This document summarizes the results of a study on the population dynamics of periwinkles (Littorina littorea) in the East Frisian Wadden Sea. The study investigated larval recruitment patterns, population preferences, shell morphology, and genetic differentiation between populations. Simulation results showed no local larval recruitment due to hydrodynamic conditions. Behavioral experiments found snails preferentially aggregate with conspecifics from their own population but no preference based on olfactory cues. Shell measurements revealed morphological differentiation between populations that can be distinguished using linear discriminant analysis. Genetic analysis of microsatellite markers found significant genetic differentiation between populations.
Pension systems and reforms are critically influenced by demographic developments that are increasingly compared across countries to identify common issues and trends. For demographic projections researchers across the world rely on those produced by the United Nations; for Europe the demographic projections by Eurostat form the basis of the periodic aging report by the EU Commission. While these projections are technically well done the underlying assumptions for the demographic drivers – fertility, mortality and migration – in the central variants are limited and are largely flawed. Worse, they risk offering a wrong picture about the likely future developments and the relevant alternatives. This paper investigates the assumptions of the demographic drivers by UN and Eurostat, compares it with those by national projections in Portugal and Spain, and offers a review of alternative, recent and cutting edge approaches to project demographic drivers that go beyond the use of past demographic developments. They suggest that economic and other socio-economic developments have a main bearing on future trends in fertility, mortality and migration. And they support the assessment that the UN/Eurostat projected re-increase in fertility rates may not take place, that the increase in life expectancy may be much larger, that the future flows of net migrants to EU countries may be much higher and rising. The resulting overall underestimation of population aging has a bearing on the financial sustainability of the pension systems and reform choices, a topic to be explored in the next papers.
Pension systems and reforms are critically influenced by demographic developments that are increasingly compared across countries to identify common issues and trends. For demographic projections researchers across the world rely on those produced by the United Nations; for Europe the demographic projections by Eurostat form the basis of the periodic aging report by the EU Commission. While these projections are technically well done the underlying assumptions for the demographic drivers – fertility, mortality and migration – in the central variants are limited and are largely flawed. Worse, they risk offering a wrong picture about the likely future developments and the relevant alternatives. This paper investigates the assumptions of the demographic drivers by UN and Eurostat, compares it with those by national projections in Portugal and Spain, and offers a review of alternative, recent and cutting edge approaches to project demographic drivers that go beyond the use of past demographic developments. They suggest that economic and other socio-economic developments have a main bearing on future trends in fertility, mortality and migration. And they support the assessment that the UN/Eurostat projected re-increase in fertility rates may not take place, that the increase in life expectancy may be much larger, that the future flows of net migrants to EU countries may be much higher and rising. The resulting overall underestimation of population aging has a bearing on the financial sustainability of the pension systems and reform choices, a topic to be explored in the next papers.
Very brief mathematical introduction to the population dynamics of insects. Last part, on spatial spread is new. Joint work with W.A.C. Godoy and R.M. Coutinho.
This covers what a population pyramid is, and how to analyze one. It covers the three basic shapes and how they correspond to population growth or decline. Finally, students analyze pyramids of US cities based on unique trends (ie; an aging population in a retirement community).
Each month, join us as we highlight and discuss hot topics ranging from the future of higher education to wearable technology, best productivity hacks and secrets to hiring top talent. Upload your SlideShares, and share your expertise with the world!
Very brief mathematical introduction to the population dynamics of insects. Last part, on spatial spread is new. Joint work with W.A.C. Godoy and R.M. Coutinho.
This covers what a population pyramid is, and how to analyze one. It covers the three basic shapes and how they correspond to population growth or decline. Finally, students analyze pyramids of US cities based on unique trends (ie; an aging population in a retirement community).
Each month, join us as we highlight and discuss hot topics ranging from the future of higher education to wearable technology, best productivity hacks and secrets to hiring top talent. Upload your SlideShares, and share your expertise with the world!
Cave animals at the dawn of speleogenomicsfriedrichwsu
Presentation on the application and impact of next generation sequencing in studies of cave animals and other subterranean species. Held at the 23rd International Conference on Subterranean Biology in the Department of Biology at the University of Arkansas, 13-17 June 2016, Fayetteville, Arkansas.
Presentation by Dr. Jonathan J. Cole, Cary Institute of Ecosystem Studies
Starting in its earliest development, limnology has tended to view lakes as rather isolated from their terrestrial watersheds. This view of lakes as microcosms (Forbes 1887) proved useful in some ways, but it failed to help explain phenomena such as eutrophication which is driven by the external input of nutrients. While the study of limiting nutrients has fully embraced the watershed for decades, the study of C cycling in lakes has maintained a somewhat microcosm viewpoint. This is a viewpoint in which organic C is envisioned as being formed almost entirely by photosynthesis within the system (autochthonous sources); exogenous sources are largely ignored, downplayed, or assumed to be refractory. A number of disparate research threads in recent decades have completely overturned this view.
