use the test-specific template sentences. Otherwise, you can use the general template sentences.
The only thing you need to know to use these general template sentences are your dependent and independent variables. To write your research question, null hypothesis, and alternative hypothesis, fill in the following sentences with your variables:
Does independent variable affect dependent variable ?
Once you know the statistical test you’ll be using, you can write your hypotheses in a more precise and mathematical way specific to the test you chose. The table below provides template sentences for common statistical tests.
( ) | ||
test
with two groups | The mean dependent variable does not differ between group 1 (µ ) and group 2 (µ ) in the population; µ = µ . | The mean dependent variable differs between group 1 (µ ) and group 2 (µ ) in the population; µ ≠ µ . |
with three groups | The mean dependent variable does not differ between group 1 (µ ), group 2 (µ ), and group 3 (µ ) in the population; µ = µ = µ . | The mean dependent variable of group 1 (µ ), group 2 (µ ), and group 3 (µ ) are not all equal in the population. |
There is no correlation between independent variable and dependent variable in the population; ρ = 0. | There is a correlation between independent variable and dependent variable in the population; ρ ≠ 0. | |
There is no relationship between independent variable and dependent variable in the population; β = 0. | There is a relationship between independent variable and dependent variable in the population; β ≠ 0. | |
Two-proportions test | The dependent variable expressed as a proportion does not differ between group 1 ( ) and group 2 ( ) in the population; = . | The dependent variable expressed as a proportion differs between group 1 ( ) and group 2 ( ) in the population; ≠ . |
Note: The template sentences above assume that you’re performing one-tailed tests . One-tailed tests are appropriate for most studies.
If you want to know more about statistics , methodology , or research bias , make sure to check out some of our other articles with explanations and examples.
Methodology
Research bias
Hypothesis testing is a formal procedure for investigating our ideas about the world using statistics. It is used by scientists to test specific predictions, called hypotheses , by calculating how likely it is that a pattern or relationship between variables could have arisen by chance.
Null and alternative hypotheses are used in statistical hypothesis testing . The null hypothesis of a test always predicts no effect or no relationship between variables, while the alternative hypothesis states your research prediction of an effect or relationship.
The null hypothesis is often abbreviated as H 0 . When the null hypothesis is written using mathematical symbols, it always includes an equality symbol (usually =, but sometimes ≥ or ≤).
The alternative hypothesis is often abbreviated as H a or H 1 . When the alternative hypothesis is written using mathematical symbols, it always includes an inequality symbol (usually ≠, but sometimes < or >).
A research hypothesis is your proposed answer to your research question. The research hypothesis usually includes an explanation (“ x affects y because …”).
A statistical hypothesis, on the other hand, is a mathematical statement about a population parameter. Statistical hypotheses always come in pairs: the null and alternative hypotheses . In a well-designed study , the statistical hypotheses correspond logically to the research hypothesis.
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Turney, S. (2023, June 22). Null & Alternative Hypotheses | Definitions, Templates & Examples. Scribbr. Retrieved August 27, 2024, from https://www.scribbr.com/statistics/null-and-alternative-hypotheses/
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Despite the powerful benefits of entrepreneurial failure experience with regard to experiential learning and future venture performance, our understanding of how failure experience impacts entrepreneurs’ decision to reenter entrepreneurship while taking advantage of the lessons that they have learned from their previous entrepreneurial endeavors remains limited. While some studies have highlighted the potential of entrepreneurial failure experience to stimulate reentry intention, other researchers have argued that failure experience can actually decrease subsequent entrepreneurial intention. This study draws on various streams of research on entrepreneurs’ responses to business failures at the cognitive, affective, and behavioral levels to propose the existence of a curvilinear relationship between entrepreneurial failure and reentry intention. We employ hierarchical regression to test a series of hypotheses by reference to a sample of 379 entrepreneurs who had experienced failure in their recent business ventures. The results reveal that the degree of failure exhibits an inverted U-shaped relationship with reentry intention. Furthermore, we find that the effect of entrepreneurial failure on reentry intention is mediated by entrepreneurs’ learning from failure and that entrepreneurial passion moderates the effects of entrepreneurial failure on both learning from failure and reentry intention. This article helps explain the distinctive effects of failure experience on reentry intention and provides empirical evidence that can facilitate the development of tailor-made support programs that can help previously failed entrepreneurs address the challenges that they encounter during the process of reentry into entrepreneurship.
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The first author would like to acknowledge the financial support of the National Natural Science Foundation of China (Grant No: 72172165) and the Natural Science Foundation of Guangdong Province, China (Grant No: 2024A1515011283).
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Associated data.
In response to the European Food Safety Authority’s establishment of a tolerable weekly intake (TWI) for the sum of PFOA, PFNA, PFHxS, and PFOS, a method was developed to quantify and confirm 20 PFASs at the sub-parts-per-trillion level in fruit and vegetables. Improved sensitivity was achieved by (i) increasing the sample intake, (ii) decreasing the solvent volume in the final extract, and (iii) using a highly sensitive mass spectrometer. Except for PFTrDA, target PFASs could be quantitatively determined with an apparent recovery of 90–119%, limits of quantitation down to 0.5 ng/kg, and a relative standard deviation under within-laboratory reproducibility conditions of <28%. The method was successfully applied to 215 fruit and vegetable samples obtained from local grocery stores and markets. Leafy vegetables prove to be the main vegetable category responsible to PFAS exposure, mainly of PFOA, followed by PFHpA and PFHxA.
Per- and polyfluoroalkyl substances (PFASs) are an extensive class of synthetic chemicals known for their chemical and heat resistance as well as their ability to strongly reduce surface tension. They have been extensively manufactured and utilized in various industries due to these desirable properties. 1 They have been used in the production of non-stick cookware, waterproof clothing, and fire-fighting foams, among other products.
Due to increasing global concern about the potential negative health effects of PFASs, the European Food Safety Authority (EFSA) conducted a new risk assessment of PFASs in food. EFSA derived a tolerable weekly intake (TWI) of 4.4 ng/kg of body weight per week for the sum of four PFASs. These PFASs are perfluorooctanoic acid (PFOA), perfluorononanoic acid (PFNA), perfluorohexanesulfonic acid (PFHxS), and perfluorooctanesulfonic acid (PFOS); the so-called “EFSA-4”. It was shown that current exposure of a large part of the European Union (EU) population exceeds this TWI, even when applying the lower-bound principle (i.e., assuming that non-detected levels are equal to zero). The upper-bound exposure [i.e., assuming that non-detected levels equal the concentration of the limit of quantification (LOQ)] was much higher, implying a large uncertainty in the assessment and the need to apply more sensitive analytical methods.
The stringent requirements of the low TWI necessitate the use of highly sensitive analytical methods with low limits of quantification. When methods with relatively high LOQs are used, the majority of analyses yield non-detectable results. Typically, exposure assessments are conducted under an upper-bound scenario, where samples with non-detects are assumed to contain PFASs at the LOQ. Following this principle, if the method’s LOQs are too high, PFAS exposure can surpass the new TWI by many orders of magnitude, even in the absence of detected PFASs in the samples.
