<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">AS</journal-id><journal-title-group><journal-title>Agricultural Sciences</journal-title></journal-title-group><issn pub-type="epub">2156-8553</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/as.2013.48057</article-id><article-id pub-id-type="publisher-id">AS-35705</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject><subject> Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Desirability of a standard notation for fisheries assessment
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>ergio</surname><given-names>Ragonese</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Sergio</surname><given-names>Vitale</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Institute for Coastal Marine Environment—IAMC, Italian National Research Council—CNR, Mazara del Vallo, Italy;</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>sergio.vitale@cnr.it(SV)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>23</day><month>07</month><year>2013</year></pub-date><volume>04</volume><issue>08</issue><fpage>399</fpage><lpage>432</lpage><history><date date-type="received"><day>26</day>	<month>April</month>	<year>2013</year></date><date date-type="rev-recd"><day>27</day>	<month>May</month>	<year>2013</year>	</date><date date-type="accepted"><day>15</day>	<month>June</month>	<year>2013</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
   The worldwide increase of the publications concerning the assessment of marine renewable living resources is highlighting long-standing problems with symbols and annotations. Starting from the symbols presented within the classic fisheries masterpieces produced, mainly in the fifty of the last century, a first “Milestone” list was organised. Thereafter, the pertinent literature was (not exhaustively) browsed in order to integrate this Milestone list on the base of a set of decisional criteria. The present contribution consists in using the Latin letters as well established symbols for the corresponding parameters, leaving free to specific use (with few historical exceptions) the Greek letters in view to open a discussion among all the fisheries scientists and bodies in order to move towards a common language and better communication standards. 
 
</p></abstract><kwd-group><kwd>Fisheries; Assessment; Symbols; Standard</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. INTRODUCTION</title><p>The intuition to separate out the effects of births, deaths and growth on fish populations in order to estimate the surplus production of an exploitable stock has been developed since the first decades of the twentieth century [1-4]. The origin of fisheries science, as an integrated and structured discipline, however, might be generally placed at the second half of fifties and first half of sixty, when the milestones of Beverton and Holt [5-7], Gulland [8-11], and Ricker [12,13] were published. At that time, the main goals of such discipline were assessing and managing the living renewable aquatic resources under a theoretical based exploitation pattern. Just little after the Beverton and Holt and Ricker works, it was evident the opportunity to be clear about the definition of physical quantities and naming conventions came [14- 16]. Almost half a century later, notwithstanding the growing importance of assessments to promote credible and effective rebuilding or managing plans for the highly depleted fishable resources in the world, on our knowledge no general agreement exists about a proper and unambiguous annotations and symbols. That notwithstanding a big effort has been realised regarding the definitions [17-23]. In the present contribution, which recalls the Holt’s heading of a section in one of his reports presented at the Biarritz symposium in 1956, the most common pitfall, ambiguities and lack of consistency arising from the literature in the field were analysed and a scheme of symbols usage was proposed in order to encourage fisheries scientists and bodies to move towards the establishment of a common language and better communication standards in assessments terminology.</p></sec><sec id="s2"><title>2. MATERIAL AND METHODS</title><sec id="s2_1"><title>2.1. Organising the Symbols Lists</title><p>The pertinent fisheries literature was browsed to highlight the different symbols uses and attributions within a “classic” definition of assessment. In fact, it is worth noting that different assessment interpretations can be found in both grey [<xref ref-type="bibr" rid="scirp.35705-ref24">24</xref>] and “official” publications [25,26] according to a more or less broad application of the word. In particular, within the “broader” interpretations can be quoted 1) the part of fisheries science that studies the status of a fish stock as well as the possible outcomes of different management alternatives; it tells us if the abundance of a stock is below or above a given target point and by doing so lets us know whether the stock is overexploited or not; it also tells us if a catch level will maintain or change the abundance of the stock [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>]; and 2) the application of statistical and mathematical tools to relevant data in order to obtain a quantitative understanding of the status of the stock as needed to make quantitative predictions of the stocks reactions to alternative future regimes [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>].</p><p>On the contrary, the goals of the classic and narrower assessment definitions can be identified in a) for any given fish populations 1) what are the present quantities that will be available for capture in one or more years and what factors are determining the quantity of the fish and how are they changing [<xref ref-type="bibr" rid="scirp.35705-ref28">28</xref>]; 2) providing a means of expressing population properties by a relatively few parameters [<xref ref-type="bibr" rid="scirp.35705-ref26">26</xref>] and of codifying the effects of fishing on stocks [<xref ref-type="bibr" rid="scirp.35705-ref29">29</xref>]; 3) using stock demographic parameters to determine the total catch and how the catch and the catch per unit of effort varies with changes in the pattern of fishing [<xref ref-type="bibr" rid="scirp.35705-ref30">30</xref>]; and 4) the study of population structure, dynamics, and past exploitation of a single population [<xref ref-type="bibr" rid="scirp.35705-ref31">31</xref>] and its reaction to the dominant influence of fishing pressure [<xref ref-type="bibr" rid="scirp.35705-ref32">32</xref>].</p><p>Considering the classic definitions, the first step consisted in establishing a “Milestone” list with the historical symbols on the base of the fisheries science masterpieces produced in the fifties and sixties, and integrated with the successive contributes of the same Authors. In particular, the following contributes were consulted: Beverton [<xref ref-type="bibr" rid="scirp.35705-ref33">33</xref>], Beverton and Holt [5-7], Beverton and Parrish [<xref ref-type="bibr" rid="scirp.35705-ref34">34</xref>], Holt [15,35-37], Holt et al. [<xref ref-type="bibr" rid="scirp.35705-ref16">16</xref>], Gulland [8-11,14,24,30,38-45], Gulland and Holt [<xref ref-type="bibr" rid="scirp.35705-ref46">46</xref>], ICNAF [29,47-50], Kesteven and Holt [<xref ref-type="bibr" rid="scirp.35705-ref51">51</xref>], Ricker [12,13,52-58], and Ricker and Foerster [<xref ref-type="bibr" rid="scirp.35705-ref59">59</xref>]. For convenience, these Authors were abbreviated within the Milestone list as BH (Beverton, Holt and Beverton and Holt); I (ICNAF reports), G (Gulland) and R (Ricker).</p><p>Hence, the literature (both official and grey), books, manuals and programmes dealing with fisheries assessments were (not exhaustively) consulted in order to compare and integrate the basic scheme previously established. The final step was proposing a standard set of symbols, preferably (or whenever possible) according to the following Decalogue of criteria and conventions [14-16]. In particular, the symbols:</p><p>1) should be referred to the most relevant and studies items in “classic” fishery assessment;</p><p>2) should have a unique correspondence for each quantity, at least in base of their position (prefix, suffix, subscripts, superscript);</p><p>3) should be found within a standard commonly and easily available (in the specific case, the symbols lists in word Microsoft) avoiding other difficult, already existing, to find symbols [<xref ref-type="bibr" rid="scirp.35705-ref60">60</xref>];</p><p>4) should avoid special characters, such as the circumflex accent or the “ ” symbol, which was employed for example by Gulland [11,30] with the meaning of “therefore” or “consequently” [60; page 415];</p><p>5) should be different from those symbols traditionally well established in other related discipline (such as statistics);</p><p>6) in the masterpieces proposals or traditionally established should be maintained;</p><p>7) should consist of one to three “components” (never more than four letters), considering that in many instances many subscripts could be necessary [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>];</p><p>8) should represent the initial words of the considered variable;</p><p>9) should help in expressing the relevant formula in a simple and compact form, which is easy to write, type and print;</p><p>10) similar should indicate similar measures.</p><p>In both Milestone and proposed list, the symbol &#167; and &#167;&#167; denote some remarks relative to the proposed symbol definition and alternative meanings of the same symbols, respectively. At the beginning of the proposed list, the X symbol was employed to represent some generalisations. Finally, the following abbreviations were adopted: coef. for coefficient, cons. for constant, n˚ for number, par. for parameter, prop. for proportion, and VBGF for von Bertalanffy Growth Function.</p></sec><sec id="s2_2"><title>2.2. The “Milestone” List</title><p>a—BH_ Coef. of linear equations relating growth to density; unit haul swept area; intersect in regression line; const.; time interval (for example, in length increment— average length regression); average (strictly speaking) median length in Tauti’s expression. G_ Probability (in age estimation); slope in the linear density dependence regression between asymptotic length and abundance; coef.; hook catch probability; area or volume under the influence of a gear; prop. of full fishing mortality rate; age at recruitment; proportionality coef. (usually 0.5) among yield, natural mortality and stock biomass (Y = aMB) in potential yield computation. I_ Mesh size. R_ Annual (or seasonal) total mortality rate; annual expectation; actual mortality; the first (multiplier) coef. in the (individual) length-weight functional relationship; coef. in Ricker’s recruitment curve (when stock size and recruitment are in the same units); competition coef.; intercept in regression; sex ratio as males over females; Brody’s coef.; intercept in yield per effort against effort; initial size; cons.</p><p>α (alfa)—BH_ Derived coef. of pre recruited mortality in the eggs-recruitment relationship; angle definition; cons. G_ Vulnerability; proportionality coef. R_ Par. in the Ricker (dimensionless) and Beverton and Holt R/S curves.</p><p>A—BH_ The area occupied by the fish population; Russell’s recruitment. G_ Sum of squares; coef. in ageing error; area of fished region; Russell’s recruitment; (Heincke’s) annual death rate; cons. in stock recruitment curves. I_ Fish breadth/fish depth ratio. R_ Average population in successive years; annual (also Heincke) or seasonal mortality rate; A' annual or seasonal rate of disappearance of fish; maturity categories n˚ in Murphy’s method; par. in other growth model than VBGF; par. in the Beverton and Holt R/S curve when S and R are in the same units; A<sub>0.95</sub> upper age limit according to Taylor’s approximation [<xref ref-type="bibr" rid="scirp.35705-ref62">62</xref>].</p><p>b—BH_ Selection factor; ratio of length at 50% point of selection ogive (or mean selection length) to mesh size; coef. of linear equations relating growth to density; Huxley’s coef. in fish length-weight relationship (w = bl<sup>k</sup>); coef. (scale factor) in the Richards curve; coef. in length increment—average length regression; oldest age in Tauti’s expression. G_ Probability (in age estimation); generic coef.; selection factor; density dependence in recruitment; generic slope in linear regression; b<sub>n</sub> expanding term in the analytical computation. R_ The exponent in the allometric (b ≠ 3) and isometric (b = 3) length-weight (individual) relationship; the slope of any line; proportionality coef. in recruits parental relationships; Brody’s coef.; annual catch in Baranov’s food biomass relationship; intercept in yield-effort (Y/f) against f; cons.</p><p>β (beta)—BH_ Derived coef. of pre recruited mortality in the eggs-recruitment relationship; cons. R_ N˚ of marked fish; incomplete beta function; par. in the Ricker and Beverton and Holt R/S curves.</p><p>B—G_ Stock biomass (size in weight); sum of squares; coef. in ageing error; biomass, B' in exploited phase; B<sub>∞</sub> at maximum population (carrying capacity); B<sub>P</sub> predators; cons. in stock recruitment curves. I_ Mesh length/mesh width ratio. R_ N˚ of natural death; biomass of a group of fish or an entire stock; maturity categories n˚ in Murphy’s method; par. in other growth model than VBGF; prop. of new recruits in the catch (Allen’s method); B<sub>∞</sub> and B<sub>S</sub> maximum stock size (the environment will support) and “optimum” stock size corresponding to maximum Y at equilibrium in Graham surplus production curve.</p><p>c—BH_ Cons. given by the ratio of fishing mortality and “effective overall fishing intensity” (effort); catch per net. G_ Cons.; c' proportionality coef. relating catch per unit of effort to density of fish (provided that the availability is cons.); reciprocal of vulnerability—aggregation product; coef.; ratio of length at capture and maximum length (in potential yield computations); mean selection or entry to the catch or first capture; Y/Y<sub>max</sub> ratio in marginal yield analysis; raising factor (from haul catch to stock size). I_ Capture related general par.; X<sub>c</sub> at first capture; first liable to capture by the fishing gear in use; t<sub>c</sub> age at entry to the exploited phase or first liability to capture; selection factor. R_ The catch up to any time; Widrig’s catchability; the fraction of the whole stock captured in a single unit of effort; Brody’s coef.; X<sub>c</sub> compensatory component in natural mortality; par. in growth models different from (or previous than) VBGF.</p><p>C—BH_ Catch in n˚; local density (concentration) of fish; C’ catch per effort. G_ Catch in n˚; sum of squares; total catch. C<sub>1</sub>…<sub>c</sub> species competing with target species; cons. in stock recruitment curves. I_ N˚ of fish in the catch (catch in n˚); head girth/head breadth ratio. R_ Cons. of integration; catch in n˚ (usually in 1 year); n˚ of fish examined for tags or marks; maturity categories n˚ in Murphy’s method; average minimum age limit of usable stock.</p><p>χ (chi)—BH_ Fecundity (/g) coef. G_ χ<sup>2 </sup>chi square statistic.</p><p>d—BH_ Average distance of fish in random movement. G_ Catch per unit of effort; sample catch; density of fish as derived in a given haul catch; mean depth. R_ Annual increase in length in Baranov’s Yield method; absolute increase in length.</p><p>D—BH_ Dispersion coef.; unconditional natural mortality rate; expectation of death by natural causes; average density of fish. G_ Density of fish on fishing grounds; n˚ dying of disease; cons. in stock recruitment curves. I_ Expectation of death by capture (unconditional natural mortality rate); expectation of death by natural causes. R_ Total deaths; maturity categories n˚ in Murphy’s method.</p><p>Δ (delta)—BH_ R_ Interval; variation; change. G_ One or unit operation.</p><p>e—G_ Sample effort. R_ Base of the natural (or Napierian) logarithms.</p><p>ε (epsilon)—BH_ Coef. of food utilisation for growth and maintenance; efficiency of utilization of food for growth. G_ Coef. in mortality estimation; random variable in fishing effort analysis.</p><p>η (eta)—BH_ Suffix denoting reference to spawning or (first) maturity; marked change in growth; cons. in the differential Richards.</p><p>E—BH_ G_ I_ R_ Exploitation rate [F/Z(1 − exp<sup>−</sup><sup>Z</sup>)]. BH_ Egg production; X<sub>E</sub> equilibrium; coef. of anabolism; unconditional fishing mortality rate; expectation of death by capture; par. in the differential length based VBGF; Taylor’s KL<sub>∞</sub> product. G_ X<sub>E</sub> expected value; probability of ultimate capture (often exploitation ratio in steady state condition). I_ Unconditional fishing mortality rate; expectation of death by capture. R_ Escapement; (absolute) n˚ of eggs; X<sub>E</sub> equilibrium (steady state); cumulative fishing effort.</p><p>E.F.—I_ Escape factor as length/mesh size.</p><p>f—BH_ Fishing activity; effort; intensity; power; overall; weighed mean fishing effort per unit area. G_ Fishing intensity; fishing effort (in some suitable units); f' adjusted; f(X) function. I_ “Japanese” mortality rate; effective overall fishing intensity. R_ Fishing effort (n˚ of units of gear in use); Widrig’s effective fishing effort adjusted, when necessary; f<sub>S</sub> corresponding to MSY (optimum f).</p><p>♀—R_ Females (reproducing the Petersen 1892 table). I_ ♀♀.</p><p>φ (phi)—BH_ Dummy (time) variable or general funcion.</p><p>ф (phi)—BH_ Dummy (time) variable or general function; ф' and ф'' function relating cost and revenues to F; ratio (generic).</p><p>Ф (phi)—BH_ Total n&#176; of age groups into which recruitment occurs.</p><p>F—BH_ G_ I_ R_ Instantaneous fishing mortality coef. BH_ 'F/K. G_ F<sub>1</sub>… F<sub>f</sub> species on which the target species feed. R_ Size of a progeny in the recruits parental relationships.</p><p>g—BH_ Grazing mortality coef. (individual); total fishing effort; fishing effort as recorded; standardized fishing effort. G_ Fishing effort; F/K ratio; rate of growth in short time interval. I_ Fishing effort as collected (uncorrected) or “crude”. R_ Instantaneous rate of growth in models different from VBGF.</p><p>γ (gamma)—BH_ Annual egg-production per recruit.</p><p>G—B_ Grazing mortality coef.; Russell’s population growth; standardized total fishing effort. G_ exponential growth rate; net (and long term) gain from a change in gear selectivity or area closure. I_ Girth factor; weight of a fish. R_ Instantaneous growth rate (general); Russell’s population growth.</p><p>G.F.—I_ Girth factor as fish length/max. girth; girth/length ratio.</p><p>Γ (gamma)—BH_ Index of competition (force of concurrence).</p><p>h—BH_ N˚ of hour fished; par. in the egg-production per recruit computation, h<sub>1</sub> and h<sub>2</sub> cons. in dependence growth on food. G_ Cons. in growth equation. I_ Degree of precision. R_ Annual (or seasonal) relative individual growth rate; weight increment/initial weight ratio; annual growth rate.</p><p>H—BH_ Coef. of synthesis in the differential VBGF; par. in M at age variation; par. in the egg-production per recruit computation.</p><p>i—G_ X<sub>i</sub> generic group identification. I_ X<sub>i </sub>year class. R_ Widrig’s instantaneous rate of (total) mortality of a stock; X<sub>th</sub> period; X<sub>i </sub>density-independent component of natural mortality.</p><p>I—BH_ Index of fishing intensity; par. in M at age variation.</p><p>j—BH_ Exponent related to maintenance requirements (usually 2/3). I_ Fishing intensity; X<sub>j </sub>age group. R_ X<sub>th</sub> period of recovering.