Assessment of the Plankton Biodiversity,Bay of Bengal, Cox's Bazar, BangladeshAbuMusa51
I am Abu Musa. This is my Internship Presentation. This is for partial fulfillment of the 4th-year final examination of the Department of Fisheries, University of Dhaka. This is based on my findings from one month of research on the Coxs Bazar coast. The research is done in the live feed lab of BFRI Cox's Bazar.
Effects of diflubenzuron on shrimp population dynamics: from lab experiments ...Jannicke Moe
The continued growth of marine aquaculture production has presented the industry with environmental and production concerns, of which the ectoparastic salmon lice (Lepeophtheirus salmonis) has gradually become a major problem. A commonly used pesticide against this crustacean is diflubenzuron (DFB), which acts as a chitin synthesis inhibitor and thereby interfere with the moulting stages during sea lice development. However, DFB from medicine feed may also affect non-target crustaceans such as the Northern shrimp (Pandalus borealis), which is an economically and ecologically important species in Norwegian fjords. Laboratory experiments have demonstrated that shrimp exposed to DFB through fish feed have reduced survival (ca. 60%) compared to control, in both the larval and the adult stages. Moreover, the effects of DFB exposure is more severe under future climate conditions (higher temperature). The aim of this study is to make the information on these mechanistic effects more relevant for risk assessment at the population level. We have developed an age-structured population model representing a Northern shrimp population located in a hypothetical Norwegian fjord containing a fish farm, under both ambient and future climates. Our model is based on thorough knowledge of shrimp biology and clear results on toxicological effects from the laboratory experiments. Nevertheless, extrapolating the individual-level effects to the population level poses several challenges. Relevant information on shrimp populations in fjords is sparse (such as abundances, survival and reproductive rates, and density-dependent processes). The degree of exposure to medicine feed at different distances from aquaculture farms is also uncertain. We have therefore developed a set model scenarios representing different medicine application schemes and different degrees of exposure for the shrimp populations. The purpose of the model is to predict effects of DFB exposure on population-level endpoints such as long-term abundance and age structure, and to assess the risk of population decline below threshold abundances.
Rising ocean temperatures, interfering with kelp reproduction, development and growth, have already devastating effects on natural kelp forests that have vanished in multiple regions after extreme summer heat waves. Moreover, increasing temperatures are likely to decrease biomass production and, thus, to reduce production security of farmed kelp. For
the kelp Alaria esculenta it has been shown that lethal thermal lmits of gametophytes, and the overall growth of sporophytes can be enhanced via thermal acclimation/priming. The
main objective of our study was to identify the importance of the methylome of the kelp Saccharina latissima for temperature acclimation. Methylation marks have been shown to be partly stable across generations, and, thus, are good epigenetic candidates in providing long-term acclimation to environmental challenges. While the first methylome of brown macroalgae has been recently described in Saccharina japonica, its functional relevance and contribution to environmental acclimation is currently unknown. We characterized the methylome in sporophyte cultures of S. latissima from Germany and Norway
(Labsamples), raised at 5°C, 10°C, and 15°C, and in adult ‘wild’ sporophytes from the same locations (Fieldsamples) using a methylation-sensitive restriction enzyme followed by Next Generation Sequencing of the digested fragments. Based on a Principal Component Analysis, the samples separated into distinct Lab- and Field-clusters, independent of their origin or treatment. This suggests that laboratory conditions have
strong effects on the methylome and, thus, putatively, on the epigenetically controlled characteristics of the kelp sporophytes. Methylation levels increased with increasing temperature. A more detailed analysis on the genomic regions affected by methylome the different methylome patterns will reveal potential functional consequences at the level of gene-regulation. This is a first step to understand whether DNA methylation marks may be used as biological regulators (via their effect on gene regulation) that allow to enhance production security and kelp restoration success under rising temperatures.
Nutraceutical market, scope and growth: Herbal drug technologyLokesh Patil
As consumer awareness of health and wellness rises, the nutraceutical market—which includes goods like functional meals, drinks, and dietary supplements that provide health advantages beyond basic nutrition—is growing significantly. As healthcare expenses rise, the population ages, and people want natural and preventative health solutions more and more, this industry is increasing quickly. Further driving market expansion are product formulation innovations and the use of cutting-edge technology for customized nutrition. With its worldwide reach, the nutraceutical industry is expected to keep growing and provide significant chances for research and investment in a number of categories, including vitamins, minerals, probiotics, and herbal supplements.
Professional air quality monitoring systems provide immediate, on-site data for analysis, compliance, and decision-making.
Monitor common gases, weather parameters, particulates.
