| Literature DB >> 31557188 |
Micaela M Kulesz1, Torbjörn Lundh2, Dirk-Jan De Koning3, Carl-Johan Lagerkvist1.
Abstract
Biotechnology can provide innovative and efficient tools to support sustainable development of aquaculture. It is generally accepted that use of the term 'genetically modified' causes controversy and conflict among consumers, but little is known about how using the term 'biotechnology' as a salient feature on product packaging affects consumer preferences. In an online discrete choice experiment consisting of two treatments, a set of 1005 randomly chosen Swedish consumers were surveyed about use of hormone and triploidization sterilization techniques for salmonids. The information given to the treatment group included an additional sentence stating that the triploidization technique is an application of biotechnology, while the control group received the same text but without reference to biotechnology. Analysis using a hierarchical Bayes approach revealed significant consumer reactions to the term biotechnology. When the term was included in information, variation in consumer willingness-to-pay (WTP) estimates increased significantly. Moreover, some participants were dissuaded towards an option guaranteeing no biotechnological intervention in production of fish. These results have multiple implications for research and for the food industry. For research, they indicate the importance of examining the distribution of variation in WTP estimates for more complete characterization of the effects of information on consumer behavior. For the food industry, they show that associating food with biotechnology creates more variability in demand. Initiatives should be introduced to reduce the confusion associated with the term biotechnology among consumers.Entities:
Year: 2019 PMID: 31557188 PMCID: PMC6762195 DOI: 10.1371/journal.pone.0222494
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
Socio-demographic characteristics of the study sample and of the Swedish population as a whole.
| Variable | Description | Sample | Swedish population |
|---|---|---|---|
| Male (base) | 43.18% | 49.80% | |
| Female | 56.82% | 50.20% | |
| Average (in years) | 47 | 41 | |
| Average household income (in SEK) | 30 001–40 000 | 25 000–28 999 | |
| Place of residence | |||
| | City (>150 000 inhabitants) | 35.62% | 37.13% |
| | Urban/medium-sized city (50 000–150 000 inhabitants) | 29.25% | 34.56% |
| | Rural development (<50 000 inhabitants) | 35.12% | 28.31% |
| | Average number of individuals per household | 2.35 | 2.60 |
Attitudes to science and interest in fish consumption among study participants.
| Variable | Description | Yes | No |
|---|---|---|---|
| | Science has mostly had a positive impact on the quality of food | 56.82% | 43.18% |
| | I have a strong interest in fish consumption | 47.36% | 52.64% |
| | Farmed fish is safe to consume. | 37.91% | 62.09% |
Attributes and levels.
| Attribute | Levels | Description |
|---|---|---|
| Farm | Fish raised in cages in the ocean or in the sea | |
| Wild | Naturally-born fish harvested in the wild | |
| None | Farmed fish not subjected to any sterilization technique | |
| Hormones | Farmed fish sterilized using hormone treatment | |
| Triploid | Farmed fish sterilized using the triploidization technique | |
| 130 SEK/kg | ||
| 260 SEK/kg | ||
| 390 SEK/kg |
Fig 1Example of a choice situation in the choice experiment.
Willingness-to-pay (WTP) estimates: Mean coefficients in 0.01SEK.
| Control | Treatment | |||
|---|---|---|---|---|
| WTP | Std. Err. | WTP | Std. Err. | |
| -3.353 | (0.274) | -3.718 | (0.317) | |
| -0.176 | (0.038) | 0.048 | (0.064) | |
| -0.183 | (0.041) | 0.031 | (0.064) | |
| -0.162 | (0.032) | -0.092 | (0.061) | |
| 0.016 | (0.031) | 0.159 | (0.063) | |
| 0.038 | (0.020) | 0.046 | (0.039) | |
| 0.057 | (0.040) | 0.005 | (0.059) | |
| 0.047 | (0.039) | -0.341 | (0.071) | |
| 0.070 | (0.028) | 0.031 | (0.064) | |
| -0.002 | (0.015) | 0.007 | (0.032) | |
| 0.048 | (0.030) | 0.099 | (0.066) | |
| 0.073 | (0.037) | 0.023 | (0.063) | |
| 0.015 | (0.034) | -0.040 | (0.075) | |
| 0.019 | (0.015) | 0.067 | (0.041) | |
| -0.004 | (0.034) | 0.056 | (0.075) | |
| 0.048 | (0.031) | -0.141 | (0.066) | |
| -0.097 | (0.036) | 0.016 | (0.077) | |
| 0.135 | (0.035) | 0.273 | (0.068) | |
| -0.349 | (0.034) | -0.221 | (0.060) | |
| 0.065 | (0.032) | -0.027 | (0.068) | |
| 0.150 | (0.038) | 0.172 | (0.067) | |
| -0.115 | (0.033) | -0.037 | (0.062) | |
| 0.032 | (0.032) | -0.096 | (0.062) | |
| 0.245 | (0.042) | 0.236 | (0.062) | |
| -0.211 | (0.036) | -0.188 | (0.080) | |
| 685 | 320 | |||
| 90420 | 42238 | |||
| 20000/10000 | 20000/10000 | |||
*** to 1%
** to 5%
Fig 2Density distribution of individual WTP coefficients for wild, hormones and triploid.
(a) In the control group. (b) In the treatment group.
Fig 3Density distribution of individual WTP coefficients (x) for the control and treatment groups.
(a) For Wild. (b) For Hormones. (c) For Triploid.