</p><p>k—BH_ Coef. of catabolism in the differential VBGF; growth equation coef.; Huxley’s coef. in w = bl<sup>k</sup>; k<sub>2 </sub>and k<sub>0 </sub>Baranov’s fishing and natural mortality coef.; k<sub>1</sub> coef. in linear approximation to a selection ogive; coef. G_ Total n˚ of fish in unit weight; n˚ of strata; sub-areas proportionality coef.; coef. in the Ricker exponential and VBGF; slope in the linear density dependence regression between mortality and abundance; cons. in growth equations; average fecundity. R_ Factor of proportionality; growth coef. in model different than VBGF; Ford’s growth coef.; a rate used in various connections; instanttaneous rate of increase in Graham surplus production curve (V of Graham); instantaneous growth rate of a stock.</p><p>κ (cappa)—BH_ Cons. relating F to “destruction” mortality.</p><p>K—BH_ I_ One of the two main par. of the VBGF, proportional only to the catabolism coef. (hence, more sensible to temperature variation); par. expressing the relative rate of approach to asymptotic size; coef. Defining the sampling efficiency of a gear (in fish dispersion); X<sub>K</sub> an alternative gear to be compared. G_ Coef. Proportional to the rate at which the fish completes its growth; the rate at which the limiting length is reached in the VBGF; selection factor in gill-nets; a new gear. I_ Coef. in the allometric relationship W = KL<sup>n</sup>; head depth/head breadth ratio. R_ A rate used in various connections; rate of change in length increment in VBGF; Brody coef.; any rate; generic cumulative catch; integration cons.; n˚ of degree days; Ivlev’s growth efficiency coef.</p><p>l—BH_, I_, R_ Length. BH_ l' some arbitrary length above which all fish are considered recruited to the gear. G_ Length; mean n˚ per unit weight for a length group; l<sub>c</sub> at first capture; l<sub>d</sub> gill net deselection; l<sub>m</sub> gill net maximum efficiency; l<sub>p</sub> partial recruitment (discards); l<sub>r</sub> recruitment; l<sub>s</sub> minimum size.</p><p>λ (lambda)—BH_ Fishable life span; maximum age a fish can attain; end of (fishable) life span; the age above which older fish contribute to fisheries can be considered practically negligible (in most cases considered λ = ∞). G_ True mean n˚; true survival rate. R_ The last period (the greatest age) considered in which an appreciable catch is made; the end of life span or maximum age attained; Halliday’s (1972) “maximum age of significant contribute to fisheries”; λ<sub>1</sub> the probability of capture between competing species; difference between maximum and recruitment ages.</p><p>L—BH_ Length of individual fish (particular); loss rate of marks; L<sub>∞</sub> upper asymptote of length; X<sub>L</sub> age at which the fish do not appear in the catch (for different reasons). G_ Mean n˚ per unit weight for a length group; total life span in the fishery; L<sub>∞</sub> maximum length, especially in the VBGF; immediate losses after gear selectivity change or area closure. I_ Fishable life span; length. R_ (Mean) length at recruitment (in Baranov’s yield method); fork length.</p><p>Λ (lambda)—G_ Average n˚ of landed fish.</p><p>m—BH_ Apparent mortality coef.; m<sub>0</sub> and m<sub>1</sub> in linear regression; coef. in M at density; instantaneous mortality (in fish dispersion); slope coef. in regression line; exponent in the differential Richards; X<sub>m</sub> size at maturity. G_ Mesh size; average n˚ of fish; exponent in general production model; cons. in Richard’s growth curve; M/K ratio; haul catch. I_ Mesh size. R_ The fraction of the initial population which has been caught up to time t for which the term “fishing mortality” will be reserved; m<sub>1</sub> the fishing mortality up to the season end (also rate of exploitation); annual or seasonal/(fishing) mortality rate (if no other causes operate; Widrig’s m); conditional fishing mortality; sample size; variable exponent in Pella and Tomlinson surplus production curve; c<sub>m</sub> maximum recruitment; slope of the Richards curve at the inflexion.</p><p>♂—R_ Males (reproducing Petersen 1892 table). I_ ♂♂.</p><p>μ (mi)—BH_ Density independent and interaction components of mortality; μ<sub>1</sub> and μ<sub>2</sub> linear coef. in M at density. G_ Apparent survival rate. I_ Coef. defining the relationship between mesh size and fish girth. R_ (Annual) expectation of death by capture; rate of exploitation.</p><p>M—BH_ G_ I_ R_ Instantaneous natural mortality coef. BH_ M'; M/K; M<sub>1</sub> and M<sub>2</sub> density independent and dependent. G_ M' limiting value approached by biggest fish; apparent n˚ in a year class; X<sub>M</sub> maximum. I_ Mesh; mesh size. R_ M' n˚ of fish marked; mean abundance of predators; average age of first recruitment.</p><p>M.I.—I_ Mesh index.</p><p>n—BH_ N˚ of marked fish recaptured; generic n˚ of items. G_ Generic n˚ (ships, years, sampling days, hooks in a long-line); generic exponent in the VBGF in weight. I_ X<sub>n </sub>age group; exponent in the allometric relationship W = KL<sup>n</sup>. R_ Annual or seasonal (natural) mortality rate (if no other causes operate), Widrig’s n; conditional fishing mortality; sample size; exponent in growth related models (Richards, Ursin and growth—temperature models); any generic n˚.</p><p>υ (ni)—BH_ Nutritional factor. R_ (Annual) expectaion of natural death.</p><p>N—BH_ G_ R_ N˚ of fish in a homogeneous group (N<sub>X</sub> year class). BH_ Total n˚ in stock. G_ N˚ of fish measured; real n˚ in a year class; abundance; n˚ in the stock; sampling days; N<sub>R</sub> and N<sub>k</sub> released and retained after a change in gear selectivity. I_ Total n˚ of fish in the exploitable phase of the stock. R_ N˚ of fish in a year class or populations; N<sub>0</sub> at the beginning.</p><p>o—G_ Subscript denoting observed values.</p><p>ω (omega)—BH_ Average weight of individual food organisms during their “grazeable” life span.</p><p>O—G_ N˚ of fish dying of other causes than fishing.</p><p>Ω (omega)—BH_ Expanding term (summation cons.) in year class weight computation.</p><p>p—BH_ Standing crop; prop. of fish caught in unit haul swept area; probability of capture; fish of a given length present in the swept area; shape related coef. G_ Fraction; n˚ (or prop.) of fish (also retained) or items (hooks) of a given type; p<sub>i</sub> relative fishing power; X<sub>p</sub> production of plant; positive cons. in the incomplete Beta function. R_ Population at the start of the fishing season; Widrig’s instantaneous rate of fishing mortality; total mortality multiplied by the ratio of fishing deaths to all deaths; complement of catchability; par. in Allen’s recruitment method; generic coef. in regressions.</p><p>π (pi)—G_ Prop. in the whole sample.</p><p>P—BH_ Generic (mean) abundance or population size in weight (P<sub>W</sub>) or n˚ (P<sub>N</sub>); (annual) production; total weight in stock; P<sub>m</sub> fishing power; P<sub>l</sub> n˚ of fish of length l which is liable to capture by the gear. G_ Probability level; year period; population size; n˚ of fish dying from predation; P<sub>H</sub> production of herbivorous; P<sub>1</sub> … P<sub>p</sub> predators eating the target species; selective gill-net; fishing power; generic par. I_ Total weight (biomass) of fish in the exploitable phase of the stock; probability. R_ Size (n˚, weight, egg production etc) of parental stock; level of statistical probability; par. in Jones yield computation.</p><p>Π (pi)—BH_ Population size.</p><p>ψ (psi)—BH_ Dummy time variable.</p><p>Ψ (psi)—BH_ Dummy time variable; par. in M at age variation. I_ Girth related probability of escaping.</p><p>q—G_ I_ R_ Catchability coef. relating F to f. BH_ Weight-length coef. in W = ql<sup>3</sup>; prop. completion (q = 1 − p); fish of a given length retained in the cod-end; generic n˚ of years. G_ Availability. I_ The ratio between the best index of effective overall fishing intensity and the resulting instantaneous fishing mortality coef. R_ Widrig’s instantaneous rate of natural mortality; total mortality multiplied by the ratio of fishing deaths to all deaths; Baranov’s integration factor; generic coef. in regressions.</p><p>Q—BH_ Physiological-temperature coef.; expansion term; maintenance energy coef. (also per unit physiological surface); Q<sub>10</sub> physiological-temperature coef. (Arrhenius) rule. G_ Gross long term increase in catch following change in selectivity or area closure; prop.; coef. in non linear catch per unit effort—effort relationship. I_ Initial slope of the eumetric catch curve (Holt’s responsiveness of the stock); fishing intensity/fishing mortality ratio. R_ The yearly n˚ of fish which reaches the minimum reference age (X<sub>Q</sub>) used in yield computations; the cons. which appears in the integration of Baranov’s yield computation; par. in Jones yield computation; par. in Allen’s recruitment method.</p><p>r—BH_ Annual recruitment to a food population; r<sub>th</sub> period; amount of food consumed per unit time (unit ration); generic cons.; fish escaping from parts of the net other than the cod-end. G_ Replacement; radius (or influence) of a fishing gear; maximum rate of population growth; time intervals; prop. recruited to the gear; age at first capture. I_ X<sub>r</sub> at recruitment to fishable stock; t<sub>r</sub> age at entry to the exploitable phase. R_ The fraction of the population remaining at time t; Widrig’s availability fraction; the fraction of the stock susceptible to fishing; rate of accession (analogous to survival rates); greatest age involved; difference between recruitment and initial ages; food ration; correlation coef..</p><p>ρ (ro)—BH_ Pre exploitation phase; recruitment at the area where the fishing is in progress; ρ’ entry to exploited phase (first retained). R_ Rate of fishing.</p><p>R—BH_ G_ I_ R_ Recruitment related par. B_ N˚ of fish recruited annually to the exploited area; n˚ entering the exploitable phase in a given period; R’ n˚ entering exploited phase each year at age t<sub>ρ’</sub>; maximal ration; n˚ of recaptured marks. G_ R' n˚ at the age of first capture; R<sub>1</sub> … R<sub>R</sub> species affecting the recruitment of target species; raising factor. I_ N˚ of recruits entering the exploitable phase. R_ (Absolute) n˚ of recruits to the vulnerable (catchable) stock whatever by movements in to the region fished or by change in size or behaviour; n˚ of recaptured marks; multiple correlation coef.; feeding ration.</p><p>s—BH_ Sex ratio as % of mature females in total mature population; physiological surface area; mean survival rate; fish which would have been caught in a large cover applied to the body of the gear; ratio of the catch obtained in a haul to the saturation catch. G_ Surface area of a fish; raising factor. I_ Observed annual fraction surviving; selection factor. R_ Rate of survival; standard deviation; X<sub>s</sub> condition of maximum sustainable yield.</p><p>σ (sigma)—BH_ Standard deviation; σ<sup>2</sup> variance; generic cons. G_ σ<sup>2</sup> population variance (var for the sampling variance).</p><p>S—BH_ Grazing efficiency; Russell’s stock size in weight; variance (in recruitment). G_ (Annual) rate of survival; Russell’s stock size; abundance of spawning stock; prop. of retained fish; X<sub>S</sub> minimum limit; standard deviation. I_ Annual fraction surviving (survival rate); selection factor; the girth at which the fish is meshed. R_ Rate of survival; S' apparent.</p><p>S.F.—I_ Selection factor as fifty percent (retention or escaping) point/mesh size.</p><p>Σ (sigma)—BH_ R_ Summation sign.</p><p>t—BH_ Age of fish; t' and t'' coef. in linear approximation to a selection ogive; t<sub>0</sub> scale cons. in the VBGF (or theoretical age at which the size is zero); t<sub>r</sub> age at recruitment; t<sub>c</sub> age at which fish are liable to be retained by the gear; t<sub>L</sub> mean age of the oldest fish. G_ Time period; t<sub>0</sub> some previous time and cons. in VBGF; t<sub>c</sub> at first capture; t<sub>L</sub> maximum age in the fishery; t<sub>p</sub> partial length recruitment; t<sub>r</sub> at recruitment. I_ Time or age. R_ Time or age; time required for growth in growth—temperature models.</p><p>τ (tau)—BH_ Recapture period in marking; calendar date.</p><p>θ (theta)—BH_ Age group n˚; X<sub>θ</sub> prop. of females of age-group θ that are mature; angle definition; the youngest age group free from the influence of recruitment of gear selectivity.</p><p>T—BH_ Transport coef. (rate of interchange of fish between adjacent areas); mean age in catch or exploited phase; T<sub>max</sub> maximum age in the sample; gross tonnage; fraction surviving; total. G_ Upper bound of a given time interval; time; non selective gear; gross tonnage. I_ Transport coef. R_ Interval of time; successive intervals in the life of the fish (not necessarily of equal length); weighed summation of age groups n˚ (also in Chapman and Robson); totals; temperature (in Celsius); metabolism.</p><p>u—BH_ Yield per recruit contributed by fish; ratio of grazing mortality coef.; weighting coef.; co-ordinate defining sub-areas. R_ The fraction by n˚ of fish caught by men; rate of exploitation (annual expectation); ratio of recovery to marked fish released; generic ratio; u<sub>E</sub> equilibrium rate of exploitation (as captures divided by recruits).</p><p>υ (upsilon)—BH_ Age group.</p><p>U—G_ R_ Catch per unit of effort in n˚ (U<sub>C</sub>) or weight (U<sub>Y</sub>). BH_ Sum of square residuals; cons. Summation in yield analytical computation. G_ U<sub>0</sub> U<sub>3</sub> cons. in the expression for yield in weight. R_ Instantaneous rate of “other loss” (also emigration and shedding of tags).</p><p>v—B_ Co-ordinate defining sub-areas; fraction of a year. R_ Expectations of natural death; v' apparent.</p><p>V—G_ R_ Virtual population and cohort analysis par. BH_ Effective velocity of (random) movements; whole n˚ of years; vulnerability. G_ Value of individual fish; fish surviving the n<sub>th</sub> year of life (in cohort analysis). R_ Utilized stock; variance.</p><p>w—BH_ R_ Weight of individual fish. BH_ w<sub>c</sub> weight corresponding to the (theoretical) greatest steady catch obtainable by catching all fish at once (F = ∞). G_ Mean weight in a group; weight sampled. R_ N˚ of spawners divided by the replacement n˚ of spawners.</p><p>W—BH_ Weight of individual fish (particular) and at stock level; W<sub>∞</sub> one of the two main par. of the VBGF proportional to the cube of the ratio of the coef. of anabolism and catabolism (hence, less sensible to temperature variation); W<sub>∞</sub> upper asymptote of weight. G_ Weight of landings; mean weight of a age group; individual fish; weight; W<sub>∞</sub> maximum (limiting) especially in VBGF; W<sub>c</sub> at mean selection length; average larger than mean selection length; W<sub>k</sub> of retained catch. I_ W<sup>∞</sup> par. of the VBGF in weight; fish weight. R_ Reproductive stock; weight of a group of fish (year-class, stock); W<sub>0</sub> initial weight of a stock; W<sub>∞</sub> theoretical maximum stock weight in unfished condition; prop. of recruits in Allen’s recruitment method; n˚ of spawners divided by the replacement n˚ of spawners.</p><p>x—BH_ Mid point of the length interval. G_ Independent variable in regression generic coef.; X<sub>x</sub> value in a particular year. I_ X<sub>x</sub> year class. R_ The ratio of two initial populations; any (mainly dependent) variable (in regression); fractional representation of each age in the catch.</p><p>ξ (xsi)—BH_ Annual food consumption (individual).</p><p>X—BH_ Denotes a particular year, usually as suffix; “other loss than fishing” coef. in marking theory; fishing effort (in case of no ambiguity). G_ Effort in surplus production; fishing power; other loss rate (in tagging). I_ Mean girth; effective overall fishing intensity (“Japanese” fishing intensity); to be used only in case of no ambiguity (otherwise f should be employed). R_ Different kind of fishing effort; classification of stock composition; par. in Jones yield computation.</p><p>Ξ (xsi)—BH_ Annual food consumption of a fish population.</p><p>y—BH_ Growth increment (and increment per unit time) in length increment—average length analysis. G_ Dependent variable in regression; generic coef.; instanttaneous rate of capture of hooks. R_ Instantaneous rate of emigration; ratio in Baranov’s food biomass relationship.</p><p>Y—BH_ G_ I_ R_ Yield (catch in weight). BH_ Yield in weight (Y<sub>W</sub>) or n˚ (Y<sub>N</sub>); total weight in fish catch; Y* expected post-regulation catch; maximum sustained yield or potential yield. G_ Catch in n˚; (yield) in weight; ultimate yield after (Y<sub>2</sub>) a change in size limit (Y<sub>K</sub>); performance. I_ Weight of fish in the catch (catch in weight). R_ Catch by weight; Y<sub>S</sub> maximum sustainable yield; Y' surplus production; different kind of fishing effort; classification of stock composition; dependent variable in regression; individual n˚ of eggs.</p><p>z—BH_ Ratio of fished to unfished areas (z = ∞ when the whole area is fished); cons. in year to year recruits variation. R_ Newcomers; instantaneous rate of recruitment or immigration; n˚ of recruits divided by the replacement n˚ of spawners (and recruits).</p><p>Ζ (zeta)—BH_ Maintenance food coef..</p><p>Z—R_ G_ I_ Instantaneous total mortality coef. BH_ Correction term (in recruitment-egg relations); 'Z/K. R_ Recruitment; recruits to a stock divided by the “replacement” n˚ of recruits; instantaneous rate of disappearance (F + M + U).</p></sec></sec><sec id="s3"><title>3. RESULTS AND DISCUSSION</title><sec id="s3_1"><title>3.1. The “Proposed” List</title><p>The x, X—Individual—(lower case) observation and stock- (capital letter) level par., respectively. &#167; Individual “fish” refers to any generic fish, shellfish or other organism exploited or exploitable [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>], if not otherwise specified.</p><p>*X—The asterisk, as left superscript, denotes that the X symbol results already well established (and maintained), but with a different meaning. &#167;&#167; As right subscript (or superscript) denotes equilibrium quantity [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>] or condition (also in unfished equilibrium), or “critical” par. [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. As right superscript, it also specifies better an almost equivalent (or homologous) par.; for example, N and N* as n˚ and biomass of recruits at the start of year [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>], R and R* as recruitment in n˚ and weight [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] or L* as maximum observed length (or largest specimen) in a sample [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Other diffuse uses are: “true” value [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]; generic critical or optimum (optimal in [67,68]) the average size of a fish of a given cohort when the instantaneous rate of natural mortality equals the growth. It also characterises symbols not used in Ricker’s textbook; a par. estimated with methodology different from the usual. Further as right superscript, it has been used to identify a statistic or estimate of a par. [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>] or a value at maximum or at stable condition [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>'X'—A special variant of the X par. As left superscript, a conceptual close par. (for example see 'U). As right superscript, a special case of the same given par. (for example, see A'). Another example is the Y' defined as total yield as a fraction of the RW<sub>∞</sub> product or X' as an adjusted value[<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. &#167;&#167; As superscript, a statistic or estimate of a par. [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>]. Pristine level or condition [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>X<sup>+</sup>—Cumulated par., integrated beyond an age, size or time limit. <sub>t</sub>X<sup>+</sup> plus (terminal) group. <sub>(x,y)</sub>X<sup>+</sup> accumulation over the considered range, for example, all previous ages [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. &#167; C<sub>t</sub> terminal catch in VPA; C(L<sub>1</sub>, <sub>∞</sub>) [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. C<sup>+</sup> cumulated catches [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. X<sub>+</sub> total; overall [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. The sum of all catches of a year-class in subsequent years starting at age A [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167;&#167; F<sup>+</sup> at extinction [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p><sub>c</sub>X—Constrained estimation (to be specified).