Toxic effects of heavy metals : Lead and Arsenicsanjana502982
Heavy metals are naturally occuring metallic chemical elements that have relatively high density, and are toxic at even low concentrations. All toxic metals are termed as heavy metals irrespective of their atomic mass and density, eg. arsenic, lead, mercury, cadmium, thallium, chromium, etc.
This presentation explores a brief idea about the structural and functional attributes of nucleotides, the structure and function of genetic materials along with the impact of UV rays and pH upon them.
Seminar of U.V. Spectroscopy by SAMIR PANDASAMIR PANDA
Spectroscopy is a branch of science dealing the study of interaction of electromagnetic radiation with matter.
Ultraviolet-visible spectroscopy refers to absorption spectroscopy or reflect spectroscopy in the UV-VIS spectral region.
Ultraviolet-visible spectroscopy is an analytical method that can measure the amount of light received by the analyte.
The ability to recreate computational results with minimal effort and actionable metrics provides a solid foundation for scientific research and software development. When people can replicate an analysis at the touch of a button using open-source software, open data, and methods to assess and compare proposals, it significantly eases verification of results, engagement with a diverse range of contributors, and progress. However, we have yet to fully achieve this; there are still many sociotechnical frictions.
Inspired by David Donoho's vision, this talk aims to revisit the three crucial pillars of frictionless reproducibility (data sharing, code sharing, and competitive challenges) with the perspective of deep software variability.
Our observation is that multiple layers — hardware, operating systems, third-party libraries, software versions, input data, compile-time options, and parameters — are subject to variability that exacerbates frictions but is also essential for achieving robust, generalizable results and fostering innovation. I will first review the literature, providing evidence of how the complex variability interactions across these layers affect qualitative and quantitative software properties, thereby complicating the reproduction and replication of scientific studies in various fields.
I will then present some software engineering and AI techniques that can support the strategic exploration of variability spaces. These include the use of abstractions and models (e.g., feature models), sampling strategies (e.g., uniform, random), cost-effective measurements (e.g., incremental build of software configurations), and dimensionality reduction methods (e.g., transfer learning, feature selection, software debloating).
I will finally argue that deep variability is both the problem and solution of frictionless reproducibility, calling the software science community to develop new methods and tools to manage variability and foster reproducibility in software systems.
Exposé invité Journées Nationales du GDR GPL 2024
Salas, V. (2024) "John of St. Thomas (Poinsot) on the Science of Sacred Theol...Studia Poinsotiana
I Introduction
II Subalternation and Theology
III Theology and Dogmatic Declarations
IV The Mixed Principles of Theology
V Virtual Revelation: The Unity of Theology
VI Theology as a Natural Science
VII Theology’s Certitude
VIII Conclusion
Notes
Bibliography
All the contents are fully attributable to the author, Doctor Victor Salas. Should you wish to get this text republished, get in touch with the author or the editorial committee of the Studia Poinsotiana. Insofar as possible, we will be happy to broker your contact.
Salas, V. (2024) "John of St. Thomas (Poinsot) on the Science of Sacred Theol...
Population dynamics of the periwinkle Littorina littorea (Linnaeus, 1758) in the East Frisian Wadden Sea
1. Introduction
Objectives
Methods
Results
Conclusions
Population dynamics of the periwinkle Littorina
littorea (Linnaeus, 1758) in the East Frisian
Wadden Sea
Diplomarbeit
Alexander Jüterbock
Animal Biodiversity and Evolutionary Biology
Carl von Ossietzky University Oldenburg
Supervisors: Prof. Dr. Gabriele Gerlach, Dr. Thomas Friedl
April 13, 2010
Alexander Jüterbock Population dynamics of the periwinkle
50. Introduction
Objectives
Methods
Results
Conclusions
Larval Recruitment
Population Preference
Shell Morphology
Population Genetics
Populations Differ Morphologically
Shell morphology differs
between . . .
Woods Hole – EFWS
North coasts – South
coasts
North coasts
South coasts
Borkum
Norderney
Langeoog
Wangerooge
Wilks’ Lambda = 0.802, p < 0.001 ***
Alexander Jüterbock Population dynamics of the periwinkle
51. Introduction
Objectives
Methods
Results
Conclusions
Larval Recruitment
Population Preference
Shell Morphology
Population Genetics
Populations Differ Morphologically
Shell morphology differs
between . . .
Woods Hole – EFWS
North coasts – South
coasts
North coasts
South coasts
Borkum
Norderney
Langeoog
Wangerooge
Wilks’ Lambda = 0.135, p < 0.001 ***
Alexander Jüterbock Population dynamics of the periwinkle
52. Introduction
Objectives
Methods
Results
Conclusions
Larval Recruitment
Population Preference
Shell Morphology
Population Genetics
Populations Differ Morphologically
Shell morphology differs
between . . .