Considering the potential harm associated with PFASs, even at low concentrations, there is an urgency to develop analytical methods with low detection limits for various food products, as emphasized by EFSA. 2 The European Union Reference Laboratory for Persistent Organic Pollutants in Feed and Food (EURL-POPs) has issued guidance on PFAS analysis, specifying that for fruit and vegetables, LOQs should be ≤5 ng/kg for PFNA, ≤10 ng/kg for PFOA and PFOS, and ≤15 ng/kg for PFHxS. 3 Furthermore, laboratories are encouraged to aim for even lower LOQs, specifically ≤1 ng/kg for PFOA and PFNA, ≤2 ng/kg for PFOS, and ≤4 ng/kg for PFHxS. These latter LOQs have been adopted by Commission Regulation EU 2022/1431 as mandatory for monitoring purposes. 4
Within the food domain, according to EFSA, 2 fish and other seafood are the main sources of exposure to PFOA and PFOS, followed by eggs, meat products, and fruit. Notably, fruit and vegetables are an important source of exposure to PFOA, because of their substantial consumption compared to other foods.
Recent literature reviews have explored analytical methodologies for PFAS analysis and their occurrence in various sources, including food 5 , 6 Furthermore, in recent years, there has been an expanded focus on examining the presence and transfer of PFASs in fruit and vegetables. Various studies describe methodologies to monitor PFAS levels in fruit and vegetables. 7 − 20 Additionally, some studies have documented analytical methods to study the transfer of several PFASs from contaminated irrigation water to crops. 21 − 23 Regrettably, most of the developed methods did not meet the targeted and/or proposed LOQs currently required by the EURL-POPs 3 and commission regulation EU 2022/1431. 4 Most methods were validated at relatively high concentration levels, and/or no fit-for-purpose validation was reported. Table 1 offers a comparison of recent studies on the analysis of PFASs in fruit, vegetables, and other plant material, highlighting the substantial variability in analytical characteristics of current methods. As a result, only scarce high-quality quantitative data on PFASs in vegetables at required concentration levels was available prior to the study presented here.
detection/quantification limit | ||||||||
---|---|---|---|---|---|---|---|---|
authors | matrix | extraction method | clean-up procedure | instrumentation | targeted PFAS | value | methodology | lowest recovered spike level |
Zhou et al. | vegetables | acetonitrile + formic acid | Sin-QuEChERS (PSA, C18, and GCB) | UHPLC–MS/MS | 20 PFASs, including PFCAs, and PFSAs | 0.003–0.034 μg/kg (LOQ) | 10× S/N | 0.1 μg/kg |
Li et al. | vegetables | methanol | online SPE | UHPLC–MS/MS | 21 PFASs, including PFCAs, PFSAs, and FTSs | 0.002–0.008 μg/kg (LOD) | 3× SD of spike (0.2 μg/kg) | 0.2 μg/kg |
Nassazzi et al. | plant material | methanol | ENVI carb cartridge | UHPLC–MS/MS | 24 PFASs, including PFCAs, PFSAs, FASAs, and FTSs | 0.01–11.0 μg/kg (LOQ) | 10× S/N | 0.025 μg/kg |
Meng et al. | fruit and vegetables | methanol + ammonium hydroxide | WAX SPE | UHPLC–MS/MS | 45 PFASs, including PFCAs, PFSAs, PFEAs, FASAs, FTSs, FTCAs, and PFESAs | 0.025 to 0.25 ng/g (LOQ) | lowest recovered solvent standard × matrix effect | 1 μg/kg |
Piva et al. | vegetables | acetonitrile + formic acid | WAX SPE | UHPLC–MS/MS | 22 PFASs, including 3 FTSs | 0.05–0.5 μg/kg (LOQ) | 10× S/N | 1 μg/kg |
Zacs et al. | fruit and vegetables | acetonitrile + NaOH | WAX SPE | nano-LC–nano-ESI–Orbitrap MS | EFSA-4 | 0.001–0.002 μg/kg | lowest validated spike | 0.001 μg/kg |
In the current study, a method was developed and validated to detect and quantify 20 PFASs, including PFOA, PFNA, PFHxS, and PFOS, at the low ppt (ng/kg) level in a wide range of fruit and vegetables (see SI-2 of the Supporting Information). This study is the first description of a method that can achieve the very low detection limits required for human exposure assessments of PFAS via fruit and vegetables. The achievement of such low detection limits is especially challenging as background contamination of commonly applied PFAS becomes apparent. Also, we demonstrate an extensive validation protocol to include a wide range of vegetables. The method was subsequently applied to a selection of fruit and vegetables obtained from local grocery stores and weekly markets ( n = 215).
Methanol (MeOH) and acetonitrile of UHPLC/MS grade were purchased from Actu-All Chemicals (Oss, Netherlands). UHPLC/MS grade water was procured from Biosolve (Valkenswaard, Netherlands). All other chemicals were obtained from Merck (Darmstadt, Germany). A 2% ammonium hydroxide solution was prepared by diluting a 25% ammonium solution 12.5 times in acetonitrile. A 25 mM sodium acetate buffer was prepared by dissolving 3.40 g of sodium acetate trihydrate in 1 L of water and adjusting to pH 4 with glacial acetic acid. A 4 M hydrochloric acid solution was prepared by diluting 3.3 mL of 37% HCl to 10 mL with water, and lower concentrations were prepared by diluting this solution. Mobile phase A was a 20 mM ammonium acetate in water solution, was prepared by dissolving 1.54 g of ammonium acetate in 1 L of water. Mobile phase B was methanol.
All reference standards were obtained from Wellington Laboratories (Guelph, Ontario, Canada). The following perfluoroalkyl carboxylic acids (PFCAs) were used in this study: perfluoropentanoic acid (PFPeA, C 5 ), perfluorohexanoic acid (PFHxA, C 6 ), perfluoroheptanoic acid (PFHpA, C 7 ), PFOA (C 8 ), PFNA (C 9 ), perfluorodecanoic acid (PFDA, C 10 ), perfluoroundecanoic acid (PFUnDA, C 11 ), perfluorododecanoic acid (PFDoDA, C 12 ), perfluorotridecanoic acid (PFTrDA, C 13 ), and perfluorotetradecanoic acid (PFTeDA, C 14 ). All PFCAs were obtained as a mixture of 2 μg/mL in MeOH.
The following perfluoroalkyl sulfonic acids (PFSAs) were used in this study: perfluorobutanesulfonic acid (PFBS, C 4 ), PFHxS (C 6 ), perfluoroheptanesulfonic acid (PFHpS, C 7 ), PFOS (C 8 ), and perfluorodecanesulfonic acid (PFDS, C 10 ). These PFSAs were obtained as individual solutions of their sodium salts (except PFBS, which is a potassium salt) of 2 μg/mL in MeOH. Additionally, a few other PFASs were included in this study. Those being: perfluorooctanesulfonamide (PFOSA), hexafluoropropylene oxide–dimer acid (HFPO–DA), also known as GenX technology, Sodium dodecafluoro-3 H -4,8-dioxanonanoate (NaDONA), sodium dodecafluoro-3 H -4,8-dioxanonanoate (9Cl-PF3ONS), and sodium dodecafluoro-3 H -4,8-dioxanonanoate (11Cl-PF3OUdS). These compounds were also obtained at a concentration of 2 μg/mL in MeOH. All reference compounds have a chemical purity of at least 98%.