</p><p>X<sub>(•)</sub>—Estimated via invariants or empirical equations rather than a true estimate. &#167; Estimates uncertain [<xref ref-type="bibr" rid="scirp.35705-ref48">48</xref>]. Preliminary estimate [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. To not be confounded with a proxy estimate [<xref ref-type="bibr" rid="scirp.35705-ref21">21</xref>].</p><p><sub>[</sub>X—The dot at the left subscript denotes a variant (to be specified) from the basic definition. For example, <sub>•</sub>K<sub>j</sub> denotes the juveniles K in the biphasic or double VBGF.</p><p><sub>₪</sub>X—Non equilibrium condition. &#167; Not cons. or random variation without trend par. condition (alternative to steady state).</p><p><sub>↨</sub>X—Array of values. &#167; X<sub>array</sub> [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>].</p><p>X<sub>∆</sub>—Par. referring to a finite interval. For example in Chen and Watanabe [<xref ref-type="bibr" rid="scirp.35705-ref75">75</xref>] procedure to estimate M.</p><p><sub>∩</sub>X—The Maximum value of a par. &#167; The “maximum” has been often interpreted [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>] as “optimum” [6, page 389] or “critical” [<xref ref-type="bibr" rid="scirp.35705-ref56">56</xref>]. For example, a<sub>cri</sub> age at maximum cohort weight t<sub>cri</sub> in [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]; c* and t* critical size and age as the value where biomass of a cohort is maximum in the absence of fishing and c<sub>opt </sub>the value which maximizes yield when fishing mortality rate is fixed at the F<sub>0.1</sub> [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]; l<sub>cri</sub> the length above which all fish are vulnerable [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>] or optimum age at exploitation); t<sub>y</sub> in [<xref ref-type="bibr" rid="scirp.35705-ref77">77</xref>]. The most famous example is the Holt’s optimum age (valid only in case of no dependence relationships) at which an (unexploited) cohort reaches its maximum abundance or reflecting the catch obtainable allowing a year class to reach its greatest total weight and hence catch it at once[6, page 374]. Other cases are: the Gulland’s approximation (F<sub>opt</sub> ~ M); the maximum value of an equilibrium curve as function of fishing intensity [78; 6, page 389]; the L<sub>opt</sub> as the length at maximum yield-per-recruit [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]; the X<sub>SUP</sub> [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>] and X<sub>m</sub> maximum or optimum [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Strictly speaking, “optimum” (i.e. any point which might be considered the “best” within the ultimate objective of fishery regulation) should be restricted to economic criteria [6, page 390] or management, but not to assessment. “Optimum” should not be confounded with the optimum sustainable yield, OSY, or Roedl’s optimum yield OY [<xref ref-type="bibr" rid="scirp.35705-ref19">19</xref>]. “Critical” should not be confounded with the Hjort’s critical period in which the numeric consistency of a cohort is determined; it is classically the larval or plankton stage (Hjort’s hypothesis) or (more recent) the juvenile stage [79,80].</p><p>X<sub>obs</sub>—Observation [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Observed value.</p><p><sub></sub>X—Inflexion. For example, W<sub>a</sub> = 0.29W<sub>∞</sub> in the isometric (cubic) VBGF.</p><p>X<sub>•</sub>—25, 50, 75 the par. corresponding to 25%, 50% and 75% of a logistic (anti symmetric) curve (or ogive) mostly in selection studies [<xref ref-type="bibr" rid="scirp.35705-ref81">81</xref>]. &#167; X50 or X<sub>50</sub> are often used to indicate size at (first) maturity or size at gear retention. The 50% has been defined “fifty percent (retention or escaping) point [<xref ref-type="bibr" rid="scirp.35705-ref49">49</xref>]. The 75% - 25% difference has been denoted as “selection span” [<xref ref-type="bibr" rid="scirp.35705-ref49">49</xref>]; nowadays, it is often denoted as “range” [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Reference [<xref ref-type="bibr" rid="scirp.35705-ref49">49</xref>] attributed a different (and apparently more appropriated) meaning to “selection range” as the range in fish length over which a fishing gear exercise selection.</p><p><sub>c</sub>X—Conventional par. For example, the Taylor’s 95% maximum length approximation as index of longevity [62,71].</p><p>a—Age [25,61,64,65,67,82-84]. (Absolute) individual age [85,70]. <sub>r</sub>a relative. &#167; t, T. Population age [<xref ref-type="bibr" rid="scirp.35705-ref85">85</xref>]. Age class; arbitrary reference age [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Age at maturity or first reproduction [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Generic age [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. &#167;&#167; Σa all individuals (new stock) transferring from the non-catchable to the catchable category [<xref ref-type="bibr" rid="scirp.35705-ref88">88</xref>]. Total mortality fraction and available population (in fished area) [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>]. Annual rate of total mortality [<xref ref-type="bibr" rid="scirp.35705-ref89">89</xref>]. Instantaneous rate of loss of bait [<xref ref-type="bibr" rid="scirp.35705-ref90">90</xref>]. Cons. in the Putter expression of the VBGF and exponent relating length to surface in the generalisation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. a<sup>2</sup> as mean square coefficient of dispersion [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Coefficient of intraspecific competition [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Production/rate of recruitment ratio [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Vulnerability-selectivity age related par.[<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Par. in Schnute model [<xref ref-type="bibr" rid="scirp.35705-ref93">93</xref>]. Mortality related par. in Ecopath [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Par. in different models [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Search rate; generic coefficient; n˚ of marked released [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Par. in different models; par. in the w =al<sup>b</sup> or non exponent coefficient in the length/ weight relationship [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Par. in different stock-recruitment relationships; effective search rate in Ecosim; [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Y-intercept in (AM or GM) linear regression, or multiplicative term in a length/weight relationship [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Positive cons. in von Bertalanffy (isometric) weight function [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>*a—Area fished (interested) by the gear by unit of effort [94;65]. Reference unit area interested by a fishing or experimental unit. a<sub>s</sub> swept [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>] or covered unit area. a<sub>f</sub> over which the fishing effort is distributed. &#167; a [25,71,74,76].</p><p>α—Free, to be specified. &#167;&#167; Season [<xref ref-type="bibr" rid="scirp.35705-ref95">95</xref>]. Cons. per unit of effort [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. Level of significance of a test [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. Cons. in the generalisation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Par. in total metabolism (T) and weight (W) according to T = αW<sup>γ</sup> [<xref ref-type="bibr" rid="scirp.35705-ref98">98</xref>]. Coefficients in Jones and Johnston [<xref ref-type="bibr" rid="scirp.35705-ref99">99</xref>] growth, reproduction and mortality analysis. Age [<xref ref-type="bibr" rid="scirp.35705-ref100">100</xref>]. Par. in different models, especially SRR i.e. stock recruitment relationship [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Par. of the “asymptotic (overall) yield model” [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Par. in the recruitment function [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Par. (also scaled) of the Ricker stock-recruitment relationship; special values related to F<sub>0.1</sub>, F<sub>ey</sub> and MSY [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Par. in age-length growth model [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Subscript indexing length frequency data in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Instantaneous tagging mortality (dying immediately after tagging); par. in catching power and vessel standardization; intercept in the Ford-Walford plot [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Biological lower critical value [<xref ref-type="bibr" rid="scirp.35705-ref103">103</xref>]. Model par.; density independent coefficient (also slope at the origin) in SRR; coefficient (condition factor) in both isometric and allometric weight-length models; coefficient in Brody model; significance level; prop. of fish of length l; tag loss [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Generic par., for example, governing stock production especially at small size (such as intrinsic rate of natural increase) or specifying the state variable in Individual Based Models; slope at the origin in the general form of the SRR also defining the compensation capability of a stock; age at maturity; α<sub>i</sub> Manly-Chesson food preference index [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Cons. in SRR; limit of R/S when S → 0 [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>].</p><p>A—Age [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Absolute age at stock level [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. <sub>r</sub>A relative. &#167; t, T. Total n˚ of age classes [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Mean age [<xref ref-type="bibr" rid="scirp.35705-ref84">84</xref>]. A<sub>0</sub> frequency of age a fish in a random sample A [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167;&#167; Recruitment in weight [88,105]. Total n˚ of hooks [<xref ref-type="bibr" rid="scirp.35705-ref90">90</xref>]. Mouth area of the net [<xref ref-type="bibr" rid="scirp.35705-ref106">106</xref>]. Smaller mesh size in gill net selection experiment [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Par. relating L<sub>∞</sub>, L<sub>1</sub>, and L<sub>2</sub> with M/K [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Annual (or seasonal) total mortality rate [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>]. N˚ of tagged fish alive at time t; abundance; area; par. in Jones’ length based cohort analysis [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Height of the growth production function [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. N˚ of fish dead after a given time; relative abundance [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. Adult; A<sub>j</sub> “total age” of predators [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Aspect ratio of the fish caudal fin [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. Attrition rate [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Annual death fraction; maximum age of reproduction; the last age group; the n˚ of age groups [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Area [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Average [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]. Attribute vector in Individual Based Models; threshold value of viability in economics of fisheries [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Cons. (intercept) of the simple linear model [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>].</p><p>A<sub>c</sub>—Age of entry to capture. Age at which 50% of fish enters the exploited phase. A<sup>c</sup> knife edge (the probability of capture becomes suddenly finite at this point). &#167; t<sub>ρ’</sub>, t<sub>c</sub>. Age at which fish are first retained; age at first capture; 50% of selection age for the mesh in question.</p><p>A<sub>ch</sub>—Age of the cohort; all the fish born in a discrete time interval of a given year. For example: A<sub>1st80</sub>. &#167; Usually coincident with the age class in case of continuous recruitment or one discrete recruitment per year; in case of multiple recruitment pulses, “micro cohort” or “stock let” [<xref ref-type="bibr" rid="scirp.35705-ref110">110</xref>] should be used and specified.</p><p>A<sub>cl</sub>—Age of the year class; age class. All the fish born in the same year. For example, A<sub>1980</sub>.</p><p>A<sub>g</sub>—Age at generation. Average age of the parents when their offspring are born. &#167; t<sub>g</sub>.</p><p>A<sub>m</sub> – Age at 50% onset of sexual maturity, based on the present gonadic activity. A<sup>m</sup> knife edge. <sub>•</sub>A<sub>m</sub> other to be specified; for example, mean age of spawners. &#167; t<sub>m</sub>, T<sub>m</sub>. Age at first maturity; mean age at maturity; massive maturation [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. A50 [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>]. Fish from A<sub>m</sub> onwards are usually considered adults [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>].</p><p>A<sub>mean</sub>—Mean age of the stock. Ratio between the integrals of the weighed by age consistency of the different cohorts (numerator) and the consistency of the different cohorts. &#167; T, t, t<sub>media</sub>.</p><p>A<sub>mx</sub>—Massive age at maturity, the minimum size above which all the fish are able to reproduce independently from the present activity or the production pattern (discrete, continuous, intermittent, batch ecc.). &#167; Almost never implemented; often confused with A<sub>m</sub>.</p><p>A<sub>M</sub>—Age at end of the reproductive span. Age above which the contribute to spawning of a cohort is negligible. &#167; t<sub>M.</sub> [<xref ref-type="bibr" rid="scirp.35705-ref75">75</xref>].</p><p>A<sub>∩</sub>—Age at maximum. Age at which an unexploited or exploited (<sub>•</sub>A<sub>∩</sub>) cohort reaches its maximum living biomass corresponding to the balance between growth rate and natural mortality. &#167; Originally referring to the unexploited condition as t<sub>cri</sub> or t*; critical age [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. In case of isometric VBGF, the critical age is empirically related to maximum age [A<sub>∩</sub>/A<sub>max</sub> ≈ 0.38; 11].</p><p>A<sub>l</sub>—Age of ultimate significant contribute to the fishery. The greatest age for which adequate data usable for fisheries assessment are available. Maximum age above which scanty and not statistical representative samples can be gathered from the stock given the reduction in n˚ as a consequence of fishing mortality (arbitrary threshold: 5% of caught or sampled specimens). &#167; t<sub>l</sub>, L, A<sub>L</sub>. Fishing or ecological longevity; maximum exploited age. A par. variable according to the fishing pattern and true longevity of the stock often confused with life span after the classic Jones’ approximation t<sub>l</sub> ~ ∞.</p><p>A'—Age of fully capture. The youngest age that is fully represented in the gross catch sample. A'' the age immediately successive to A' (which should be preferred in computations). &#167; t' [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. To not be confounded with the age at entry to capture.</p><p>A<sub>R</sub>—Age at which the 50% of fish enter the area where the fishing is in progress and becomes liable to encounter with the gear. &#167; t<sub>ρ</sub>, t<sub>r</sub>. Recruitment at the fishing grounds; age at which the fish become present in the exploited area and susceptible to the capture with the given gear.</p><p>A<sub>dR</sub>—Age at de-recruitment from the fishery. Age at which the fish are still present in the exploited area, but become no more susceptible to the capture with the given gear (fish will no longer be vulnerable or accessible to the gear for a given fishing pattern). &#167; A<sub>d</sub>, D50%, R, t<sub>rif</sub>. Deselection (length) [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Gill net de-selection; age at de-selection; at reform; right-end de-selection [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>].</p><p>A<sub>L</sub>—Longevity. True life span in unexploited condition. Estimated or observed theoretical (true) longevity (maximum age). Average age of the specimens in the upper tail (95<sup>th</sup> quantile) [111,112] as estimated from a representative (not biased) sample extracted from an unexploited (or lightly exploited) stock sampled from its natural environment. &#167; T<sub>max</sub> [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>]. T<sub>L</sub> experimental wild longevity. T<sub>m</sub> [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. t<sub>max</sub> [<xref ref-type="bibr" rid="scirp.35705-ref114">114</xref>].</p><p>A<sub>Lx</sub>—Present longevity. The maximum age recorded for the present investigated stock or (A<sub>Lx</sub>) species by aging just the largest few fish at hand [as proxy of A<sub>L</sub>; 112]. A<sub>mx</sub><sup> </sup>estimated according to a method to be specified (mean of n<sup>th</sup> extremes, extreme values theory etc). &#167; T<sub>max</sub>, a<sub>max</sub> [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. t<sub>max</sub> [<xref ref-type="bibr" rid="scirp.35705-ref114">114</xref>].</p><p>A<sub>Lxe</sub>—Ever observed longevity. The maximum age ever recorded for the investigated stock or (A<sub>Lxe</sub>) species in nature (*A<sub>Lxe</sub> from captivity data). &#167; T<sub>max</sub>.</p><p><sub>c</sub><sub>x</sub>A<sub>L</sub>—Conventional longevity. Age at which the cohort has been reduced to <sub>0.05</sub> (x = 5) or <sub>0.01</sub> (x = 1) of the initial reference abundance. <sub>c</sub><sub>95</sub>A<sub>L</sub> age at 95% of the asymptotic length or Taylor’s approximation, originally expressed as = (2.966/K) + t<sub>0</sub>; often reported as ≈ 3/K).</p><p>A<sub>x</sub>—Age group where x varies from <sub>I</sub>, <sub>II</sub>, <sub>III</sub> <sub>IV</sub> etc [<xref ref-type="bibr" rid="scirp.35705-ref8">8</xref>].</p><p>A—Age at inflexion. Age at which a discontinuity occurs (to be specified). &#167; t<sub>η</sub>.