Woods Hole – EFWS
North coasts – South
coasts
North coasts
South coasts
Borkum
Norderney
Langeoog
Wangerooge
Wilks’ Lambda = 0.731, p < 0.001 ***
Alexander Jüterbock Population dynamics of the periwinkle
69. Appendix
Further Reading
Introduction
Methods
Results
For Further Reading I
Reid, D.G. (1996)
Systematics and Evolution of Littorina.
The Ray Society, London.
Cowen, R.K. & Sponaugle, S. (2009)
Larval dispersal and marine population connectivity
Annual Review of Marine Science 1:443–466.
Alexander Jüterbock Population dynamics of the periwinkle
70. Appendix
Further Reading
Introduction
Methods
Results
For Further Reading II
Staneva, J.; Stanev, E.V.; Wolff, J.-O.; Badewien, T.H.;
Reuter, R.; Flemming, B.; Bartholomä, A. & Bolding, K.
(2009)
Hydrodynamics and sediment dynamics in the German
Bight. A focus on observations and numerical modelling in
the East Frisian Wadden Sea.
Continental Shelf Research 29(1):302–319.
Jost, L. (2008)
Gst and its relatives do not measure differentiation.
Molecular Ecology 17(18):4015–4026.
Alexander Jüterbock Population dynamics of the periwinkle
71. Appendix
Further Reading
Introduction
Methods
Results
Residual Current in the German Bight
55.4N
55.2N
55.0N
54.8N
54.6N
54.4N
54.2N
54.0N
53.8N
53.6N
53.4N
6.3E
6.6E
6.9E
7.2E
7.5E
7.8E
8.1E
8.4E
8.7E
9.0E
(m/s)
0.16
0.14
0.12
0.10
0.08
0.06
0.04
0.02
0.25
(Staneva et al., 2009)
Alexander Jüterbock Population dynamics of the periwinkle
73. Appendix
Further Reading
Introduction
Methods
Results
The Periwinkle’s Life Cycle Includes a Planktotrophic
Larva
a b| ~
(Fretter and Graham, 1962)
(Fretter and Graham, 1962)
(Reid, 1996)
5–6 days
4–7 weeks
12–18 months
1–12 hours
after fertilization
Alexander Jüterbock Population dynamics of the periwinkle
75. Appendix
Further Reading
Introduction
Methods
Results
The Periwinkle’s Life Cycle Includes a Planktotrophic
Larva
a b| ~
(Fretter and Graham, 1962)
(Fretter and Graham, 1962)
(Reid, 1996)
5–6 days
4–7 weeks
12–18 months
1–12 hours
after fertilization
Alexander Jüterbock Population dynamics of the periwinkle
84. Appendix
Further Reading
Introduction
Methods
Results
Detailed Analysis of Aggregation experiments
10 cm
60 cm60 cm
1
2
3
4
5
Are certain types of
conspecifics preferred?
Snails of the same
population
Snails of the same sex
Snails of the same size
Alexander Jüterbock Population dynamics of the periwinkle
85. Appendix
Further Reading
Introduction
Methods
Results
Detailed Analysis of Aggregation experiments
10 cm
60 cm60 cm
1
2
3
4
5
Individual from population 1
Individual from population 2
- PPI -
Are certain types of
conspecifics preferred?
Snails of the same
population
Snails of the same sex
Snails of the same size
Alexander Jüterbock Population dynamics of the periwinkle
86. Appendix
Further Reading
Introduction
Methods
Results
Detailed Analysis of Aggregation experiments
10 cm
60 cm60 cm
|||
|
|
1
|
||
2
|
|
3
~~
~ 4
~~~
~
5
~
~
- Sex-PI -
Are certain types of
conspecifics preferred?
Snails of the same
population
Snails of the same sex
Snails of the same size
Alexander Jüterbock Population dynamics of the periwinkle
87. Appendix
Further Reading
Introduction
Methods
Results
Detailed Analysis of Aggregation experiments
10 cm
60 cm60 cm
1
2
3
4
5
- Size-PI -
Are certain types of
conspecifics preferred?
Snails of the same
population
Snails of the same sex
Snails of the same size
Alexander Jüterbock Population dynamics of the periwinkle
88. Appendix
Further Reading
Introduction
Methods
Results
Detailed Analysis of Aggregation experiments
10 cm
60 cm60 cm
1
2
3
4
5
PPI and Size-PI, both high
Are certain types of
conspecifics preferred?