Isotopically labeled compounds were used as internal standards in this study. A mixture containing the following compounds was obtained at a concentration of 2 μg/mL in methanol: 13 C 2 -PFHxA, 13 C 4 -PFOA, 13 C 5 -PFNA, 13 C 2 -PFDA, 13 C 2 -PFUnDA, 13 C 2 -PFDoDA, 18 O 2 -PFHxS, and 13 C 4 -PFOS. Additionally, 13 C 3 -PFPeA, 13 C 4 -PFHpA, 13 C 3 -PFBS, and 13 C 3 -HFPO–DA were obtained as individual solutions at the same concentration. Isotopically labeled 13 C 8 -PFOA and 13 C 8 -PFOS standards were used as injection checks (2 μg/mL). All labeled compounds had a chemical purity of at least 98% and isotopic purities of at least 99% for 13 C and 94% for 18 O.
Ten grams of sample were transferred to a 50 mL polypropylene (PP) centrifuge tube (Greiner Bio-One, Kremsmünster, Austria). The sample was then fortified with 50 μL of internal standard solution (1 ng/mL) and 0.5 mL of 200 mM sodium hydroxide solution was added, followed by 10 mL of MeOH. The mixture was vortexed for 1 min in a multivortex mixer (VWR, VX-2500 Vulti-Tube Vortexer, Radnor, PA, U.S.A.), followed by 15 min of ultrasonication at room temperature (in an ultrasonic bath by Branson, Danbury, CT, U.S.A.) and 30 min of shaking on a rotary tumbler (REAX-2, Heidolph, Schwabach, Germany). After the extraction, 100 μL of formic acid was added and the mixture was centrifuged for 10 min at 3600 rpm at 10 °C (Rotixa 500 RS, Hettich Zentrifugen, Westphalia, Germany). The supernatant was then carefully decanted into a 50 mL PP tube that contained 25 mL of HPLC-grade water. The extract was mixed and centrifuged again if cloudy, before the cleanup.
For cleanup and further concentration of the sample, a Strata-X-AW cartridge (mixed mode weak anion exchange, 200 mg per 6 mL, 33 μm; Phenomenex, Torrance, CA, U.S.A.) was conditioned with 8 mL MeOH and then 8 mL of 0.04 M HCl. The extract was transferred onto the cartridge and slowly passed through (if necessary, by applying a vacuum) to allow interaction between the SPE material and the PFASs. The cartridge was then rinsed with 5 mL of 25 mM sodium acetate buffer, followed by 3 mL of 0.04 M HCl in MeOH. The PFASs were eluted from the cartridge using 5 mL of 2% ammonium hydroxide in acetonitrile and collected into a 14 mL PP tube (Greiner Bio-One, Kremsmünster, Austria).
The solvent was evaporated (at 40 °C using nitrogen gas) using a TurboVap LV Evaporator (Zymark, Hopkinton, MA, U.S.A.). After evaporation to dryness, 80 μL MeOH, 270 μL ammonium acetate buffer (20 mM), and 50 μL of the injection standard mixture (1 ng/mL) (containing 13 C 8 -PFOA and 13 C 8 -PFOS) were added. The residues were then reconstituted by rigorous mixing (vortex mixer) and 5 min of ultrasonication. The final extract was passed through a 0.45 μm regenerated cellulose syringe filter (Whatman, Little Chalfont, Buckinghamshire, U.K.) before LC–MS/MS analysis.
The UPLC–MS/MS analysis was performed using a Sciex ExionLC UPLC system (Sciex, Framingham, MA, U.S.A.). A Luna Omega PS C18 analytical column (100 Å, 100 × 2.1 mm inner diameter, 1.6 μm, Phenomenex, Torrance, CA, U.S.A.) was used to separate the PFASs at a column temperature of 40 °C. Additionally, a Gemini C18 analytical column (110 Å, 50 × 3 mm inner diameter, 3 μm, Phenomenex) was used as an isolator column, placed between the pump and the injector valve to isolate and delay potential PFAS contamination eluting from the LC system parts prior to the injection valve. The gradient: 0–1.5 min, 20% mobile phase B, 1.5–9.5 min, linear increase to 98% B with a final hold of 1.4 min. The gradient was returned to its initial conditions within 0.1 min and the column was allowed to equilibrate for 2.5 min before the next injection was initiated, resulting in a total run of 13.5 min. The flow rate was 0.5 mL/min and the injection volume 20 μL.
The detection of PFASs was done using MS/MS on a Sciex QTRAP 7500 system in negative electrospray ionization (ESI−) mode. The ion spray voltage, curtain gas, source temperature, gas 1, gas 2, and collision gas were set at −1500 V, 45 psi, 400 °C, 40, 80, and 9 psi, respectively. To fragment the PFASs, collision-induced dissociation (CID) was used with argon as the collision gas. The analysis was performed in multiple reaction monitoring (MRM) mode, using two mass transitions per component (except for PFPeA), which were selected based on the abundance of the signal and the selectivity of the transition. Additional information on the MRM transitions, entrance potential, collision energy, and cell exit potential can be found in Table S1 of the Supporting Information. The data were acquired using SciexOS and processed using MultiQuant software (SCIEX, Framingham, MA, U.S.A.).
To reduce the risk of contamination through material selection, all fluoropolymer containers (tubes, vials, etc.) and devices (filters, pipets, etc.) were excluded from the method, if possible. The analysts did not wear any cosmetics or PFAS-containing clothing during sample handling, as required by EU regulations (EU) 2022/1428. Although no significant concentrations of PFASs were observed in the procedural blanks, except for PFBA, PFPeA, and small amounts of PFOA, it is recommended to test solvents and chemicals for PFASs prior to method development. Several sources with low-contamination were identified and eliminated. This test became essential only after the need for very low detection limits.
To test and correct for incidental contamination originating from the laboratory or laboratory consumables, blank chemical preparations (procedural blanks) were carried out in duplicate each day. The signal of all samples was corrected with the average response of the procedural blanks. The impact of interfering signals becomes more pronounced with extremely low method detection limits.
This validation study aimed to cover a broad range of commonly consumed fruit and vegetables in the Netherlands. As a basis for the validation of the EURL POPs guidance document on PFAS analysis in food 3 was applied. The validation was done more extensively than required by that document.
The following parameters related to a quantitative confirmatory method were determined: selectivity, stability, robustness, apparent recovery (trueness based on spiked samples), within-laboratory reproducibility (expressed as relative standard deviation, RSD RL ), repeatability (expressed as relative standard deviation, RSD r ), limit of detection (LOD), limit of quantification (LOQ), and limit of confirmation (LOC).