</p><p>A<sub>0</sub>—Age at theoretical zero size in the VBGF and allies [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. The theoretical (hypothetical, artificial, arbitrary) “age” at which the fish would have been zero length/weight if it had always grown according to the VBGF (hence, it can be either positive or negative). Location par [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. A<sub>0</sub> any initial or starting age (such as length at birth in sharks); scale par. to be specified. &#167; a<sub>0</sub> [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. t<sub>0</sub> theoretical age at which the weight/length is zero; cons. which simply moves the curves along the abscissa and can be interpreted as the time measured from 0 at which the animal would had zero length if it had followed the same growth curve all its life [<xref ref-type="bibr" rid="scirp.35705-ref115">115</xref>]. Adjusting par. [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>]. Almost always it takes non-zero negative values [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>], and does not usually express “prenatal growth” [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Strictly speaking, the par. should be referred to isometric (cubic) weight-length relationship. Often it is omitted in the general treatment or assessment based on the VBGF, but it must be considered in real computations [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>].</p><p>*A—Amount of area occupied by the population or stock [94,76,65]. Reference area of stock distribution. *A<sub>s</sub> study area. *A<sub> f</sub> over which the fishing effort is distributed. &#167; A [67,71].</p><p>AA'—The eumetric line joining the (locus) of maxima of yield-mortality curves in the yield-isopleths diagram.</p><p>ASP—Annual surplus production [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>b—The exponent in the length-length (<sub>•</sub>b) and lengthweight relationships[25,66,70,74,76,116,117] according to = *kL<sup>b</sup>. b<sub>e</sub> and b<sub>10</sub> after ln and log transformation. b = 1 and b = 3 conventionally denote an isometric (or isogonic) relationship in length-length and weight-length relationship, respectively. ≠1 and ≠3 denote a positive or negative allometry (heterogonic or disharmonic relaionship) [<xref ref-type="bibr" rid="scirp.35705-ref116">116</xref>]. &#167; The original Huxley and Teissier formula was expressed as y = bx<sup>k</sup>. Strictly speaking, the isometry and allometry would be used for length-length relationship. n [118,119]. &#167;&#167; Instantaneous rate of hooking fish [<xref ref-type="bibr" rid="scirp.35705-ref90">90</xref>]. Life span [<xref ref-type="bibr" rid="scirp.35705-ref120">120</xref>]. Exponent relating length to “effective metabolic rate” in the generalisation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Par. in different models [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Par. in the autoregressive time series model [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Selectivity age related par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Shape par. in Schnute model [<xref ref-type="bibr" rid="scirp.35705-ref93">93</xref>]. Par. in different models; recruitment per spawner [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Yearly clutch size or scale par. [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Juveniles produced/unit adult biomass/time [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Selectivity coefficient [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>]. Generic coefficient [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Par. specifying the adaptive trait in Individual Based Models; mass of prey [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Slope in linear regression [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Positive cons. in von Bertalanffy (isometric) weight function [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. (Scaling) par. relating some initial length (L<sub>0</sub>) such as at settlement [<xref ref-type="bibr" rid="scirp.35705-ref121">121</xref>] or at birth [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>] to L<sub>∞</sub>.</p><p>b'—Slope in the relationship between trophic level and body weight &#167; b [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>β—Free. &#167;&#167; Season indices of adult stock [<xref ref-type="bibr" rid="scirp.35705-ref95">95</xref>]. Exponent in the length weight relationship [<xref ref-type="bibr" rid="scirp.35705-ref122">122</xref>]. Unit value of the catch [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. Probability to accept a null hypothesis (H<sub>0</sub>), when in fact it is false [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. Par. in different models, especially SRR [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Par. of the Ricker stock-recruitment relationship [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Par. in the recruitment function [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Par. in age-length growth model [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Tag reporting (or returning) rate; par. in catching power and vessel standardization [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Biological upper critical value [<xref ref-type="bibr" rid="scirp.35705-ref103">103</xref>]. Exponent in K1—W relationship; Bunsen coefficient [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. Par. in effort standardisation; model par.; exponent in the allometric weight-length models; coefficient in Brody model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] Shape par. in different SRR and yield —effort relationships; density-dependent mortality coefficient in the Ricker SRR [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>B—Biomass [65,67,76,83,104,107,117]. Average biomass of the fishable stock at equilibrium [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Size in (living) weight [88,105], population [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>], total [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>] or stock biomass [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Fish biomass [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. B<sub>0</sub> the pristine (unexploited, unfished, prior of any fishing) level [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. B<sub>∞</sub> theoretical asymptote biomass, the level to which an unexploited (or lightly exploited) stock tend in an undisturbed environment. B<sub>s</sub> spawning stock. B<sub>m</sub> at which MSY occurs [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167; B<sub>F</sub> fecund biomass [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. B as bioass of a cohort [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Generic Biomass [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. B<sub>0</sub> virgin or unfished; B<sub>∞</sub> asymptotic or “pristine”, “virgin”, “unfished” analogous to the logistic K; births [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. S [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. K carrying capacity (normally according to the logistic population model, also defined with L by [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>] and A by Ivlev [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. SSB [<xref ref-type="bibr" rid="scirp.35705-ref21">21</xref>]. B<sub>inf</sub> or K carrying capacity or unexploited biomass [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. B<sub>0</sub> natural (no fishing) biomass curve; B** escapement [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. &#167;&#167; B n˚ of fish perished by natural causes [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. Frequencies in equal length intervals [118,119]. Total n˚ of newborn individuals in Schaffer formula [<xref ref-type="bibr" rid="scirp.35705-ref121">121</xref>]. Larger mesh size in gill net selection experiment [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Bias [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. B par. in Caddy [<xref ref-type="bibr" rid="scirp.35705-ref124">124</xref>] M asymptotic model. Variance component between length interval in LFA [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Cons. (slope) of the simple linear model [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>].</p><p>BB'—The eumetric line (contours) joining the (locus) of maxima of yield-age at entry (mesh) curves F in the yield-isopleths diagram.</p><p>BI—Biomass index. Estimation of local abundance in weight of fish standardized to 1km<sup>2</sup>. BI<sub>h</sub>; in case of hour based standardization.</p><p>B/R—Biomass per recruit. B'/R, relative [66. &#167; BPR [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>].</p><p>c—Capture related general par. with the exception of the (commercial) catchability coefficient (q) relating fishing mortality to fishing effort. X<sub>c</sub> of entry to fishery; at first liable to capture by the fishing gear in use. Fishable size [65,70]. c<sub>s</sub> the fraction of fish captured in an experimental set (0 &lt; 1); &gt; 1 in case of herding effect [<xref ref-type="bibr" rid="scirp.35705-ref94">94</xref>]. &#167; Σc sum of the weights of all fish caught during the year [<xref ref-type="bibr" rid="scirp.35705-ref88">88</xref>]. c = l/m relative releasing effect or ratio between the length at 50% of release and inner mesh size [<xref ref-type="bibr" rid="scirp.35705-ref125">125</xref>]. t<sub>c</sub> at first capture. c, Q, overall gear efficiency, i.e. the prop. of fish which have been in touch of the gear and were at the end captured; exceptionally, fish can be attracted and actively enter inside the codend by the mesh [<xref ref-type="bibr" rid="scirp.35705-ref126">126</xref>]. Cons. of proportionality between F and f [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>]. Proportionality coefficient relating to the efficiency of the gear [<xref ref-type="bibr" rid="scirp.35705-ref94">94</xref>]. &#167;&#167; Instantaneous rate of loss of hooked fish [<xref ref-type="bibr" rid="scirp.35705-ref90">90</xref>]. Juvenile survival rate to maturity in Schaffer formula [<xref ref-type="bibr" rid="scirp.35705-ref121">121</xref>]. Index of ecological similarity [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Cons. in P/B = bw<sup>c</sup>; CPUE [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Cons. [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Upper and lower limits for the mean asymptotic length [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Par. in different models; competition coefficient; shape par. in Deriso’s SRR; n˚ of prey; capacity in multistage SRR [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Exponent in the height of the growth production function [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Food consumption rate per unit biomass [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. c and c<sub>y</sub> operating cost and cost per unit caught [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Coefficient in the allometric W = cl<sup>n</sup> [<xref ref-type="bibr" rid="scirp.35705-ref77">77</xref>] or W = cl<sup>m</sup> [Bayley’s method; 70]. Par. in different contexts, for example, as correlation coefficient in the Shepherd’s stock recruitment model; district-specific escapements vector in “run reconstruction” [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Competition [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Positive cons. in the von Bertalanffy (isometric) weight function [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>*c—Ratio of length at capture and maximum (asymptotic) length in potential yield computations. &#167; c [67,76].</p><p>*c<sub>1</sub>*c<sub>2</sub>—Hoenig and Lawing’s coefficients; multipliers for estimating Z and its standard error using one of Hoenig’s methods given the sample size from which the longevity estimation was derived. &#167; c<sub>1</sub>-c<sub>2</sub> [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. &#167;&#167; c<sub>1</sub>-c<sub>2</sub> interaction coefficients in Lotka-Volterra model [70,71]. Coefficients in Beddington and Cooke potential yield computations [<xref ref-type="bibr" rid="scirp.35705-ref128">128</xref>]. To not be confounded with unit costs of measuring length and age [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>cov—Covariance [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>C—Catch in n˚ [64,67,86,89,95,104,117] related to the fishing activity [25,65,107,70]. C<sub>g</sub> gross; C<sub>b</sub> not target; C<sub>r</sub> retained on board; C<sub>l</sub> live; C<sub>r</sub> rejected; C<sub>u</sub> landed. &#167; Catch in weight [88,129]. N˚ of tagged fish which will be caught [<xref ref-type="bibr" rid="scirp.35705-ref130">130</xref>]. C<sub>W</sub> catch in weight [<xref ref-type="bibr" rid="scirp.35705-ref94">94</xref>]. C<sub>n</sub> food intake [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Tags caught and returned; change in weight from tagging to recovery; total catch in weight units; catch per unit of time; aggregate productivity in multistage SRR [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. From [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]: CLi∞ cumulative catch in n˚ from length i to L∞ and C<sub>im</sub> cumulative catch in n˚ for mesh size m; t terminal catch in VPA. C<sub>(t)</sub> cumulative catch; n˚ of fish in age a group; capture of marked specimens [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167;&#167; Cost of the fishing effort [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>] Cons. in the Putter expression of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Average increment per day in larval life [<xref ref-type="bibr" rid="scirp.35705-ref131">131</xref>]. Cons. in trawl performance [<xref ref-type="bibr" rid="scirp.35705-ref106">106</xref>]. Multiplicative factor for debiasing recruitment estimates [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Generic cons. [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Efficiency par. in mammals [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Cons. in integration and matrix; total cost of measuring length and age; consumption rate in multispecies modelling [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. C* prey consumption [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Consumption [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]. Amount of food consumed; cost per unit of effort; energy cost in handling or searching for prey; control; C<sub>24</sub> daily ration [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Cons. of the SRR generalising the model [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>]. Cost coefficient [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>˚C—Sea water temperature in Celsius degrees. ˚C<sub>b</sub> at bottom; ˚C<sub>s</sub> at surface.</p><p>*C—Factor which expresses the amplitude (or magnitude) of the growth oscillation in the Pauly and Gatschuz’s seasonal length growth VBGF [66,72]. &#167; C [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. It ranges between 0, no oscillation, up 1, growth stops at WP [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. Values higher than 1 can be also obtained indicating a prolonged no growing phase (length shrinkage is a rare phenomenon in wild marine organisms [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>].</p><p>C<sup>2</sup>—Par. in Powell Z/K estimation [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>].</p><p>CC—Catch curve, the ln of the abundance in n˚ (or index) at successive ages (CC<sub>a</sub>) or sizes (CC<sub>l</sub>).</p><p>CE—Coefficient of error [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>].</p><p>CF—Condition factor [70,116], generally as [w/l<sup>b</sup>] &#215; 100. <sub>T</sub>CF Tesch w/L<sup>b</sup>. <sub>F</sub>CF Fulton (in case of isometry). <sub>C</sub>CF Clark. <sub>rel</sub>CF Le Cren’s relative [<xref ref-type="bibr" rid="scirp.35705-ref116">116</xref>]. CF any other to be specified (for example, within age groups or a given age group). &#167; c.f. [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. q [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. The symbol K is generally used for Fulton [56,70,116]. K<sub>mean</sub> for Clark [<xref ref-type="bibr" rid="scirp.35705-ref116">116</xref>].</p><p>CH—Cohort (see A<sub>ch</sub>).</p><p>CI—Confidence interval [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>].</p><p>CL—Age class (see A<sub>cl</sub>).</p><p>C/R—Catch per recruit in n˚.</p><p>CR—Covered region [132,133]; the area included between the trawl doors.</p><p>CV—Coefficient of variation [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>], as standard deviation/mean ratio [<xref ref-type="bibr" rid="scirp.35705-ref21">21</xref>]. <sub>•</sub>CV as standard error/mean ratio. As % if not otherwise specified. &#167; C.V. [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. CSC—Contact and selection curves; the relationships describing the probability of a fish to avoid, contact and escape after the contact/capture with a given gear. aCSC availability, rCSC contact-selection and sCSC selection [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. &#167; Selection curves [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>].</p><p>χ—Free. &#167;&#167; Arbitrary reference age in Francis’ VBGF reparameterization [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Mid point of the i<sup>th</sup> length frequency interval in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Sex ratio as fraction of spawning population that are mature females by weight; prop. of fertilised eggs that will result in females [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. To not be confounded with the chi square statistic χ<sup>2</sup> [65,66].</p><p>d—Average distance of fish in random movement. Distance travelled [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>]. &#167;&#167; Increment in length in the compensatory growth analysis [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Time interval in capture-recapture [<xref ref-type="bibr" rid="scirp.35705-ref134">134</xref>]. Integration cons. [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. d<sub>1</sub> and d<sub>2</sub> weighting factors in ELEFAN fit; pseudo-random n˚ [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Random variable and other deviation related par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Discount rate; temperature effect par. [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Power of weight to which anabolism is proportional; a cons. term [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. d<sub>1</sub> and d<sub>2</sub> density independent and dependent recruitment effects, respectively; par. in different contexts, for example, correlation coefficient between weight at recruitment and n˚ of eggs; n˚ of deaths [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. N˚ (or prop.) of prey in the diet; as subscript, deterministic [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Stage [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>df—Degree of freedom. &#167; DF [<xref ref-type="bibr" rid="scirp.35705-ref8">8</xref>]. d.f. [66,71,73].