Snails of the same
population
Snails of the same sex
Snails of the same size
Alexander Jüterbock Population dynamics of the periwinkle
98. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =0.263
Ambiguous
p =1.0 var =0.000
Alexander Jüterbock Population dynamics of the periwinkle
99. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =0.263
Ambiguous
p =1.0 var =0.000
Alexander Jüterbock Population dynamics of the periwinkle
100. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index
Population mixture
p =0.5 PPI =0.000
Real population preference
p =0.5 PPI =0.263
Ambiguous
p =1.0 PPI =0.000
Alexander Jüterbock Population dynamics of the periwinkle
102. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =
5
10 ∗10+ 5
10 ∗10
20
var =
Real population preference
p = var =
Ambiguous
p = var =
Alexander Jüterbock Population dynamics of the periwinkle
103. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =
( 5
10 −0.5)2∗10+( 5
10 −0.5)2∗10
19
Real population preference
p = var =
Ambiguous
p = var =
Alexander Jüterbock Population dynamics of the periwinkle
105. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =0.000
Real population preference
p =
10
10 ∗10+ 0
10 ∗10
20
var =
Ambiguous
p = var =
Alexander Jüterbock Population dynamics of the periwinkle
106. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =
( 10
10 −0.5)2∗10+( 0
10 −0.5)2∗10
19
Ambiguous
p = var =
Alexander Jüterbock Population dynamics of the periwinkle
107. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =0.263
Ambiguous
p = var =
Alexander Jüterbock Population dynamics of the periwinkle
108. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =0.263
Ambiguous
p =
10
10 ∗10
10
var =
Alexander Jüterbock Population dynamics of the periwinkle
109. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =0.263
Ambiguous
p =1.0 var =
( 10
10 −1)2∗10
9
Alexander Jüterbock Population dynamics of the periwinkle
110. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =0.263
Ambiguous
p =1.0 var =0.000
Alexander Jüterbock Population dynamics of the periwinkle
111. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 var =0.000
Real population preference
p =0.5 var =0.263
Ambiguous
p =1.0 var =0.000
Alexander Jüterbock Population dynamics of the periwinkle
112. Appendix
Further Reading
Introduction
Methods
Results
Defining the Population Preference Index in Detail
Population mixture
p =0.5 PPI =0.000
Real population preference
p =0.5 PPI =0.263
Ambiguous
p =1.0 PPI =0.000
Alexander Jüterbock Population dynamics of the periwinkle
113. Appendix
Further Reading
Introduction
Methods
Results
Snails Aggregate Assortatively
Borkum
Norderney
Langeoog
Wangerooge
B1 B2 N3 N1 N2 L1 W1 W2 WH
B1
B2
N3
N1
N2
L1
W1
W2
****
·
**
·
·
· **
Population preference
significance
Size preference
significance
· p ≤ 0.10,* p ≤ 0.05, ** p ≤ 0.01,*** p ≤ 0.001
Alexander Jüterbock Population dynamics of the periwinkle
119. Appendix
Further Reading
Introduction
Methods
Results
Simplified Monte Carlo Simulation
10 cm
60 cm60 cm
1
2
3
4
5
A histogram of PPI values
Mean PPI
Frequency
0.00 0.02 0.04 0.06 0.08 0.10
0
20
40
60
80
100100
80
60
40
20
0
Frequency
0.00 0.02 0.04 0.06 0.08 0.10
Mean PPI
Critical value
90% < 0.068
significantnot significant
Alexander Jüterbock Population dynamics of the periwinkle
129. Appendix
Further Reading
Introduction
Methods
Results
Detailed Monte Carlo Simulation
10 cm
60 cm60 cm
|
~|
~
~ 1
|~|
2
|
| 3
~|~
4
~~
|
~5
|~
|
A histogram of PPI values
Mean PPI
Frequency
0.00 0.02 0.04 0.06 0.08 0.10
0
20
40
60
80
100100
80
60
40
20
0
Frequency
0.00 0.02 0.04 0.06 0.08 0.10
Mean PPI
Critical value
90% < 0.068
significantnot significant
Alexander Jüterbock Population dynamics of the periwinkle
154. Appendix
Further Reading
Introduction
Methods
Results
Allometric correction
−3 −2 −1 0 1 2 3
−3
−2
−1
0
1
2
3
log10(x) = log10(shell length (cm))
log10(y)=log10(shellwidth(cm))
spread of x
x mean of x
log(x)
Correction
log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗log(x)