The method was characterized as a quantitative confirmatory method and the validation was designed to challenge fit-for-purpose for this goal. Fruit and vegetables were selected and subdivided into five matrix categories: leafy vegetables, fruit, root vegetables, bulb vegetables, and leek, and “other vegetables” mostly containing fruiting vegetables, legumes, and cabbage. The validation of each matrix category was performed on a single day, yielding a total of 5 validation days ( Table 2 ). For each category, a representative matrix was selected for preparation of the matrix-fortified calibration (P1, Table 2 ). Furthermore, an additional six matrices (P2–P7, Table 2 ) of each category were analyzed as is (blank) and with the addition of all 20 PFASs at 2.5, 50, and 500 ng/kg. A detailed overview of the validation design is given in Table S2 of the Supporting Information.
number | leafy vegetables | bulb vegetables and leek | root vegetables | fruit | other vegetables |
---|---|---|---|---|---|
P1 (MFS) | spinach | onion | potato | apple | zucchini |
P2 | endive | onion | beets (peeled) | strawberry | cauliflower |
P3 | kale | leek | beets (unpeeled) | white grape | broccoli |
P4 | iceberg lettuce | garlic | carrot (peeled) | plum | snow peas |
P5 | Turkish lettuce | red onion | carrot (unpeeled) | pear | rhubarb |
P6 | chard | scallions | potato (peeled) | red berries | pumpkin |
P7 | Batavia lettuce | chives | potato (unpeeled) | apple | cucumber |
One specific sample batch (P1, Table 2 ) was selected for matrix-fortified standard calibration on each day. The matrix fortified standards (MFS calibration standards) included the following concentration levels to cover a wide concentration range: 0, 0.5, 1.0, 2.5, 5.0, 10, 25, 50, 100, 500, 1000, and 2000 ng/kg. Based on the PFAS concentration in the samples, the lower or higher end of the calibration line was used for quantification. Quantitative results were achieved using the matrix-fortified standard calibration approach, which involved correcting the signals (peak area) of the individual PFASs with the corresponding isotopically labeled internal standards. This correction accounts for differences in the recovery, ionization, and other matrix influences. For PFTrDA, PFHpS, PFDS, DONA, 9Cl-PF3ONS, and 11Cl-PF3OUdS no labeled internal standard were available. For these compounds, an internal standard was selected based on their retention time and chemical similarities. Retention time was the most important factor. The internal standards used per analyte are included in Table S1 of the Supporting Information.
For confirmatory analysis, criteria have been established in the EURL-POPs guidance document 3 for the maximum allowed deviation of the relative abundance of both diagnostic ions (ion ratio) resulting from an unknown sample. The maximum allowed deviation is 30%. Furthermore, the relative retention time of a PFAS should not deviate more than 1% from the reference relative retention time. To assess the possibility of confirming the identity of a detected compound using the presented method the average ion ratio and the average relative retention time of the matrix-fortified standard calibration samples was used as the reference value.
The EURL-POPs guidance document 3 states that analytical methods should demonstrate the ability to reliably and consistently separate the analytes of interest from other coextracted and possibly interfering compounds that may be present. It is known that PFOS detection may suffer from a coeluting interference of taurodeoxycholic acid (TDCA), which is a bile acid with the same transition as the most sensitive PFOS transition ( m / z 499 > 80). 28 This bile acid is particularly prominent in eggs. 29 In this method TDCA was chromatographically separated from PFOS and the mass transition m / z 499 > 99 was applied for quantitative purposes, preventing any interference. Moreover, it is unlikely that this bile acid interference occurs in fruit and vegetables. Additionally, it is noteworthy that although the m / z 499 to 99 transition is 75% less sensitive, it offers much greater specificity, resulting in fewer observed interferences in general. The robustness of the method was challenged by including many different fruit and vegetables. Furthermore, the validation was carried out on five different days and by three different technicians.
The stability of the PFASs in the samples and solvent solutions was not tested as it is generally agreed upon that these substances are very persistent. From the PFASs included in this study, only HFPO–DA is known to degrade to heptafluoropropyl 1,2,2,2-tetrafluoroethyl ether in aprotic polar solvents, such as dimethyl sulfoxide, acetone, and to a lesser extent in acetonitrile; with 100% degradation after approximately 15 h. 30 , 31
Additionally, Zhang et al. showed that the degradation of HFPO–DA in acetonitrile was negligible in the presence of water (>20%), suggesting that acetonitrile can be used as a solvent for sample preparation when the water content is >20%. 31 In our experiments, the lowest water concentration in acetonitrile of the extract is approximately 8%, under alkaline conditions. Under these conditions, we therefore assume that the degradation of HFPO–DA is limited, but not excluded. To test this hypothesis, a single-factor ANOVA was performed on the relative standard deviation of the signal of the internal standards for HFPO-DA, PFOA, and PFOS; two PFASs that are considered to be very persistent. We assume that there would be a larger variance in signal intensity of HFPO-DA, when degradation is a critical factor.
For the calculation of apparent recovery (trueness), repeatability, and within-laboratory reproducibility for each PFAS the quantitative data obtained from the samples spiked at 2.5, 50, and 500 ng/kg of each analyte was used. The apparent recovery for each sample was calculated by dividing the calculated concentration by the actual spiked concentration, in some cases after correction for a signal found in the procedural blank or the non-fortified sample. The reported apparent recovery for a specific PFAS is the average of all spiked samples at a concentration level. The relative standard deviation under repeatability conditions (RSD r ) was calculated from all the individual analyzed matrices within a single matrix category for each concentration level. The relative standard deviation under within-laboratory reproducibility conditions (RSD RL ) was calculated from all matrices at each concentration level. Note that in this validation design, for repeatability calculations different matrices are included. Therefore, the result is an overestimation of the actual repeatability. This approach was used to determine the overall performance of the method with a very high variation in types of fruit and vegetables.
The performance criteria were established in advance and derived from the EURL POPs guidance document. 3 The guidance document differentiates analysis for compliance testing and analysis for monitoring purposes. Compliance testing relates to the EFSA-4 PFASs at the regulatory level. As for fruit and vegetables, no regulatory limits have been established, in this validation the method performance criteria for monitoring apply. The apparent recovery must lie between 65 and 135%, RSD RL should be ≤25%. No criterion for RDS r is established.
As this method would be applied to food exposure studies, it is crucial to establish limits for determining the absence and presence of specific substances. To accomplish this, we have adopted the approach previously described by Berendsen et al., 32 with a focus on the LOQ and LOC.
The LOQ represents the concentration at which a quantitative result can be obtained, typically based on a single ion transition, whereas confirmation of the identity at this concentration may not be possible. Concentrations at or below the LOQ are used to report the absence of a substance, based on this single ion transition. The LOC is considered to be the lowest concentration level of a PFAS at which it complies with the confirmatory criteria, as described under “ Confirmation of Peak Identity ”. 33
For some substances, signals in the procedural blanks, originating from e.g. solvents, are common. Therefore, we applied two different strategies to determine the LOQ and LOC. One approach is employed when no substantial signal is observed in the procedural blanks, while the other is used when a substantial signal is detected in the procedural blanks.
If no signal of a specific PFAS is detected in the procedural blank samples, we established the LOQ as the lowest spiked concentration in the MFS calibration line with a signal-to-noise ratio ≥6. 34 The LOC, in this case, is defined as the lowest spiked concentration in the MFS calibration line, meeting the confirmatory requirements.