</p><p>δ (delta)—Free. &#167;&#167; Par. in growth model derivation [<xref ref-type="bibr" rid="scirp.35705-ref122">122</xref>]. Recruitment par. for density dependence; effective discount rate [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Successive age increment [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Variance related par. in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Relative size at independence [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Death rate related to natural mortality [<xref ref-type="bibr" rid="scirp.35705-ref84">84</xref>]. Asymmetry (shape) par. in selection curves; probability of grid contact and allies in “grid” studies [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Discount rate [63,68]. Standard deviation and (δ<sup>2</sup>) variance [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Variances ratio; par. in Schnute-Richards and seasonal growth models; δ<sub>t</sub> additive and independent error in each year [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Natural mortality fraction (1-exp M); density dependent mortality component; fraction of revenues to cover depreciation of the fleet; stochastic vector; derivate; zooplankton temporal “width” in the Cushing’s match/mismatch hypothesis; isotopic “fingerprint”; stable isotope index [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Par. in Schnute-Richards’ growth model [<xref ref-type="bibr" rid="scirp.35705-ref135">135</xref>]. D—Dispersion coefficient of fish [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167; Usually referred to movements among adults distribution, spawning and juvenile concentration areas [<xref ref-type="bibr" rid="scirp.35705-ref136">136</xref>]. &#167;&#167; Fishing (F) changes [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>]. Par. (1-M/H) in the Allen’s method [118,119]. Total n˚ of deaths [25,69,70, 104,107,123]. Finite time interval in capture-recapture [<xref ref-type="bibr" rid="scirp.35705-ref134">134</xref>]. A measure of the sensitivity of the output [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Jacobian matrix; n˚ of fish eaten [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Catch related par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Density of fish [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>]. Density per km<sup>2</sup> of fish [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Door spread [<xref ref-type="bibr" rid="scirp.35705-ref137">137</xref>]. N˚ dying from natural mortality in VPA [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Duration (in days) required to reach any particular stage ([<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]; for example, the larval stage [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. From [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>] density dependence, diversity indexes, egg stage duration, and density of fish. Fraunhofer diffraction function in Shepherd's method [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Coefficient in the L<sub>∞</sub> = DK<sup>−</sup><sup>h</sup> relationship [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Natural death; population density; density of prey; decrease due to natural mortality; squared deviation; par. in delay difference model; square root of accumulated variance among ages or Lai’s transformation; specified level of precision [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. As D or subscript, X<sub>D</sub>, it denotes discards; D as diet related par., for example, in Ecopath [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Deviance residuals; variance; variance matrix [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>].</p><p>*D—The shape par. in Pauly’s generalised VBGF. &#167; D (gill) surface factor [71,138].</p><p>DC—Diet composition [68,82].</p><p>DI—Density index. Estimation of local abundance in n˚ of fish standardized to 1km<sup>2</sup>. DI<sub>h</sub> in case of hour based standardization.</p><p>Δ—Any finite difference [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. &#167; Elapsed (time) and size increment in mark recapture studies [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167;&#167; Taxonomic diversity related par. [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>].</p><p>e—Base of the natural (or Napierian) logarithms; e = 2.71828… [65,66,107]. &#167;&#167; Unit effort in tagging studies [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. Effective [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Stochastic term [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Error term in model definition. Age specific fecundity; prey density [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. e<sub>detritus</sub> instantaneous export rate of detritus [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Normal random (0 - 1) variable; &#234; rate of egg production per unit biomass and unit time; fishing effort in markrecapture experiments [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Elasticity (sensitivity) [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>ε—Error term. &#167;&#167; Mean of the logarithms of n˚ sampled [<xref ref-type="bibr" rid="scirp.35705-ref130">130</xref>]. Midpoint in a given class [<xref ref-type="bibr" rid="scirp.35705-ref122">122</xref>]. Efficiency of conversion of available energy into growth or gonad energy or converting surplus energy into body weight [<xref ref-type="bibr" rid="scirp.35705-ref99">99</xref>]. Sampling error [<xref ref-type="bibr" rid="scirp.35705-ref85">85</xref>]. Par. in catching power and vessel standardization [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Gross food conversion efficiency; ratio of growth increment/food ingested during a given period [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. (Total) egg production [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Stochastic vector; variable (unrelated to abundance) mortality component [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>є—To not be used in order to avoid confusion with similar symbol. &#167;&#167; Particle size conversion efficiency [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Error term [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Unexplained predictor error or residual [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Different error terms (process, normal, additive, multiplicative etc ) [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>η—Shape par. in different models (especially in growth curves). &#167;&#167; Random variable in population equilibrium catch relationship [<xref ref-type="bibr" rid="scirp.35705-ref129">129</xref>]. Par. related to food [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Probability of being recaptured [<xref ref-type="bibr" rid="scirp.35705-ref141">141</xref>]. Random perturbation in the stochastic analysis of an exploited population [<xref ref-type="bibr" rid="scirp.35705-ref142">142</xref>]. Expected catch [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Par. in weigh at age models; residuals [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Random residuals [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>E—Exploitation rate [67,74,76] or fraction [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Prop. of dying due to fishing [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. The ratio of fish caught to total mortality when F and M take place concurrently and are unchanging or change proportionally. Overall E<sub>∞</sub> (t→∞) or E annual (t = 1) expectation of capture. &#167; Fishing effort [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. Exploitation fraction [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Defined as the F/Z ratio multiplied by 1-exp-Zt (the exploitation fraction, μ in [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] or, more properly, by 1-exp-Z(t<sub>∞</sub> - t<sub>c</sub>), hence, as t<sub>∞</sub> → ∞ E → F/Z. Rate of exploitation (u in [69,123]. E' probability of ultimate capture [118,119]; in case of cons. F/M ratio, it is equal to the exploitation rate. Exploitation pattern in Lleonart [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>]. Heincke’s fishing coefficient. &#167;&#167; Total (cumulative) effort in tagging studies [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. Expected estimate or value [65,70,72,73,122, 130]. Par. (=Hp/3q) in the length based derivation of VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Const. of locomotion [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. Efficiency index in Tuna fishing effort analysis [<xref ref-type="bibr" rid="scirp.35705-ref144">144</xref>]. E'' and E emigrating rate [145,70]. True effort [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. (Expected) mean value [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Fishing effort; size of fishing fleet; n˚ of prey eaten by a predator; total egg production; some environmental variable [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Reproductive effort [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Rate of fish encounter/escaping with/from the gear [<xref ref-type="bibr" rid="scirp.35705-ref137">137</xref>]. Fishing effort; expected par.; cumulative fishing effort in mark recapture experiments [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Instantaneous rate of gastric evacuation; effort rate; energy gained [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Reproduction rate; age or stage elasticity [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>EE—Ecotrophic efficiency [68,82]. &#167; Fraction of mortality not due to predation or fishing in Ecopath [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>ER—Expected revenue [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. &#167; R net of operative costs [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>].</p><p>f—(General) fishing effort [27,74,94,117,127]. f<sub>c</sub> capacity; f<sub>n</sub> fishing effort as collected (uncorrected; nominal); f<sub>e</sub> overall (fleet and time); f<sub>i</sub> intensity (by unit surface and time); f<sub>t</sub> time; f<sub>o</sub> effective overall intensity (weighted sum); f<sub>MSY</sub> corresponding to MSY [<xref ref-type="bibr" rid="scirp.35705-ref21">21</xref>]. &#167; F, f. N˚ of fishing efforts [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. Full-recruitment fishing mortality or effective fishing effort coefficient [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Fishing mortality rate for fully vulnerable individuals; exploitation rate [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. E as fishing effort [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. The amount of “energy” (work, fishing boats, technique and technology) used to catch fish. f<sub>MSY</sub> a.k.a. optimum f [<xref ref-type="bibr" rid="scirp.35705-ref21">21</xref>]. Fleet [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. &#167;&#167; Probability of tags recapture [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. f* n˚ of eggs/ adults [<xref ref-type="bibr" rid="scirp.35705-ref145">145</xref>]. Feeding level [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Ration requirement coefficient [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. f<sub>y</sub> first year of fishery data [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Set of auxiliary factors; fecundity; f<sub>(x)</sub> net fecundity; average net fecundity; degree of freedom; females; par. in the (fixed allocation) age sample size determination; age [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Fraction of females spawning in a given time interval [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. (Length) frequency [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Tag recovery rate [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>♀—Females [72,87].</p><p>φ—Free. &#167;&#167; Retention rate; function [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>].</p><p>φ—To not be used in order to avoid confusion with similar symbol. &#167;&#167; Generic par.; function [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. Probability of survival in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref146">146</xref>]. Par. related to food [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Translocation rate [<xref ref-type="bibr" rid="scirp.35705-ref145">145</xref>]. “Pseudovalue” in jackknife [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Fraction of population at some stage or condition [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Probability; Daan’s food requirement [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Arbitrary reference age in Francis VBGF reparameterization [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Natural mortality hazard par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Coefficient in autoregressive process; general non linear term; par. in seasonal growth model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Increase factor in R in surplus production modelling [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>Ф—Pauly and Munro growth performance index in weight and Ф' in length; logK + 2/3logW<sub>∞</sub> and (in case of isometry) logK + 2logL<sub>∞ </sub>[<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. &#167;&#167; Angle [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Gear saturation par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Par. Vector [<xref ref-type="bibr" rid="scirp.35705-ref93">93</xref>]. The same symbol is employed to denote the Golden ratio.</p><p>F—Instantaneous coefficient of fishing mortality [63, 65,67,70,74,76,86,117,130]. If not specified (see below) it indicate the average (overall weighed) F over the range of age groups which can be considered fully represented in the samples. F<sub>J</sub> juveniles. F<sub>p</sub> parental (adults). F<sub>MAX</sub> at maximum equilibrium yield. F<sub>max</sub> corresponding to Y/R<sub>max</sub> for a given entry to fishery. F<sub>MSY</sub> at maximum sustainable yield [F<sub>msy</sub> ≡ F<sub>m </sub>according to 65]. F<sub>r</sub> ratio of fishing mortality on the oldest age group to the fishing mortality of the preceding age group, used in many tuned VPA assessments [<xref ref-type="bibr" rid="scirp.35705-ref21">21</xref>]. F<sub>λ</sub> terminal (last year for which data are available for assessment; mainly in VPA). F<sub>↨</sub> array of values according to a model or equation to be specified. F' collateral mortality induced by fishing; for example, mortality due to discard [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167; M<sub>f</sub> [<xref ref-type="bibr" rid="scirp.35705-ref95">95</xref>]. F<sub>ey</sub>, F<sub>p</sub> where marginal yield per recruit is 10% or p-times the marginal equilibrium yield in a lightly exploited stock [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Fishing loss rate; fleet size [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. (F)<sub>max</sub> force of fishing mortality. To remember that F<sub>MAX</sub> is usually different than F<sub>MSY</sub>. &#167;&#167; Biomass flow up the size spectrum; scalar-valued function [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Variance within length interval in LFA [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Stomach content; starting area in fish migration [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>F<sub>c</sub>—Fecundity (general). N˚ of “mature” (hydrated) “eggs” (strictly speaking oocytes) produced on average by a female of a given size-age. aF<sub>c</sub> absolute; pF<sub>c</sub> potential (as the stock of eggs in the ovary before spawning; F<sub>pot</sub> in [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]; fF<sub>c</sub> free eggs released into water (F<sub>rea</sub> realised fecundity, in [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]; rF<sub>c</sub> relative (as function of size or age); mF<sub>c</sub> life time fecundity (i.e. the progeny derived by a female during its life); dFc daily; Fc<sub>/R</sub> annual egg-production per recruit. &#167; Often replaced by spawning biomass as a proxy. fec [76,86]. F<sub>atr</sub> as fecundity and prop. of atresic eggs [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. DEPM, daily eggs production model in Lleonart [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>].</p><p>FP—Fishing power. Relative unit efficiency of capture of different vessels versus a standard vessel. &#167; ρ, P, Q. Efficiency. [148,149].</p><p>FR—Fished region [<xref ref-type="bibr" rid="scirp.35705-ref150">150</xref>], the area covered by the wings of the gear. &#167; Fished area; 50% of the head rope length according to the Baranov’s approximation.</p><p>g—Individual general growth rate. g<sub>a</sub> absolute; g<sub>r</sub> relative; g<sub>i</sub> instantaneous; g<sub>f</sub> finite; g<sub>s</sub> specific. &#167; Σg sum of growth increments of all individuals surviving at the end of year [<xref ref-type="bibr" rid="scirp.35705-ref88">88</xref>]. Mean annual growth increment [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Net growth of adult population [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Coefficients of predator negative growth in Lotka-Volterra model [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Growth per unit time [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>]. &#167;&#167; Par. related to food [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. g gonad [<xref ref-type="bibr" rid="scirp.35705-ref99">99</xref>]. F/K; global [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Probability density of fish length; ration requirement coefficient [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. N˚ of groups [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Par. group or stratum index [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Par. combining mortality and growth effects; observation error; age specific vulnerability to fishing induced mortality [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Index identifying a group of fish tagged and released over a short period of time [<xref ref-type="bibr" rid="scirp.35705-ref151">151</xref>]. Gross food conversion efficiency [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Probability of a fish to be retained by a grid [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Coefficient in Fletcher’s quadratic model; g<sub>1</sub> and g<sub>2</sub> density independent and dependent growth effects, respectively; F/K ratio in the allometric Y/R model; index of gear type [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. The greatest true age group [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Gear type [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>]. To be not confounded with gram [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. γ—Free. &#167;&#167; Par. in total metabolism (T) and weight (W) according to T = αW<sup>γ</sup> [<xref ref-type="bibr" rid="scirp.35705-ref98">98</xref>]. Area successfully searched [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. Shape par. in the Shepherd’s SRR [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Par. in the recruitment function [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Par. in catching power and vessel standardization; tag shedding rate [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Par. in Fletcher’s modification of the Pella-Tomlinson model; exponent in different stock recruitment models; coefficient in Brody model; par. in the Schnute and Schnute-Richards growth models; inflexion in the maturing model; vector of movement and population par. [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Transformation or shape par.; degree of compensation par. in Shepherd’s general SRR relationship [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Fraction of individuals in a stage moving to the next stage; population growth rate [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>]. Shape par. in Schnute-Richards’ growth model [<xref ref-type="bibr" rid="scirp.35705-ref135">135</xref>].