Alexander Jüterbock Population dynamics of the periwinkle
155. Appendix
Further Reading
Introduction
Methods
Results
Allometric correction
−3 −2 −1 0 1 2 3
−3
−2
−1
0
1
2
3
log10(x) = log10(shell length (cm))
log10(y)=log10(shellwidth(cm))
spread of x
x mean of x
log(x)
Correction
log(a) = log(y)−b∗(log(x)−log(x))log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗log(x)
Alexander Jüterbock Population dynamics of the periwinkle
156. Appendix
Further Reading
Introduction
Methods
Results
Allometric correction
−3 −2 −1 0 1 2 3
−3
−2
−1
0
1
2
3
log10(x) = log10(shell length (cm))
log10(y)=log10(shellwidth(cm))
spread of x
x mean of x
log(x)
Correction
log(a) = log(y)−b∗(log(x)−log(x))log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗log(x)
Alexander Jüterbock Population dynamics of the periwinkle
157. Appendix
Further Reading
Introduction
Methods
Results
Allometric correction
−3 −2 −1 0 1 2 3
−3
−2
−1
0
1
2
3
log10(x) = log10(shell length (cm))
log10(y)=log10(shellwidth(cm))
spread of x
x mean of x
log(x)
Correction
log(a) = log(y)−b∗(log(x)−log(x))log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗log(x)
Alexander Jüterbock Population dynamics of the periwinkle
158. Appendix
Further Reading
Introduction
Methods
Results
Allometric correction
−3 −2 −1 0 1 2 3
−3
−2
−1
0
1
2
3
log10(x) = log10(shell length (cm))
log10(y)=log10(shellwidth(cm))
spread of x
x mean of x
log(x)
Correction
log(a) = log(y)−b∗(log(x)−log(x))log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗(log(x)−log(x))
log(a) = log(y)−b∗log(x)
Alexander Jüterbock Population dynamics of the periwinkle
182. Appendix
Further Reading
Introduction
Methods
Results
Snails Prefer Conspecifics of the own Population
Population-wise aggregation
PPI significant (p ≤ 0.1) in 6 of 17 tests
Sex-bias aggregation
~~~~~
~
~~~~ ||
||
|||||
| Sex-PI significant (p ≤ 0.1) in 0 of 17 tests
Size-wise aggregation
Size-PI significant (p ≤ 0.1) in 2 of 17 tests
Alexander Jüterbock Population dynamics of the periwinkle
183. Appendix
Further Reading
Introduction
Methods
Results
Snails Prefer Conspecifics of the own Population
Population-wise aggregation
PPI significant (p ≤ 0.1) in 6 of 17 tests
Sex-bias aggregation
~~~~~
~
~~~~ ||
||
|||||
| Sex-PI significant (p ≤ 0.1) in 0 of 17 tests
Size-wise aggregation
Size-PI significant (p ≤ 0.1) in 2 of 17 tests
Alexander Jüterbock Population dynamics of the periwinkle
184. Appendix
Further Reading
Introduction
Methods
Results
Snails Prefer Conspecifics of the own Population
Population-wise aggregation
PPI significant (p ≤ 0.1) in 6 of 17 tests
Sex-bias aggregation
~~~~~
~
~~~~ ||
||
|||||
| Sex-PI significant (p ≤ 0.1) in 0 of 17 tests
Size-wise aggregation
Size-PI significant (p ≤ 0.1) in 2 of 17 tests
Alexander Jüterbock Population dynamics of the periwinkle
187. Appendix
Further Reading
Introduction
Methods
Results
Snails do not Prefer any Volatile ChemicalsPreference(%)
−0.6
−0.4
−0.2
0.0
0.2
0.4
0.6
B2
−
L1L1
−
B2B2
−
N
1N
1
−
B2N
1
−
L1L1
−
N
1N
2
−
N
3N
3
−
N
2W
1
−
B2B2
−
W
1W
1
−
L1L1
−
W
1W
1
−
N
1N
1
−
W
1W
2
−
N
2N
2
−
W
2
W
H
−
B2.2
B2.2
−
W
H
N
1m
a
−
N
1fe
N
1fe
−
N
1m
a
B1u
−
B1m
B1m
−
B1uN
1
−
Sw
0.93 0.32 0.54 0.47 0.59 0.62 1 0.22 0.12 0.19 0.81 0.58 0.91 1 0.99 0.22 1 0.43 0.19 0.76 0.52 0.1 0.59
own
other
.
0.6
0.4
0.2
0.0
-0.2
-0.4
-0.6
Preference(%)
ownother
B2–L1L1–B2B2–N
1N
1–B2N
1–L1L1–N
1N
2–N
3N
3–N
2W
1–B2B2–W
1W
1–L1L1–W
1W
1–N
1N
1-W
1W
2–N
2N
2–W
2
W
H
–B2.2
B2.2–W
H
N
1m
a–N
1fe
N
1fe–N
1m
aB1u–B1tB1t–B1uN
1–Sw
Alexander Jüterbock Population dynamics of the periwinkle
188. Appendix
Further Reading
Introduction
Methods
Results
Snails do not Prefer any Volatile ChemicalsPreference(%)
−0.6
−0.4
−0.2
0.0
0.2
0.4
0.6
B2
−
L1L1
−
B2B2
−
N
1N
1
−
B2N
1
−
L1L1
−
N
1N
2
−
N
3N
3
−
N
2W
1
−
B2B2
−
W
1W
1
−
L1L1
−
W
1W
1
−
N
1N
1
−
W
1W
2
−
N
2N
2
−
W
2
W
H
−
B2.2
B2.2
−
W
H
N
1m
a
−
N
1fe
N
1fe
−
N
1m
a
B1u
−
B1m
B1m
−
B1uN
1
−
Sw
0.93 0.32 0.54 0.47 0.59 0.62 1 0.22 0.12 0.19 0.81 0.58 0.91 1 0.99 0.22 1 0.43 0.19 0.76 0.52 0.1 0.59
own
other
.