On the other hand, when a signal is detected in the procedural blank, we follow the guidelines set by the EURL, 3 which provides that the contribution of blank levels should not exceed 30% of the levels in the samples analyzed in the accompanying batch. In such a case, the LOQ was determined by multiplying the concentration of the PFAS in the procedural blank by a factor of 3.3. The LOC remains as the lowest spiked concentration in the MFS calibration line that meets the confirmatory requirements. If, in this scenario, the determined LOC is lower than the LOQ, it is set equal to the LOQ. In any case, the determined LOQ and LOC are assessed by comparing them to the results of the spiked validation samples and adjusted accordingly if needed (e.g., in case the LOQ derived from the MFS seems unachievable or unrealistic as that is only derived from a single matrix).
The developed method was applied to the analysis of 215 fruit and vegetables obtained from Dutch grocery stores and weekly markets, of which 35 leafy vegetables, 25 root vegetables, 23 bulb vegetables and leek, 50 fruit, and 82 other vegetables. The samples were collected and analyzed in 2021. A list of samples and their land of origin is included in SI-4 of the Supporting Information.
Method development.
Not all substances recommended by the EURL-POPs were included in this study, such as some long-chain PFSAs (perfluoroalkyl sulfonic acids) and next-generation PFASs. 3 These compounds were at the time unavailable to the laboratory.
Achieving the required LOQs for fruit and vegetables poses a significant challenge due to their exceptionally low target thresholds and diverse matrices. Our strategy to achieve the lowest possible LOQs involves increasing the concentration factor of samples by increasing the sample intake and lowering the extract reconstitution volume. However, practical constraints, such as the capacities of extraction tubes, shaking equipment, and centrifuges, limit the sample intake volume.
It is crucial to fine-tune the extraction process as well, focusing on optimizing the solvent and solvent-to-sample ratio to allow the extract to run through the solid-phase extraction (SPE) cartridge. In the case of certain fruit and vegetables, the final extracts exhibited turbidity. A filtering step was therefore a requirement. Even after filtering, some extracts were somewhat turbid, demonstrating that the practical limitations of the method had been reached. Final extracts that were still turbid were shortly centrifuged, using a high-speed centrifuge, at 12 000 rpm.
The extraction process presented particular challenges when dealing with leafy greens, as they tended to yield cloudy extracts. Moreover, the preparation of certain leafy greens, like chives and leek, occasionally proved cumbersome, especially during the grinding process, due to their unique textures and structures. The fibrous nature and large, flat surface areas of some leaves made grinding a labor-intensive task. These combined factors contribute to the complexity of the analytical process in this study.
To gain insights into the performance of the analytical process, we introduced internal standards into the samples prior to the preparation stage and added injection standards just before the sample injection. The injection standard consists of two isotopically labeled analogs of PFOS and PFOA (see SI-1 of the Supporting Information). Assessing the relative abundance of the internal- and injection standards, we found absolute recoveries ranging between 41 and 79% for PFOA and 32 and 63% for PFOS. Notably, bulb vegetables exhibited substantially lower absolute recoveries (32–53%) compared to other fruit and vegetables. Matrix effects for PFOA and PFOS were determined by comparing the injection standard added to sample matrices after cleanup with the injection standard added to the procedural blank, revealing a range from 32% for bulb vegetables to 157% for leafy vegetables. The matrix effect could only be determined for PFOA and PFOS since isotopically labeled variants ( 13 C 8 ) of those PFAS were included in the injection standard.
The hydrophobic nature of the PFASs included in this study is very diverse, as indicated by the octanol–water partitioning coefficient ( K ow ) ranging from 3.4 for PFPeA to 7.15 for PFUnDA, 35 with higher values for the longer chain PFASs (no data available). 36 Prior work by Zenobio et al. highlighted the adsorption of hydrophobic PFASs to container surfaces. 36 From the recovery experiments in the current study, this effect was observed for the long-chain PFASs (≥C 12 ). Approximate 50% MeOH is required to keep these PFASs in solution in the glass LC vial. However, a high organic solvent percentage in the final extract jeopardizes the chromatographic separation of short-chain PFAS. To address this, we opted for a final extract composition containing 32.5% MeOH, ensuring satisfactory peak shapes for the early eluting PFASs and an acceptable recovery for the long-chain PFASs.
Given that long-chain PFASs (≥C 12 ) were anticipated to be present in crops to a lesser extent than shorter chain PFASs, 37 an absolute recovery within the range of approximately 5 to 20% compared to PFOA was deemed an acceptable threshold. PFHxDA (perfluorohexadecanoic acid) and PFODA (perfluorooctadecanoic acid) were originally included in the method development. However, it demonstrated extremely low absolute recovery under the current conditions. Given the unlikely accumulation of these compounds in fruit or vegetables, we adjusted the method’s focus toward more hydrophilic PFASs. During method development and validation, perfluorobutyric acid (PFBA) was also considered. Unfortunately, it displayed severe background signals in all injections, restricting the method’s applicability (see SI-3 of the Supporting Information). Consequently, PFBA was excluded from the method. A MRM chromatogram of a potato sample spiked at 10 ng/kg with all 20 PFASs is presented in Figure Figure1 1 . In SI-3 of the Supporting Information, example chromatograms are included of unspiked samples, and at 1 ng/kg.
MRM chromatogram of all 20 PFASs in a spiked potato sample at 10 ng/kg. PFOSA is not visible in the current view but elutes after 10 minutes.
In examining the selectivity challenges posed by both PFBA and PFPeA, which have only a single sufficiently abundant product ion in MS/MS detection, the method’s limitation becomes apparent. It becomes difficult to conclusively determine whether an observed signal is related to the presence of an interfering substance or if PFBA or PFPeA is genuinely present in the chromatogram. The few publications that integrated PFBA and PFPeA in their methods and reported their presence in fruit and vegetables share this limitation, often without addressing the lack of selectivity. Therefore, findings related to PFBA and PFPeA should be interpreted with caution. To address this selectivity issue, we introduced the ion transition from precursor ion mass to precursor ion mass at low collision energy for PFPeA, allowing for the calculation of relative ion abundance. It is important to note that this approach deviates from EURL guidance requirements, and for definitive confirmation, an additional orthogonal separation or alternative detection technique must be employed.
In the current study, the inclusion of PFOSA, a neutral PFAS, needs some extra clarification. As a neutral compound, PFOSA does not interact with the anion exchange mechanism of the SPE cleanup procedure, only interacting with the backbone material based on its hydrophobicity. During the SPE procedure, the cartridge is flushed with methanol, causing a large fraction of PFOSA to elute from the column. Only a small part is eluted in the final elution step. This fraction is sufficient for the quantitative determination of PFOSA, but due to the lower absolute recovery, only with a higher detection limit and a larger variance in recovery. The PFOSA recovery can be improved by collecting, evaporating, reconstituting, and injecting the methanolic wash fraction separately.
Additionally, another challenging compound to analyze is HFPO-DA, known for its susceptibility to degradation under specific conditions. To test for the degradation of HFPO-DA, a single-factor ANOVA was conducted on the relative standard deviation of the signals of the internal standards for HFPO-DA, PFOA and PFOS. No significant variance was observed in the signal of the internal standard of HFPO-DA compared to PFOA and PFOS ( p = 0.39, among all matrix categories). Consequently, the null hypothesis was rejected, suggesting that any potential degradation of HFPO-DA is negligible during the evaporation of the extracts. This ANOVA analysis was based on a total of 10 individual measurements, with all matrix categories included twice.