</p><p>G—General growth rate at stock level. <sub>a</sub>G absolute; <sub>r</sub>G relative; <sub>i</sub>G instantaneous; <sub>f</sub>G finite; <sub>s</sub>G, specific; <sub>•</sub>G other to be specified. &#167; Stock growth in weight [<xref ref-type="bibr" rid="scirp.35705-ref95">95</xref>]. Instantaneous growth rate [67,76]. Growth survival factor [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. g in [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Specific growth rate. Increase due to growth of individuals [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Par. relating Z/K or Z/H to length and weight [118,119]. &#167;&#167; Par. related to food [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Scalarvalued function [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Cumulative length-distribution function [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Par. in the recruitment function [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Total n˚ of group or strata; true age composition [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Income for the fishing industry; fishing induced mortality [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Natural mortality factor in Pope’s cohort analysis [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Sea area over which egg production is expressed [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Anabolic component [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Probability of moving form one stage to another stage [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>*G—General growth rate at stock level as whole population; for example, in surplus production [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>Γ—Free. &#167;&#167; Index of competition. Notation for the gamma distribution; environmental variable affecting recruitment in semelparous population modelling [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>GI—Gonosomatic (or gonadosomatic) index; ratio between gonadic (ovaries or testis) and body weight. GI<sub>o</sub> whole body; GI<sub>e</sub> eviscerated; <sub>•</sub>GI to be specified in case gonad weight includes also other reproductive annexes (for example, the ovary glands in cephalopods). &#167; Usually it is considered an index of the state of maturity or of the level of sexual activity (especially in females).</p><p>Ger—Gastric evacuation rate. &#167; E [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>GML—Growth-maturity-longevity-plot [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>].</p><p>GOF—Goodness-of-fit [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. &#167; G for the projection matrix method [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>h—Hour [25,109]. &#167;&#167; Time required to capture and consume [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. Par. combining mortality and growth effects; annual harvest rate; time taken by a predator [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>] Exponent in the L<sub>∞</sub> = DK<sup>−</sup><sup>h</sup> relationship [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Instantaeous longline fishing mortality rate [<xref ref-type="bibr" rid="scirp.35705-ref151">151</xref>]. From [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]: height of a fish’s caudal fin; h<sup>2</sup> measure of genetic heritability; squared of caudal fin. Harvest rate related to fishing mortality [<xref ref-type="bibr" rid="scirp.35705-ref84">84</xref>]. Arbitrary increment; coefficient in Fletcher’s quadratic model; derivative of the underlying deterministic growth curve; eigenvector [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. N˚ of age groups; herbivore organisms [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Density dependence or steepness par. in B&amp;H SRR [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. *h—Haul. &#167; h [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>].</p><p>H—Loss rate of marks. &#167;&#167; Weight synthesised per unit surface area in the derivation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Instantaneous (exponential) growth rate [<xref ref-type="bibr" rid="scirp.35705-ref119">119</xref>]. Par. in surplus and Shepherd’s SRR [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Distribution function [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Estimated age composition or percent of total catch [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Par. in the recruitment function [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Prop. of females mating [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Herding effect related par. [<xref ref-type="bibr" rid="scirp.35705-ref137">137</xref>]. Coefficient of anabolism used in the derivation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. Natural mortality factor in Jones’ length-based cohort analysis [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Overall n˚ of hauls [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Probability of dying after being caught (and discarded); matrix related par. [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Evenness and diversity indexes or alternative hypothesis [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Harvest fraction; handling time for a prey [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. General power function [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>]. Hamiltonian in the conditional equation [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>HI—Hepatosomatic index; ratio between liver and body weight. HI<sub>o</sub> whole body; HI<sub>e</sub> eviscerated.</p><p>i—As subscript, generic index to designate stock or site [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>] or group identification [61,65,66]. &#167; Year [<xref ref-type="bibr" rid="scirp.35705-ref129">129</xref>]. For counting items [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. &#167;&#167; Index of total mortality [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. Instantaneous total mortality [<xref ref-type="bibr" rid="scirp.35705-ref120">120</xref>]. Intercept in the generalisation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Mesh opening [<xref ref-type="bibr" rid="scirp.35705-ref81">81</xref>].</p><p>ι (iota)—To not be used in order to avoid confusion with similar symbol.</p><p>I—Ingestion of food and related par. Food consumption in a given period. Coefficient of food utilisation for growth and maintenance. <sub>g</sub>I gross food conversion efficiency. I<sub>S</sub> stock’s feeding requirement (I) in [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. I<sub>dr</sub> daily ration i.e. the amount of food consumed by a fish of a given weight in one day, and often expressed as % of its own weight [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]; I in Ware [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. &#167; Growth efficiency, for example, the ratio between production and food consumption [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. &#167;&#167; Marked specimens [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Par. related to “optimal grouping”; index of cohort [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Money invested in a new boat [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. As subscript, inflexion; groups deriving from cohort stratification; survey index in ADAPT approach; integral [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Index of relative abundance (68,70). Income [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>*I—Separation Index [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. &#167; SI [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>].</p><p>∞—Infinite. The upper limit which can (probabilistic) or cannot (asymptote; integral) be touched by the considered par. In the asymptotic case, it might characterise the maximum size towards which a fish (or a stock; [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>] would grow if it could assimilate energy at the maximum possible rate throughout its life.</p><p>IALK—Iterate age length key [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>j—Juvenile. Fish which has not reached the maturity condition. j<sub>a</sub>, always, which maintain non developed gonads in spite of a size larger than A<sub>m</sub> [<xref ref-type="bibr" rid="scirp.35705-ref152">152</xref>] &#167; <sub>j</sub> as subscript in Walters et al. [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Usually in Mediterranean stocks, they include the recruits or the young(est) of the year (YOY). Immature. &#167;&#167; Location or area [<xref ref-type="bibr" rid="scirp.35705-ref94">94</xref>]. Time interval [86,97]. N˚ of par. [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. For counting items [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. Index for predators or consumers [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. A given gear [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Different periods of life; as subscript, generic index or group identification [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>J—Juvenile at stock level. &#167;&#167; N˚ of recapture period [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Time intervals [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. Jaws size in urchins [<xref ref-type="bibr" rid="scirp.35705-ref121">121</xref>]. Age at first capture; yield [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Jacobian matrix; n˚ of jobs in fishing industry [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. An alternative to a given gear (73). N˚ of length interval; total value function [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>k—The coefficient in the allometric length-weight relationship according to w = kl<sup>b</sup>. k<sub>e</sub> and k<sub>10</sub> after ln and log transformation. &#167; C in [118,119]. &#167;&#167; Catchability in tagging studies [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. Cons. in surplus model [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. Terms which do not contain F or M in virtual population analysis [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>]. Destruction per unit weight in the derivation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Rate of deceleration in growth increment [<xref ref-type="bibr" rid="scirp.35705-ref77">77</xref>]. N˚ of discrete sampling occasion in Jones [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. New age or length at capture related index [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Age at (of full) recruitment; discount rate; ratio of the size-specific mortality to the size-specific growth rate [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Youngest possible age at recruitment [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. As k<sub>a</sub> and k<sub>t</sub> growth coefficient related to mean length at age and length increment (tagging) analysis [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Cohort index [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Carrying capacity; cost of a new boat [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Identifies size-at-release class of fish from a given group [<xref ref-type="bibr" rid="scirp.35705-ref151">151</xref>]. Coefficient of catabolism or n˚ of par. [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. Time at recruitment to the adult stage [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Often employed to represent the growth coefficient in the VBGF [70,87]. Par. in effort standardisation; intrinsic growth par. analogous to r in surplus models [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Sampling effort factor; k1 and k2 cons. relating mode/spread with mesh size [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Catch per unit capital [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Cohort Index in Extended Survivors Method; coefficient of proportionality between Y and f in case of cons. density of fish; n˚ of prey categories [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Cons. in the SRR and (as carrying capacity) production model [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>]. N˚ of par. estimates in a given procedure [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. k<sub>1</sub>, k<sub>2</sub>,… k<sub>n</sub> growth coefficients or rate in different compared models; n˚ of estimable par. in AIC computation [<xref ref-type="bibr" rid="scirp.35705-ref135">135</xref>].</p><p>κ—To not be used in order to avoid confusion with similar symbol. &#167;&#167; Eigenvector; difference between intrinsic rate and exit rate in migration model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Log of spawning level; curvature par. in different (growth and maturing) model; identifying the Ricker’s conventional Brody coefficient in the VBGF; coefficient in Brody model [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>K—Rate of curvature [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>]. Curvature par. [66,72, 74,153] or coefficient in the monomolecular or inverse exponential equation VBGF [70,117,154] and its allies. It determines the rate at which the asymptotic-infinite size is approached. &#167; von Bertalanffy growth par. [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>] or coefficient [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Par. (=k/3) in the length based derivation of VBGF (91). Rate of change in length/weight increment; growth rate in the VBGF; Brody’s (length) or Putter’s (weight) coefficient [56,58] Stress factor [71,138]. Par. of the von Bertalanffy length equation [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>].The Brody’s denomination in the VBGF is also adopted by other Authors [25,65,68]. Growth completion rate [<xref ref-type="bibr" rid="scirp.35705-ref155">155</xref>]. Growth rate [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]&#167;&#167; Total (cumulative) catch in tagging studies [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. Efficiency of utilization of food [<xref ref-type="bibr" rid="scirp.35705-ref98">98</xref>] = j-1 in Jones [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>], recalling the Robson and Chapman classification. Par. in gear saturation modelling [<xref ref-type="bibr" rid="scirp.35705-ref156">156</xref>]. Drag coeffcient [<xref ref-type="bibr" rid="scirp.35705-ref106">106</xref>]. Par. in surplus and Shepherd’s SRR models [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Selectivity factor [<xref ref-type="bibr" rid="scirp.35705-ref126">126</xref>]. K<sub>n</sub> gross production efficiency of food [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Oldest possible age at recruitment [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Index of food abundance in extended stock recruitment relationship [<xref ref-type="bibr" rid="scirp.35705-ref157">157</xref>]. Total n˚ of cohort [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Cumulative catch [in Leslie and De Lury model; 25] and fleet related par.s [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Growth-survival-catch analogous to the catch factor of closed populations [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Upper limit or carrying capacity; matrix related par. [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Par. in predator model to estimate natural mortality [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]. Size of the fishing fleet; threshold (biomass) level in the SRR relationship [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>*K—Threshold biomass in surplus production model [upper limit or carrying capacity; 65] and different stockrecruitment relationships (above which the relationship departs from linearity ([<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].<sub>•</sub>l—Individual body length as effective or index of the whole fish extension [total in 11]<sub>e</sub>l extreme (total with the caudal tips joined). <sub>n</sub>l natural (total with tail tips in natural position). <sub>f</sub>l fork. <sub>s</sub>l standard. <sub>c</sub>l carapace (crustaceans). <sub>d</sub>l dorsal mantle (cepahalopods). <sub>h</sub>l height. l recently killed. l<sub>•</sub> defrosted. l<sup>•</sup> other to be specified (see also age for other subscripts). &#167; Length at 50% of release [<xref ref-type="bibr" rid="scirp.35705-ref125">125</xref>]. &#167;&#167; l<sub>x</sub> probability of living at age x [<xref ref-type="bibr" rid="scirp.35705-ref121">121</xref>]. l<sub>t</sub> landing tax [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. l<sub>y</sub> last year of fisheries data [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Annual survival rate [65,70] after natural mortality [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Early life survival from the egg stage to recruitment; annual survival from natural sources; index for length interval [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>•<sub>l</sub>—Body component (organ, appendix etc) length.</p><p>l—Ultimate significant contribute to the fishery. &#167; Maximum age [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>]. &#167;&#167; Par. relating variance and n˚ of observations [<xref ref-type="bibr" rid="scirp.35705-ref130">130</xref>]. Fraction of the catch inspected for tags [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. Par. related to the growth in yield computation [<xref ref-type="bibr" rid="scirp.35705-ref120">120</xref>]. Length in the Putter expression of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Coefficients which takes account of the difference in summer and winter feeding [<xref ref-type="bibr" rid="scirp.35705-ref99">99</xref>]. Fecundity per recruit; cons. relating the resulting recruitment from a given spawning biomass [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Annual growth rate in Schaffer’s formula [<xref ref-type="bibr" rid="scirp.35705-ref121">121</xref>]. Importance of residual [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Convenience notation to relate two growth expressions for tagging data [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Max par. in fish vision [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. Probability that a tag is lost due to tag shedding or tag-induced mortality [<xref ref-type="bibr" rid="scirp.35705-ref151">151</xref>]. Coefficient of variation of length at age [<xref ref-type="bibr" rid="scirp.35705-ref153">153</xref>]. Poisson mean [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Term corresponding to F in stochastic model; attack rate; par. in Gompertz’s differential growth derivation; eigenvalue; penalty weight; ratio of variance [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Intercept in linear weight at age plots; average per capita encounter rate [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Finite rate of population growth [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>]. Theoretical initial growth rate in Gompertz’s model [<xref ref-type="bibr" rid="scirp.35705-ref135">135</xref>]. Adjunct variable [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>log—10 based logarithm [66,70] &#167; log<sub>10</sub>, log, lg.</p><p>ln—e based logarithm [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>] &#167; log<sub>e</sub>.