0.6
0.4
0.2
0.0
-0.2
-0.4
-0.6
Preference(%)
ownother
B2–L1L1–B2B2–N
1N
1–B2N
1–L1L1–N
1N
2–N
3N
3–N
2W
1–B2B2–W
1W
1–L1L1–W
1W
1–N
1N
1-W
1W
2–N
2N
2–W
2
W
H
–B2.2
B2.2–W
H
N
1m
a–N
1fe
N
1fe–N
1m
aB1u–B1tB1t–B1uN
1–Sw
Population preference
Alexander Jüterbock Population dynamics of the periwinkle
189. Appendix
Further Reading
Introduction
Methods
Results
Snails do not Prefer any Volatile ChemicalsPreference(%)
−0.6
−0.4
−0.2
0.0
0.2
0.4
0.6
B2
−
L1L1
−
B2B2
−
N
1N
1
−
B2N
1
−
L1L1
−
N
1N
2
−
N
3N
3
−
N
2W
1
−
B2B2
−
W
1W
1
−
L1L1
−
W
1W
1
−
N
1N
1
−
W
1W
2
−
N
2N
2
−
W
2
W
H
−
B2.2
B2.2
−
W
H
N
1m
a
−
N
1fe
N
1fe
−
N
1m
a
B1u
−
B1m
B1m
−
B1uN
1
−
Sw
0.93 0.32 0.54 0.47 0.59 0.62 1 0.22 0.12 0.19 0.81 0.58 0.91 1 0.99 0.22 1 0.43 0.19 0.76 0.52 0.1 0.59
own
other
.
0.6
0.4
0.2
0.0
-0.2
-0.4
-0.6
Preference(%)
ownother
B2–L1L1–B2B2–N
1N
1–B2N
1–L1L1–N
1N
2–N
3N
3–N
2W
1–B2B2–W
1W
1–L1L1–W
1W
1–N
1N
1-W
1W
2–N
2N
2–W
2
W
H
–B2.2
B2.2–W
H
N
1m
a–N
1fe
N
1fe–N
1m
aB1u–B1tB1t–B1uN
1–Sw
Sex preference
Alexander Jüterbock Population dynamics of the periwinkle
190. Appendix
Further Reading
Introduction
Methods
Results
Snails do not Prefer any Volatile ChemicalsPreference(%)
−0.6
−0.4
−0.2
0.0
0.2
0.4
0.6
B2
−
L1L1
−
B2B2
−
N
1N
1
−
B2N
1
−
L1L1
−
N
1N
2
−
N
3N
3
−
N
2W
1
−
B2B2
−
W
1W
1
−
L1L1
−
W
1W
1
−
N
1N
1
−
W
1W
2
−
N
2N
2
−
W
2
W
H
−
B2.2
B2.2
−
W
H
N
1m
a
−
N
1fe
N
1fe
−
N
1m
a
B1u
−
B1m
B1m
−
B1uN
1
−
Sw
0.93 0.32 0.54 0.47 0.59 0.62 1 0.22 0.12 0.19 0.81 0.58 0.91 1 0.99 0.22 1 0.43 0.19 0.76 0.52 0.1 0.59
own
other
.
0.6
0.4
0.2
0.0
-0.2
-0.4
-0.6
Preference(%)
ownother
B2–L1L1–B2B2–N
1N
1–B2N
1–L1L1–N
1N
2–N
3N
3–N
2W
1–B2B2–W
1W
1–L1L1–W
1W
1–N
1N
1-W
1W
2–N
2N
2–W
2
W
H
–B2.2
B2.2–W
H
N
1m
a–N
1fe
N
1fe–N
1m
aB1u–B1tB1t–B1uN
1–Sw
Control for effect of
label color
Alexander Jüterbock Population dynamics of the periwinkle
191. Appendix
Further Reading
Introduction
Methods
Results
Snails do not Prefer any Volatile ChemicalsPreference(%)
−0.6
−0.4
−0.2
0.0
0.2
0.4
0.6
B2
−
L1L1
−
B2B2
−
N
1N
1
−
B2N
1
−
L1L1
−
N
1N
2
−
N
3N
3
−
N
2W
1
−
B2B2
−
W
1W
1
−
L1L1
−
W
1W
1
−
N
1N
1
−
W
1W
2
−
N
2N
2
−
W
2
W
H
−
B2.2
B2.2
−
W
H
N
1m
a
−
N
1fe
N
1fe
−
N
1m
a
B1u
−
B1m
B1m
−
B1uN
1
−
Sw
0.93 0.32 0.54 0.47 0.59 0.62 1 0.22 0.12 0.19 0.81 0.58 0.91 1 0.99 0.22 1 0.43 0.19 0.76 0.52 0.1 0.59
own
other
.