The determined LOQs for each matrix category are presented in Table 3 . We selected the definition of the LOQ fitting the aim of this research: exposure assessment. A clear definition of the LOQ is crucial to obtain reliable data as requested by the risk assessors. Unfortunately, the definition of the LOQ and the determination of it is not harmonized. This commonly results in underestimations of the actual LOQ, since often system-LOQs are used, instead of method-LOQs. This often results in potential false positives and an overestimated risk. 33
analyte | leafy vegetables | bulb vegetables and leek | root vegetables | fruit | other vegetables |
---|---|---|---|---|---|
PFPeA | 25 | 10 | 100 | 100 | 25 |
PFHxA | 1.0 | 1.0 | 0.5 | 2.5 | 1.0 |
PFHpA | 0.5 | 1.0 | 2.5 | 2.5 | 0.5 |
PFOA | 25 | 25 | 10 | 25 | 25 |
PFNA | 0.5 | 2.5 | 1.0 | 1.0 | 0.5 |
PFDA | 0.5 | 2.5 | 0.5 | 0.5 | 0.5 |
PFUnDA | 0.5 | 2.5 | 2.5 | 0.5 | 0.5 |
PFDoDA | 0.5 | 1.0 | 2.5 | 0.5 | 0.5 |
PFTrDA | |||||
PFTeDA | 500 | 1 | 100 | 2.5 | 500 |
PFBS | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 |
PFHxS | 0.5 | 0.5 | 0.5 | 1.0 | 0.5 |
PFHpS | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 |
PFOS | 0.5 | 1 | 0.5 | 0.5 | 0.5 |
PFDS | 1.0 | 1.0 | 1.0 | 1.0 | 1.0 |
PFOSA | 25 | 2.5 | 2.5 | 0.5 | 2.5 |
HFPO–DA | 0.5 | 2.5 | 2.5 | 2.5 | 1.0 |
DONA | 1.0 | 2.5 | 2.5 | 5.0 | 0.5 |
9Cl-PF3ONS | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 |
11Cl-PF3OUdS | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 |
The apparent recoveries and RSD r ’s were first calculated within each matrix category. Upon comparing the outcomes across different categories, no statistically significant differences were observed. As a result, it was decided to combine all matrix groups to determine the method performance characteristics. Note that in all series, the MFS calibration was based on a matrix from the same category as the actual samples. As such, this is also applied in the practical application of the method. The validation results for apparent recovery, RSD r , and RSD RL at all the validation levels are presented in Table 4 .
analyte | spike level (ng kg ) | number of samples confirmed | apparent recovery (%) | RSD (%) | RSD (%) | conclusion |
---|---|---|---|---|---|---|
PFPeA | 500 | 29 | 97 | 13 | 17 | quan |
PFHxA | 2.5 | 29 | 95 | 15 | 16 | quan |
50 | 30 | 102 | 4 | 5 | ||
500 | 30 | 103 | 3 | 3 | ||
PFHpA | 2.5 | 19 | 95 | 12 | 13 | quan |
50 | 30 | 100 | 10 | 11 | ||
500 | 30 | 103 | 4 | 4 | ||
PFOA | 50 | 29 | 103 | 4 | 8 | quan |
500 | 30 | 99 | 7 | 8 | ||
PFNA | 2.5 | 30 | 97 | 9 | 11 | quan |
50 | 30 | 103 | 4 | 8 | ||
500 | 30 | 101 | 4 | 7 | ||
PFDA | 2.5 | 30 | 101 | 12 | 12 | quan |
50 | 30 | 107 | 9 | 10 | ||
500 | 30 | 101 | 7 | 7 | ||
PFUnDA | 2.5 | 30 | 95 | 16 | 16 | quan |
50 | 30 | 102 | 6 | 7 | ||
500 | 30 | 102 | 4 | 5 | ||
PFDoDA | 2.5 | 29 | 113 | 23 | 23 | quan |
50 | 30 | 103 | 5 | 6 | ||
500 | 30 | 102 | 4 | 5 | ||
PFTrDA | 2.5 | 14 | 146 | 35 | 44 | qual |
50 | 30 | 134 | 63 | 64 | ||
500 | 30 | 139 | 52 | 57 | ||
PFTeDA | 500 | 30 | 108 | 8 | 10 | quan |
PFBS | 2.5 | 29 | 97 | 21 | 24 | quan |
50 | 30 | 102 | 5 | 6 | ||
500 | 30 | 103 | 4 | 5 | ||
PFHxS | 2.5 | 29 | 104 | 9 | 9 | quan |
50 | 30 | 106 | 6 | 7 | ||
500 | 30 | 107 | 3 | 6 | ||
PFHpS | 2.5 | 30 | 105 | 16 | 17 | quan |
50 | 30 | 104 | 12 | 15 | ||
500 | 30 | 105 | 12 | 13 | ||
PFOS | 2.5 | 28 | 104 | 13 | 14 | quan |
50 | 30 | 101 | 4 | 5 | ||
500 | 30 | 104 | 3 | 4 | ||
PFDS | 2.5 | 30 | 94 | 16 | 25 | quan |
50 | 30 | 90 | 13 | 23 | ||
500 | 30 | 92 | 13 | 24 | ||
PFOSA | 50 | 30 | 101 | 7 | 10 | quan |
500 | 30 | 102 | 6 | 7 | ||
HFPO–DA | 2.5 | 23 | 96 | 17 | 17 | quan |
50 | 24 | 108 | 6 | 7 | ||
500 | 30 | 107 | 8 | 9 | ||
DONA | 50 | 30 | 119 | 17 | 21 | quan |
500 | 30 | 103 | 13 | 20 | ||
9Cl-PF3ONS | 2.5 | 30 | 105 | 23 | 23 | quan |
50 | 30 | 101 | 24 | 23 | ||
500 | 30 | 103 | 22 | 22 | ||
11Cl-PF3OUdS | 2.5 | 30 | 99 | 27 | 37 | qual |
50 | 30 | 94 | 21 | 28 | quan | |
500 | 30 | 97 | 18 | 28 |
The method proved to be fit-for-purpose for quantification and confirmation of most PFASs included in all matrix categories. PFTrDA did not meet the quantitative performance criteria at all levels and as such, PFTrDA can only be analyzed qualitatively using this method. This is a direct result of the absence of a fitting internal standard. Also for PFDS, DONA, 9Cl-PF3ONS, and 11Cl-PF3OUdS no isotopically labeled internal standards are available. The RSD RL for these substances is higher compared to the other PFASs, but they do mostly comply with the performance criteria.