</p><p>L—Length (generic) at stock level [67,70]L<sub>m</sub> at 50% sexual maturity [70,113]. L<sub>rt</sub> at 50% of retention. L<sub>ml</sub> minimum landing length. See l (individual length) and A (age) subscripts for other specifications. &#167; N˚ of length class [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Mean length of a fish at age t [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] L<sub>50%</sub>, (l<sub>50</sub> in 73) length at which 50% of fish are retained [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>] MLS minimum landing size [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>] &#167;&#167; Catch or landings; production in weight [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]; limiting population [<xref ref-type="bibr" rid="scirp.35705-ref129">129</xref>]. t<sub>L</sub> longevity [<xref ref-type="bibr" rid="scirp.35705-ref112">112</xref>]. Penalty weight [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Likelihood [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Depth [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Length of the search along the transect; cumulative survival; n˚ of individuals measured for length; observed and true length frequencies; likelihood; instantaneous rate of tags shedding [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. As subscript, <sub>L</sub>, also denoted fish caught and landed [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>L<sup>∞</sup>—Asymptotic length. Length to which the curve approaches closer and closer as the independent par. Becomes extremely large (→∞) or extremely small (→ −∞) [<xref ref-type="bibr" rid="scirp.35705-ref30">30</xref>] l<sub>∞a</sub> mean length of “old fish”, where old means of an age beyond which the mean length at age does not increase appreciably [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Mean length of infinitely old fish [<xref ref-type="bibr" rid="scirp.35705-ref153">153</xref>]. Length at maximum age [t<sub>∞</sub> in65]. In the VBGF, the size at t = ∞ ]70] or that an average fish would achieve if it continued to grow indefinitely according to the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref13">13</xref>], without touching it (L<sup>∞ </sup>&gt; L<sub>mxe</sub>). &#167; Usually reported as L<sub>∞</sub>. The same symbol (L<sup>∞</sup>) was recommended for VBGF by ICNAF [<xref ref-type="bibr" rid="scirp.35705-ref47">47</xref>]. Limiting size [<xref ref-type="bibr" rid="scirp.35705-ref11">11</xref>]. Maximum expected length [<xref ref-type="bibr" rid="scirp.35705-ref158">158</xref>]. Maximum possible length [154,72]. l<sub>∞•t</sub> maximum length achieved in a population where the subscript t refers to tag data analysis [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. L<sub>inf</sub> in Rosenberg and Beddington [<xref ref-type="bibr" rid="scirp.35705-ref115">115</xref>]. Infinite; the mean length of very old (strictly speaking, infinitely old) fish” [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>]. Sometimes it is assumed [in Elasmobranchs VBGF modelling;159] or mistaken [<xref ref-type="bibr" rid="scirp.35705-ref21">21</xref>] for the largest observed size for the species (i.e. L<sup>∞</sup> ≡ L<sub>max</sub> approximation [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>].</p><p>L∞—Pristine infinite. The mean length the fish of a given stock would reach if they were to grow forever [66, 72]. Mean size according to a probabilistic distribution function [<xref ref-type="bibr" rid="scirp.35705-ref160">160</xref>]. &#167; Mean length of oldest specimens estimated in the pristine condition. In the VBGF, L∞ &lt; L<sub>mxe</sub>.</p><p>L<sub>∞</sub>—Actual infinite. Mean size of oldest specimens esimated in the exploited condition. Mean size according to a probabilistic distribution function [<xref ref-type="bibr" rid="scirp.35705-ref160">160</xref>]. &#167; L<sub>n</sub> successsive (pseudo-) infinite lengths in seasonal VBGF [<xref ref-type="bibr" rid="scirp.35705-ref161">161</xref>]. In the VBGF, L<sub>∞</sub>&lt; mxe.</p><p>L<sub>mx</sub>—The present maximum size recorded for the investigated stock. L<sub>mx</sub><sup> </sup>ever recorded; L<sub>mx </sub>estimated according to a method to be specified such as mean of n extremes, 95<sup>th</sup> percentile, extreme values theory etc LC50—Median lethal concentration [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>].</p><p>LFA—Length frequency analysis [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>Λ (lambda)—To not be used in order to avoid confusion with similar symbol. &#167;&#167; Test statistic [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Diagonal matrix [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p><sub>•</sub>m—Mesh [66,68,76,125,126] Mesh size [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. The size of hole in a fishing net [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>] and related par. <sub>d</sub>m diamond or <sub>q</sub>m squared; m<sub>b</sub> bar, m<sub>s</sub> stretched size. &#167; Codend mesh remain open [<xref ref-type="bibr" rid="scirp.35705-ref148">148</xref>]. &#167;&#167; Σm sum of the weights of all fish which have died from natural causes during the year [<xref ref-type="bibr" rid="scirp.35705-ref88">88</xref>]. Fraction of fish removed in 1 year [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>] Bertalanffy anabolism exponent in the generalisation of the VBGF; slope in Ford-Walford plot [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Rate of change between metabolic rate and weight [<xref ref-type="bibr" rid="scirp.35705-ref154">154</xref>]. Prop. of larvae [<xref ref-type="bibr" rid="scirp.35705-ref145">145</xref>]. Shape par. in the Pella and Tomlinson’s model; M/K (76). N˚ of marked specimens; cons. in the Lotka-Volterra equations [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. M/K (Conditional fishing mortality rate [107). As subscript, marked specimens [<xref ref-type="bibr" rid="scirp.35705-ref93">93</xref>]. Generic slope in linear regression; arbitrary exponent in the Pella and Tomlinson’s model; natural mortality rate; maximum age in multispecies analysis [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Maximum flow between preys and predators/consumers [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. K/Z [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Median; maximum productivity in surplus models; estimated variance related par.; m<sub>(x)</sub>, probability of maturity; males; M/K ratio; n˚ of marked fish recaptured; index of consumption of species I by species j [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] Maintenance and depreciation [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Conversion for prey mass to energy; fecundity [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. As subscript, marking related par. [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. To not be confounded with meter.</p><p>♂—Males [72,87]. &#167; M, m.</p><p>μ—Free. &#167;&#167; Mortality rate [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. Population mean [<xref ref-type="bibr" rid="scirp.35705-ref130">130</xref>]. N˚ of tagged fish recaptured [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. Par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Prop. in length frequency analysis [121,162]. Cons. relating the spawning biomass resulting from a given recruitment [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Annual exploitation fraction [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Food size preference coefficient [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Fraction of the catch removed [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Mean length in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Term corresponding to M in stochastic model; annual exploitation fraction (C/N); mean; maximum growth rate [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Mesh size [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Exploitation rate [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>mp<sub>a</sub>—Mean parental age, the average n˚ of progeny produced by a females during its life weighed by the different age class. &#167; Most suitable for iteroparous species. As the mean fecundity, it is a par. not simple to estimate [163; pag. 128].</p><p>M—Instantaneous rate of natural mortality, where “natural” refers to all causes of mortality except fishing [61,63-65,67,74,76,86,117,130]. If not specified (see below), it indicates the average (overall weighed) M over the range of age groups which can be considered fully represented in the samples. M<sub>∞</sub> infinite mortality (≈ 0), or mean of infinitely old and big fish [<xref ref-type="bibr" rid="scirp.35705-ref153">153</xref>] to which approach the M (assuming no senescence); it is analogous to Gulland [<xref ref-type="bibr" rid="scirp.35705-ref45">45</xref>] M' limiting value. M<sub>j</sub> juveniles. M<sub>pa</sub> parental (adults). M<sub>bur</sub> bursts, the high M values in early period such as eggs and larvae lifetime [<xref ref-type="bibr" rid="scirp.35705-ref164">164</xref>]. M<sub>asy</sub> the mathematic theoretical (lower) asymptotic natural mortality [M<sub>a</sub> in163]. M<sup>asy</sup> the asymptotic upper biological mortality to which tend the oldest specimens of a stock. M↨ array of values according to a model or equation to be specified. M<sub>Δt</sub> phase mortality, defined as the product MΔt (in the presence of fishing, ZΔt) and represents the cumulative mortality which occurs in the time interval under consideration [<xref ref-type="bibr" rid="scirp.35705-ref165">165</xref>] M* the combination between M and the instantaneous rate in tags shedding [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. M<sub>0</sub> and M<sub>1</sub>, M<sub>2</sub> etc., natural mortality excluding predators [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>], and other forms of natural mortality, for example, in multispecies VPA [68,70]. &#167; M<sub>n</sub> [<xref ref-type="bibr" rid="scirp.35705-ref95">95</xref>]. M<sub>asy</sub> is a mathematical par. without any biological meaning (may also assume negative values). M% in % as recorded in aquaculture experiments [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. M* due to predation by marine mammals [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. M = + ∞ catastrophic mortality at the end of lifetime [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. &#167;&#167; Maximum population which the environment will support under average conditions and with no fishing [<xref ref-type="bibr" rid="scirp.35705-ref129">129</xref>]. Metabolism par. in the “surface law” or “two-thirds rule” or “Rubner’s rule” [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. t<sub>M</sub> age at reform; X<sub>M</sub> at MSY [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. N˚ of fish in a sample [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. N˚ of predators [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Projection matrix [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. ). Mature specimens [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]. Metabolism term or catabolic losses [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>MC—Migration coefficient [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>MPA—Modal progression analysis.</p><p>*MPA—Marine protected areas. &#167; MPA [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>].</p><p>MS—Mean square [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. &#167; MSE mean square error [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. &#167;&#167; It can be confounded with the Maximum Sustainable Economic Yield [MSE in 74].</p><p>MSY—Maximum sustainable yield [65,74,117] &#167; At equilibrium [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>MSEY—Maximum sustainable economic yield [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. &#167; MSE [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. MEY [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>].</p><p>n—Generic n˚ of specimens or items to be specified [68,70] &#167; As superscript, indicates the order of a moment [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. &#167;&#167; Exponent in the allometric W = cl<sup>n</sup> [<xref ref-type="bibr" rid="scirp.35705-ref77">77</xref>] Shape par. in Richard’s growth curve [<xref ref-type="bibr" rid="scirp.35705-ref121">121</xref>]. Trophic level; year [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Conditional natural mortality rate [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>]. N˚ of encounter; shape par. in Pella-Tomlinson model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>υ—To not be used in order to avoid confusion with similar symbol. &#167;&#167; Fraction of the total mortality [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Par. in Schnute-Richards growth model; vector of par. (general and related to mark recovery) [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Selection par. related to haul [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Par. in Schnute-Richards’ growth model [<xref ref-type="bibr" rid="scirp.35705-ref135">135</xref>].</p><p>N—N˚ [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>] of fish [25,130] in a homogeneous group [61,68] N˚ of survivors of a cohort [70,76] Population in n˚ [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. N<sub>0</sub> total at the beginning of a given year. &#167; Initial population [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>] in n˚ [<xref ref-type="bibr" rid="scirp.35705-ref89">89</xref>] N˚ of fish of a given cohort alive at age a; n˚ marked and total recaptured [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167;&#167; Par. related to Hill diversity [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>] N˚ of schools; egg production [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Sample size in n˚ [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>o—To not be used in order to avoid confusion with similar symbol. &#167;&#167; Term in stochastic mortality model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>ω—Gallucci and Quinn’s [<xref ref-type="bibr" rid="scirp.35705-ref166">166</xref>] growth performance index (KL<sub>∞</sub>). &#167;&#167; Fraction of the total biomass due to newly recruited fish [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Weight at age ratio [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>O—N˚ of dead fish in a given time interval. O<sub>Z</sub> dying of total causes. O<sub>F</sub> dying of fishing (C plus n˚ of fish dying for collateral effects of fishing). O<sub>M</sub> dying of other causes than fishing (all natural causes). O<sub>Mp</sub> predators. O<sub>Md</sub> diseases. &#167; Estimate of total fish taken [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. &#167;&#167; Coefficient related to the age at maturity of a cohort [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Objective function [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Mature ogive [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]</p><p>OI—Omnivore index [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>Ω—Expanding term or factor [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Summation cons. in year class weight computation. &#167;&#167; Yamanaka’s yield function [<xref ref-type="bibr" rid="scirp.35705-ref120">120</xref>]. Period in seasonal growth models [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Region bounded by [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>p—Prop. [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>] of related, but not dependent variables. p<sub>r</sub> retained in the cod-end [<xref ref-type="bibr" rid="scirp.35705-ref81">81</xref>] p<sub>m</sub> mature. p<sub>♂</sub> of males over females. p<sub>♀ </sub>females over males. p<sub>♀s</sub> females over sexed specimens. p<sub>m♀s</sub> mature females over mature sexed specimens (operational sex ratio; [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]&#167; S<sub>R</sub> sex ratio [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Prop. [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Prop. of ration (72). Probability [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Probability in selection curves [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Generic prop. [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] Prop. of mature at age [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>] &#167;&#167; Instantaneous rate of fishing mortality [89,120]. Annual mortality rate (1-exp-Z) [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>]. Index of intensity of exploitation or mortality owing to catches; standard fishing effort [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. Cons. of proportionality in the derivation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Term for correcting injested to utilizable energy [<xref ref-type="bibr" rid="scirp.35705-ref98">98</xref>]. t<sub>p</sub> age at reruitment in the fishing ground [<xref ref-type="bibr" rid="scirp.35705-ref77">77</xref>]. Assimilation factor [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. Duration of each recapture period in Jones [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Movement probability in diffusion model [<xref ref-type="bibr" rid="scirp.35705-ref141">141</xref>]. Price [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Weighting factor [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Landed price; probability of moving from an area to the other; movement rate; residence prop.; generic par. in GLM; productivity in multistage SRR; probability of encounter-chase-capture [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Probability that an individual is caught in stochastic mortality model; model par.; n˚ of tests; generic fraction; true prop. of fish by length interval; par. in the (proportional allocation) age sample size determination; probability of finding a marked member at time t; prop. Mature at age [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Relative fishing effort [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Coefficient related to food energy; index of predator type; predation [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Net price per unit weight [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. To be not confounded with the probability level in statistical inference.