0.6
0.4
0.2
0.0
-0.2
-0.4
-0.6
Preference(%)
ownother
B2–L1L1–B2B2–N
1N
1–B2N
1–L1L1–N
1N
2–N
3N
3–N
2W
1–B2B2–W
1W
1–L1L1–W
1W
1–N
1N
1-W
1W
2–N
2N
2–W
2
W
H
–B2.2
B2.2–W
H
N
1m
a–N
1fe
N
1fe–N
1m
aB1u–B1tB1t–B1uN
1–Sw
Own population –
seawater
Alexander Jüterbock Population dynamics of the periwinkle
193. Appendix
Further Reading
Introduction
Methods
Results
Results of Discriminant analyzes
EFWS – Woods Hole
9
8
7
6
5
4
3
2
-2 -1 0 1 2 3 4 5 6 7
Canonical2
Canonical 1
-SP (Spire height)
NorthAmerica
Europe
Continent
North America
Europe
Wilks’ Lambda: 0.867
p < 0.001 ***
significant influence: SP
Alexander Jüterbock Population dynamics of the periwinkle
194. Appendix
Further Reading
Introduction
Methods
Results
Results of Discriminant analyzes
North coasts – South coasts
10
9
8
7
6
5
4
3
2
Canonical2
-7 -6 -5 -4 -3 -2 -1 0 1 2 3 4 5
Canonical 1
+CL (Columellar length)
-LA (Length of aperture
south
north
Side
north
south
Wilks’ Lambda: 0.802
p < 0.001 ***
significant influence: CL > LA
Alexander Jüterbock Population dynamics of the periwinkle
195. Appendix
Further Reading
Introduction
Methods
Results
Results of Discriminant analyzes
Within north coasts
12
11
10
9
8
7
6
5
4
3
Canonical2
-SP(Spireheight)
-CL(Columellarlength)
-7 -6 -5 -4 -3 -2 -1 0
Canonical 1
+SP (Spire height)
-CL (Columellar length)
Wangerooge
Borkum
Norderney
Place
Borkum
Wangerooge
Wilks’ Lambda: 0.135
p < 0.001 ***
significant influence: SP > CL
Norderney
Alexander Jüterbock Population dynamics of the periwinkle
196. Appendix
Further Reading
Introduction
Methods
Results
Results of Discriminant analyzes
Within south coasts
6
5
4
3
2
1
0
-1
-2
Canonical2
-CL(Columellarlength)
+SW(Shellwidth)
-LA(Lengthofaperture)
-SP(Spireheight)
7 8 9 10 11 12 13 14 15 16 17 18 19
Canonical 1
+CL (Spire height)
-SW (Shell width)
+LA (Length of aperture)
+SP (Spire height)
Norderney
Langeoog
Wangerooge
Borkum
Place
Borkum
Langeoog
Norderney
Wangerooge
Wilks’ Lambda: 0.731
p < 0.001 ***
significant influence: CL > SW > LA > SP
Alexander Jüterbock Population dynamics of the periwinkle
197. Appendix
Further Reading
Introduction
Methods
Results
Results of Discriminant analyzes
Sexes
4
3
2
1
0
-1
-2
-3
-4
-5
Canonical2
3 4 5 6 7 8 9 10 11 12
Canonical 1
male
female
Sex
male
female
Wilks’ Lambda: 0.985
p < 0.277
Alexander Jüterbock Population dynamics of the periwinkle
198. Appendix
Further Reading
Introduction
Methods
Results
Genetic (Dest) and Geographic (km) Distance
B2 W1 N2 WH
B2 . . . 0.011 -0.007 0.033 *
W1 82.5 . . . 0.006 0.056 **
N2 38.0 39.9 . . . 0.057 *
WH 5662.8 5730.7 5692.3 . . .
Alexander Jüterbock Population dynamics of the periwinkle
199. Appendix
Further Reading
Introduction
Methods
Results
Genetic (Dest) and Geographic (km) Distance
B2 W1 N2 WH
B2 . . . 0.011 -0.007 0.033 *
W1 82.5 . . . 0.006 0.056 **
N2 38.0 39.9 . . . 0.057 *
WH 5662.8 5730.7 5692.3 . . .
Borkum
Norderney
Langeoog
Wangerooge
Within the EFWS
Alexander Jüterbock Population dynamics of the periwinkle
200. Appendix
Further Reading
Introduction
Methods
Results
Genetic (Dest) and Geographic (km) Distance
B2 W1 N2 WH
B2 . . . 0.011 -0.007 0.033 *
W1 82.5 . . . 0.006 0.056 **
N2 38.0 39.9 . . . 0.057 *
WH 5662.8 5730.7 5692.3 . . .
Woods Hole
EFWS
Between the EFWS and Woods Hole
Alexander Jüterbock Population dynamics of the periwinkle