The required LOQs stated by the EURL guidelines 3 for the analysis of the EFSA-4 PFAS in fruit and vegetables are achieved for PFNA, PFHxS, and PFOS, but not for PFOA. The targeted LOQs stated by the guidelines (which are equal to the required LOQs by the commission recommendation 2022/1431) are achieved for PFNA in almost all matrix categories, PFHxS and PFOS. They were not achieved for PFNA in the category “bulb vegetables and leek” and for PFOA in all matrix categories. In all these cases the elevated LOQs are a result of a signal in the procedural blank. For PFOA this blank contribution was around 5 ng/kg in all cases and for PFNA this was approximately 0.5 ng/kg. Clearly, to achieve the target LOQs extra effort is required to eliminate the background contamination for PFOA and to a lesser extent for PFNA. That requires an extremely controlled working environment and an extreme level of quality control on solvents and consumables.
High LOQs were observed for PFPeA, indicating that the current method is unsuitable for the quantitative analysis of PFPeA at low ppts levels, as evident from the validation results. This issue is a result of background signals in the chromatogram. Most likely originating from an interfering substance that shares the same ion transition and retention time as PFPeA. 38 Further work is needed to identify the exact cause of these elevated LOQs.
For HFPO–DA the validation of all matrix categories except “bulb vegetables and leek” complied with all quantitative and confirmative performance criteria. Only in “bulb vegetables and leek”, HFPO–DA showed high interfering signals in the ion transition used for confirmatory analysis. Furthermore, also the most abundant ion transition showed high signals. As the confirmatory criteria were not met, it cannot be stated if HFPO–DA is present in these samples at a high level or if another substance is interfering with the quantification and confirmation of HFPO–DA.
Some compounds showed a higher variability in the LOQ between matrix categories. PFTeDA’s LOQs ranged from 500 pg/g in leafy greens and other vegetables to as low as 1 pg/g in bulb vegetables. The variability may be caused by the low absolute recovery of PFTeDA, mainly attributed to its tendency to adsorb to the LC-vial. For some matrices PFTeDA remained better in solution, yielding lower LOQs for 3 of the 5 validated categories ( Table 3 ). Future work will be undertaken to improve the solubility of PFTeDA and other long-chain compounds, to improve the absolute recovery.
The developed method was applied to analyze of 215 fruit and vegetable samples obtained from Dutch grocery stores and weekly markets, including 35 leaf vegetables, 23 bulb vegetables including leeks, 25 root vegetables, 50 fruit, and 82 other vegetables. Note that, in specific series, lower or slightly higher LOQs were achieved compared to the validation due to a lower signal in the procedural blanks.
Out of the 215 fruit and vegetables, the presence of one or more PFASs was confirmed in 87 (40.5%) samples. These included 25 leaf vegetables (71%), 3 bulb vegetables and leek (13%), 20 root vegetables (80%), 21 fruit (42%), and 18 other vegetables (22%). It is common to detect multiple PFASs in a single sample, with a total of 156 PFASs confirmed, reaching a maximum of 7 in a single sample. Concentrations ranged from 0.3 ng/kg to 117 ng/kg, indicating a highly right-skewed distribution. The monitoring data can be found in the Risk assessment of exposure to PFAS through food and drinking water by the RIVM. 39 A schematic presentation of the results is shown in Figure Figure2 2 .
Schematic representation of detected PFAS concentrations in the fruit and vegetable samples, per PFAS. Detected PFASs are individual observations, with no sum-concentrations of different samples. n = number of occasions that a specific PFAS was detected in the samples (number of samples = 215).
Root vegetables have the highest frequency of PFAS detection (80%), but concentrations are all below 7 ng/kg. Mainly PFPeA and PFBS were detected. Leafy vegetables also have a high frequency of contamination (71%) and in this category, the highest concentration was found, mainly of PFOA followed by PFHpA and PFHxA. The highest concentrations were found in crisp lettuce, followed by endives and spinach. Fruit has a lower frequency of occurrence of PFASs (42%) with no specific type of fruit standing out: mainly PFUnDA and PFOA were found, all at concentrations below 6 ng/kg. Other vegetables have a frequency of detection of 22%. In specific cases elevated concentrations were detected, in all cases for PFUnDA. The category “bulb vegetable and leek” seems to have relatively high PFAS content, see Figure Figure3 3 . However, the frequency of detection is low, and only in one case an elevated concentration was found in a leek sample: 96 ng/kg PFUnDA.
Schematic representation of detected PFAS concentrations in the fruit and vegetable samples, per matrix category. Detected PFASs are individual observations, no sum-concentrations of different PFASs. n = number of occasions that a PFAS was detected in the samples (number of samples = 215).
Interestingly, the data suggest a relation between the matrix category and the PFASs detected. PFPeA was mainly found in the root vegetables. PFHpA, PFNA, and PFBS were most prominent in leafy vegetables. PFOA was only found in fruit, leafy vegetables, and root vegetables, not in the other two categories. More generic, the above-ground vegetables and fruit seem to contain mainly C 7 – C 11 carboxylic acids and some PFOS, whereas the underground vegetables contain mainly the shorter chain carboxylic acids and sulfonates: PFPeA and PFBS. Most likely, the observed effects are the result of matrix-specific uptake kinetics and are also influenced by different exposure routes, e.g. via uptake from soil and direct contact with irrigation/sprinkling water and air. For the latter two, the PFAS concentration is related to the plant surface area to mass ratio.
In general, the observations are in good agreement with the data reported previously. It was demonstrated that in Belgium, most similar to The Netherlands, PFOA contamination mainly occurs in leafy vegetables and root vegetables. 12 Also, the concentration levels for the EFSA-4 PFASs are in good agreement. Also 10 demonstrated high accumulation of PFOA in leafy vegetables and grapes. Furthermore, the finding of PFOA and PFOS in carrots and the finding of a series of PFCAs in lettuce is in agreement with previously published data. 14 The finding of multiple PFCAs in potato as previously reported 14 is not in agreement with the current study, where only mainly PFPeA was detected in potatoes.
According to multiple publications, 9 , 13 , 20 in fruit and vegetables most often PFBA was detected. Furthermore, in uptake studies 22 , 23 it was reported that mainly the short-chain PFASs are taken up by leafy vegetables and crops. Unfortunately, in the current study, PFBA could not be determined according to current quality standards. Notably, we observed higher concentrations of PFHxA and longer chains compared to PFPeA in all positive samples except potatoes. Uptake kinetics could be different among fruit and vegetable species. Another explanation for the observed difference could be the occurrence of different exposure routes and spatial effects (e.g., related to PFAS use and the occurrence of PFAS hotspots in the vicinity of the production site). Note the potential lack of selectivity for PFBA as previously mentioned.
Among the PFASs detected, the finding of PFUnDA stands out: it is found more often than expected and at higher levels: PFUnDA has not been previously reported and also no applications of PFUnDA are known. Even though it is unknown what the origin of PFUnDA is, its presence was confirmed by the observation of two ion transitions, a correct relative ion abundance, and a relative retention time.
As most of the concentration levels of PFAS in fruit and vegetables are low, it is important to develop and apply analytical methods with low LOQs when studying human exposure to PFASs through consumption of fruit and vegetable consumption. The method proved to be useful in detecting the currently deemed most relevant PFASs and important analogs, at relevant levels. The LOQs of some of the PFASs should be lowered further. However, these challenges arise primarily due to background signals originating from laboratory consumables, solvents, and the working environment. Special requirements may therefore be needed to further lower the LOQs.
The work presented was funded by the Dutch Ministry of Agriculture, Nature and Food Quality (Project WOT-02-001-015) and the Ministry of Public Health, Welfare and Sports. The authors thank our colleagues from the WFSR Quality Department for critically assessing the validation plan and report.
Published as part of Journal of Agricultural and Food Chemistry virtual special issue “North American Chemical Residue Workshop”.
The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acs.jafc.4c01172 .
The authors declare no competing financial interest.
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COMMENTS
Present the findings in your results and discussion section. Though the specific details might vary, the procedure you will use when testing a hypothesis will always follow some version of these steps. Table of contents. Step 1: State your null and alternate hypothesis. Step 2: Collect data. Step 3: Perform a statistical test.
Formulate the Hypotheses: Write your research hypotheses as a null hypothesis (H 0) and an alternative hypothesis (H A).; Data Collection: Gather data specifically aimed at testing the hypothesis.; Conduct A Test: Use a suitable statistical test to analyze your data.; Make a Decision: Based on the statistical test results, decide whether to reject the null hypothesis or fail to reject it.
HYPOTHESIS TESTING. A clinical trial begins with an assumption or belief, and then proceeds to either prove or disprove this assumption. In statistical terms, this belief or assumption is known as a hypothesis. Counterintuitively, what the researcher believes in (or is trying to prove) is called the "alternate" hypothesis, and the opposite ...
A statistical hypothesis test is a method of statistical inference used to decide whether the data sufficiently supports a particular hypothesis. A statistical hypothesis test typically involves a calculation of a test statistic. Then a decision is made, either by comparing the test statistic to a critical value or equivalently by evaluating a ...
A hypothesis test consists of five steps: 1. State the hypotheses. State the null and alternative hypotheses. These two hypotheses need to be mutually exclusive, so if one is true then the other must be false. 2. Determine a significance level to use for the hypothesis. Decide on a significance level.
A hypothesis test is a procedure used in statistics to assess whether a particular viewpoint is likely to be true. They follow a strict protocol, and they generate a 'p-value', on the basis of which a decision is made about the truth of the hypothesis under investigation.All of the routine statistical 'tests' used in research—t-tests, χ 2 tests, Mann-Whitney tests, etc.—are all ...
Hypothesis testing is a crucial procedure to perform when you want to make inferences about a population using a random sample. These inferences include estimating population properties such as the mean, differences between means, proportions, and the relationships between variables. This post provides an overview of statistical hypothesis testing.
In hypothesis testing, the goal is to see if there is sufficient statistical evidence to reject a presumed null hypothesis in favor of a conjectured alternative hypothesis.The null hypothesis is usually denoted \(H_0\) while the alternative hypothesis is usually denoted \(H_1\). An hypothesis test is a statistical decision; the conclusion will either be to reject the null hypothesis in favor ...
Components of a Formal Hypothesis Test. The null hypothesis is a statement about the value of a population parameter, such as the population mean (µ) or the population proportion (p).It contains the condition of equality and is denoted as H 0 (H-naught).. H 0: µ = 157 or H0 : p = 0.37. The alternative hypothesis is the claim to be tested, the opposite of the null hypothesis.
A hypothesis test is a statistical inference method used to test the significance of a proposed (hypothesized) relation between population statistics (parameters) and their corresponding sample estimators. In other words, hypothesis tests are used to determine if there is enough evidence in a sample to prove a hypothesis true for the entire population. The test considers two hypotheses: the ...
Test Statistic: z = x¯¯¯ −μo σ/ n−−√ z = x ¯ − μ o σ / n since it is calculated as part of the testing of the hypothesis. Definition 7.1.4 7.1. 4. p - value: probability that the test statistic will take on more extreme values than the observed test statistic, given that the null hypothesis is true. It is the probability ...
Mean Population IQ: 100. Step 1: Using the value of the mean population IQ, we establish the null hypothesis as 100. Step 2: State that the alternative hypothesis is greater than 100. Step 3: State the alpha level as 0.05 or 5%. Step 4: Find the rejection region area (given by your alpha level above) from the z-table.
Hypothesis testing is an act in statistics whereby an analyst tests an assumption regarding a population parameter. The methodology employed by the analyst depends on the nature of the data used ...
There are 5 main hypothesis testing steps, which will be outlined in this section. The steps are: Determine the null hypothesis: In this step, the statistician should identify the idea that is ...
Hypothesis testing is a technique that is used to verify whether the results of an experiment are statistically significant. It involves the setting up of a null hypothesis and an alternate hypothesis. There are three types of tests that can be conducted under hypothesis testing - z test, t test, and chi square test.
Medical providers often rely on evidence-based medicine to guide decision-making in practice. Often a research hypothesis is tested with results provided, typically with p values, confidence intervals, or both. Additionally, statistical or research significance is estimated or determined by the investigators. Unfortunately, healthcare providers may have different comfort levels in interpreting ...
Hypothesis Testing Formula. Z = ( x̅ - μ0 ) / (σ /√n) Here, x̅ is the sample mean, μ0 is the population mean, σ is the standard deviation, n is the sample size. How Hypothesis Testing Works? An analyst performs hypothesis testing on a statistical sample to present evidence of the plausibility of the null hypothesis.
Hypothesis testing; T-test definition and formula explanation; Choosing the level of significance; T-distribution and p-value; Conclusion; Hypothesis testing. Meet David! He is a high school student and he has started to study statistics recently. ... So, if I conduct a study, I can always set α around 0.00001 (or less) and get valid results".
A number of elements involved in hypothesis testing are - significance level, p-level, test statistic, and method of hypothesis testing. (Also read: Introduction to probability distributions ) A significant way to determine whether a hypothesis stands true or not is to verify the data samples and identify the plausible hypothesis among the null ...
Hypothesis testing is a formal procedure for investigating our ideas about the world using statistics. It is used by scientists to test specific predictions, called hypotheses, by calculating how likely it is that a pattern or relationship between variables could have arisen by chance.
Hypothesis testing is composed of two parts: null and alternative hypothesis. A null hypothesis (Ho) is a statement that proposes there is no difference between what is observed and the control.
The null hypothesis (H 0) answers "No, there's no effect in the population." The alternative hypothesis (H a) answers "Yes, there is an effect in the population." The null and alternative are always claims about the population. That's because the goal of hypothesis testing is to make inferences about a population based on a sample.
Hypothesis testing is the process used to evaluate the strength of evidence from the sample and provides a framework for making determinations related to the population, ie, it provides a method for understanding how reliably one can extrapolate observed findings in a sample under study to the larger population from which the sample was drawn ...
In addition, this study used the stepwise regression method (Baron & Kenny, 1986) to test the mediating role of learning from failure in this context. As shown in Model 4 of Table 4 , the relationship between learning from failure and reentry intention is significant and positive (γ1 = 0.776, p < 0.01), thus confirming Hypothesis 3.
This study is the first description of a method that can achieve the very low detection limits required for human exposure assessments of PFAS via fruit and vegetables. ... To test this hypothesis, a single-factor ANOVA was performed on the relative standard deviation of the signal of the internal standards for HFPO-DA, PFOA, and PFOS; two ...