</p><p>π—3.14 [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. &#167;&#167; π<sub>a</sub> prop. of each cohort which recruits at age a; fixed prop.; harvest rate [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Fraction of total recruitment (64). Fishing mortality hazard par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Fraction of total recruitment of a given cohort or at the start of a year (exploitation fraction) [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>ψ (psi)—To not be used in order to avoid confusion with similar symbol. &#167;&#167; Generic par. [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>] N˚ of tidal cycle per day [145in key papers]. The mean direction of movement [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Arbitrary reference age in Francis VBGF reparameterization [<xref ref-type="bibr" rid="scirp.35705-ref101">101</xref>]. Moment-generating function; monotically decreasing function of r; instantaneous rate of movement from region i to region j [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Ratio between C and pristine biomass [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>P—Production [67,70,82,83,167], the quantity of overall (dead and still alive) biomass produced during the interval under consideration. P<sub>n</sub> net production, amount of living matter [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>]. &#167; Population of usable size [<xref ref-type="bibr" rid="scirp.35705-ref95">95</xref>]. Population size [<xref ref-type="bibr" rid="scirp.35705-ref56">56</xref>]. Biomass of adult stock [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Latent productivity; dynamic resource (or prey) term [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Productivity of the prey’s food resource [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Cons. of the production model generalising the model [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>]. &#167;&#167; Prop. of tagged [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. Survival rate [<xref ref-type="bibr" rid="scirp.35705-ref130">130</xref>]. Population size [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. P<sub>W</sub> biomass in weight [<xref ref-type="bibr" rid="scirp.35705-ref77">77</xref>]. P<sub>W</sub> average population or standing stock in weight [<xref ref-type="bibr" rid="scirp.35705-ref94">94</xref>]. Pressure (m off the bottoms) in Harden Jones [<xref ref-type="bibr" rid="scirp.35705-ref146">146</xref>]. P<sub>e</sub> n˚ of eggs spawned [<xref ref-type="bibr" rid="scirp.35705-ref145">145</xref>]. Rate of growth; price; probability [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Prop. [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Previously exploited fish in Schnute [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>] model. Availability [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Points in a score (or objective) function; prop.; aggregate productivity in multistage SRR [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Probability of obtaining a catch distribution in stochastic mortality model; fishing power; ratio of catchability; average egg production per day; probability; prop. of individuals in size class [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Prey biomass and egg production in n˚ [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. PM as prop. of mature [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]. Population; fish price; generic par. [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Probability of capture or of occurrence [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Probability of remaining in the same stage [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>]. *P—Parental, the non juvenile component of a stock. *P<sub>m</sub> “mature” fish which are almost mature or fully mature. *P<sub>s</sub> spawners. *P<sub>a</sub> adults, i.e. fish which have reached the capacity to reproduce independently from their present contribute to reproduction (i.e. including abortive fish).</p><p>Π—Free. &#167; To not be confounded with “product”.</p><p>Ψ—Free. &#167;&#167; Dummy time variable. Function [76,96]. Natural survival rate; elasticity (sensitivity) [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>P/B—Production biomass ratio [70,167]. &#167; Turnover rate [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Equivalent to Z, under more circumstances [70,167].</p><p>PF—Power factor [cfr Fig. 1 in 34]. Fishing power. The relative performance of each vessel computed by applying a specific equation; for example, PF = cons. *(vessel length)<sup>n</sup>. &#167; P, P.F., P<sub>i</sub> and Q<sub>j</sub> for power factor of the ith vessel and jth location [<xref ref-type="bibr" rid="scirp.35705-ref168">168</xref>].</p><p>PDF—Probability density function [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>q—Catchability [65,67,70,74,76,86,94,97,107,117,169]. Coefficient of proportionality between F and f (specified for the f used). q<sub>f</sub> the stock fraction taken by 1 unit of effort (usually &lt; 0.1). See “effort” for other speciications. &#167; The fraction taken by 1 unit of fishing effort [<xref ref-type="bibr" rid="scirp.35705-ref122">122</xref>]. Efficiency of fishing; efficiency of each fishing boat [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Different catchability in Jennings et al. [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Availability [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. q* in Lleonart [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>]. &#167;&#167; Instantaneous rate of natural mortality [89,120]. Total mortality (127]. Coefficient in the length weigh relationship [<xref ref-type="bibr" rid="scirp.35705-ref122">122</xref>]. Index of natural mortality [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. Cons. of proportionality in the derivation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Different par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. N˚ of par. [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Prop. of ration [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Essentially a cons. of proportionality [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Density independent mortality [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Complement to p in stochastic mortality model; model par.; time (years) range; calibretion coefficient in ADAPT [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Sub sampling fraction [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Recruitment ratio in [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Quarter or any time period in fish migration [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Q—Physiological-temperature related coefficients; mainly referring to the correction factor such as Q<sub>01</sub> [<xref ref-type="bibr" rid="scirp.35705-ref98">98</xref>] or Q<sub>10</sub> (Arrhenius) rule [70,103]. &#167;&#167; Fishing effort efficiency [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>]. N˚ of fish caught per moment [<xref ref-type="bibr" rid="scirp.35705-ref123">123</xref>]. Fraction of fish taken from a cohort [<xref ref-type="bibr" rid="scirp.35705-ref156">156</xref>]. Weight of prey consumed [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Gill-net catch per lift; harvest [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Fish group in Schnute [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>] model. Q and Q/B amount of food consumed per unit weight of an age structured population of fish generally expressed on an annual base [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. Par. (difference between maximum and minimum age considered) in Shepherd’s lengthcomposition analysis [70,115]. Index of biomass concentration in the Csirke’s SRR [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>]. Probability or prop. in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Par. in the Charnov and Berrigan K = Q(L<sub>∞</sub>)<sup>–h</sup> invariant [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>]. Quantity [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Total consumption rate [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. One of the par. defining the REP (replication estimate of dispersion) par. [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Mean catchability; par. related to Fletcher’s quadratic model [<xref ref-type="bibr" rid="scirp.35705-ref6">6</xref>]. Amount of food consumed [70,109]. Consumption and, as Q*, upper limit to fleet catching capacity [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Par. in surplus production modelling; catchability at fleet level [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Capturability coefficient [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>]. In management designs, Quota, a share of total allowable catch in weight [22, 65,68,70].</p><p>QO<sub>2</sub>—Weight-specific oxygen uptake [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>].</p><p>r—Product-moment (Pearson) and (r<sup>2</sup>) determination coefficient [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. &#167; R<sup>2</sup> [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. &#167;&#167; Exponent in compound interest equation as applied to stock weights [<xref ref-type="bibr" rid="scirp.35705-ref105">105</xref>]. Year [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>]. N˚ of tags recovered [27,97]. Distance [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Different par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Accessibility [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Multipliers in yield per recruit equations [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Average of some rate; intrinsic rate [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Optimal length class interval; prop. of ration [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Age at recruitment; survival probability [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Relative recruitment rate; uniform random (0 - 1) n˚; age at recruitment in multispecies analysis [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Coefficient in Jones and Johnston [<xref ref-type="bibr" rid="scirp.35705-ref99">99</xref>] growth, reproduction and mortality analysis. Instantaneous growth par.; probability that an individual is alive at time t in stochastic mortality model; region; model par.; intrinsic growth par. in surplus models; r<sub>1</sub> and r<sub>2</sub> density independent and dependent natural mortality effects, respectively; par. in Francis’ growth model; (knife edge) recruitment age; sequential observation of biomass; logarithmic (median and average) growth rate of a population; the first age group; prop. of fish of length l and age a; par. in the age sample size determination; generation length in semelparous (once-breeding) population modelling [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Reciprocal of catchability [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>*r—sIntrinsic rate of initial population growth; the rate showed at very low abundance (assuming no depensation). &#167; r intrinsic rate of growth [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. r<sub>m</sub> intrinsic rate of growth of a stock [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. Pollard’s Malthusian par. in Quinn and Deriso [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. r<sub>pop</sub> [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>ρ—Ratio [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>] of dependent variables. ρ<sub>N</sub> ratio of surviving (absolute rate of surviving per year). ρ<sub>Z</sub> ratio of complementary surviving (absolute rate of total mortality per year). ρ<sub>GR</sub> part of the metabolic energy available for growth and reproduction. ρ<sub>E</sub> part of the reproductive energy used for zygotes formation [<xref ref-type="bibr" rid="scirp.35705-ref167">167</xref>].&#167; Tags reported/ tags captured ratio [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. S, A. ρ' exchange ratio per tidal cycle [<xref ref-type="bibr" rid="scirp.35705-ref145">145</xref>]. Recruit per spawner ratio [<xref ref-type="bibr" rid="scirp.35705-ref84">84</xref>]. &#167;&#167; Probability of individual fish to be available [<xref ref-type="bibr" rid="scirp.35705-ref122">122</xref>]. Par. related to food [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Fluid density [<xref ref-type="bibr" rid="scirp.35705-ref106">106</xref>]. Slope in the Ford-Walord plot [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Ford’s growth par. (coefficient in 67]; correlation factor; inverse of the capture probability [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>R—Recruitment related par. [25,61,63-65,67,70,76,86, 95,107,127]. N˚ of recruits [<xref ref-type="bibr" rid="scirp.35705-ref89">89</xref>]. R<sub>af</sub> to the area interested by fishery. R<sub>gf</sub> to the gear used by fishery. R<sub>X</sub> effective recruitment (the total n˚ of fish recruited in one year from X year-classes. &#167; Whatever recruitment by movements in to the region fished or by change in size or behaviour [56; page 40]. R as recruits abundance [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Recruitment to the exploitable phase [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. &#167;&#167; Net radius [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Food intake [<xref ref-type="bibr" rid="scirp.35705-ref98">98</xref>]. Food consumed by a species [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Standard vessel [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Rate of respiration per unit area [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Ration; rectangular distribution [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. N˚ of tags released; n˚ of boat retired [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. R<sub>0</sub> net reproductive rate [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. R<sub>d</sub> daily ration [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. Variance matrix [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Cons. ratio of change in population n˚ or Malthusian par.; life-time egg production; lifetime reproduction [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Current observation in Bayesian statistics [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Revenue from fishing; food ration; radius of an hard part in backcalculation; inherent riskiness in fish foraging and habitat choice [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. RL—Reproductive load [<xref ref-type="bibr" rid="scirp.35705-ref145">145</xref>]. The ratio between the length at maturity (L<sub>m</sub>) and L<sub>∞</sub> [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>].</p><p>RP—Recruitment pattern.</p><p>RV—Reproductive value [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>RSS—Residual sum of square [65,67].</p><p>s—Sampling standard deviation and (s<sup>2</sup>) variance [25, 70,107] &#167; s.d. and s.e. [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. S.D. and S.E. [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. SD [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. τ in [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. &#167;&#167; Total survival fraction [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>]. N˚ of tags reported [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. Area of surfaces involved in anabolic process in the derivation of the VBGF [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. s<sub>0</sub> time when the organism begins to react to the net’s approach [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Selectivity [76,86,107]. Oldest exploited age class [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Annual survival rate from natural mortality; survival rate; responsiveness of a fleet; speed of a vessel [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Surface area of a fish’s caudal fin [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>]. Gear selectivity; ratio between L<sub>s</sub>, earliest age at spawning, and asymptotic length; gear selectivity; district-specific catches vector in “run reconstruction” [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Index for prey species in multispecies VPA; stage in Individual Based Models; as subscript, stochastic [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Selectivity; exploitation pattern [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>]. To not be confounded with the unit time second.</p><p>σ—Stock standard deviation and σ<sup>2</sup> variance [65,86] &#167; SE<sup>2</sup> [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167;&#167; Fraction of population at some stage or condition [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Fraction of the fish population that survives mortality by natural causes [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Food size preference coefficient [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Annual survival rate [<xref ref-type="bibr" rid="scirp.35705-ref84">84</xref>]. Larval temporal “width” in the Cushing’s match/mismatch hypothesis [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Stage [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>S—Stock size in n˚. S' unit stock. S<sub>0</sub> the pristine level. S<sub>∞</sub> asymptote size in n˚, the level to which an unexploited stock tends. &#167; Catchable stock in weight [<xref ref-type="bibr" rid="scirp.35705-ref88">88</xref>]. Escarpment biomass; adult abundance [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Spawning stock [65,157], usually as proxy of egg production [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. N as stock size in n˚ [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>]. Post harvest biomass in delay difference model; spawning biomass; n˚ of sets [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Stock size in n˚ or biomass [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. (Standing) stock as an (homogeneous) group of fish which occupy a given area in a given period, which are subject to the same opportunities of growth and reproduction and to the same risks of natural and fishing mortality [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. The unit stock represents a stock which can be kept unitary from the point of view of fishing when the assessments carried out on the basis of this assumption does not give contrasting results with the real situation [24,30,42]. Both terms are often synonym with assessment/management unit, even if there is migration of the same species to and from adjacent areas. “Stock let”, S<sub>•</sub>, is used in case of short living species such as most cephalopods [<xref ref-type="bibr" rid="scirp.35705-ref110">110</xref>]. &#167;&#167; Selection function [<xref ref-type="bibr" rid="scirp.35705-ref122">122</xref>]. Speed of the (fishing boat) ship [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Competition coefficient [<xref ref-type="bibr" rid="scirp.35705-ref131">131</xref>]. Partial recruitment factor [<xref ref-type="bibr" rid="scirp.35705-ref85">85</xref>]. Squared deviations [<xref ref-type="bibr" rid="scirp.35705-ref141">141</xref>]. Fishing mortality subdivisions; S<sub>R</sub> sex ratio [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. (Generic individual) length or weight size [71,121]. Selectivity; recruitment; survival rate [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Index of samples or cruises; standard deviation of a distribution [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Survival rate [86,107]. N˚ of sets; natural survival rate [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Survival fraction over one year; S<sub>0</sub> early life survival; average size of a school; size of any hard body structure uses for back calculation; escarpment of adults from the fishery [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. From Jennings et al. [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. species richness (n˚ of species), survivorship, scale radius, spawner abundance, and escarpment related par. Prop [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]. Swimming speed; fishing mortality on age group in the separable VPA; index for predator species in multispecies VPA; species-specific selection pattern; score; strategy vector in Individual Based Models; measure of suitability; coefficient in the logistic; for example, the ML<sub>50%</sub> maturity estimation [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>*S—Generic score, such as the S function in Shepherd’s method [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. &#167; S [66,108]. &#167;&#167; N˚ of surviving fish after a certain time period [66,108].</p><p>SF— Selection factor [66,74] The ratio between the 50% of entry to capture and mesh size. &#167; S.F. [<xref ref-type="bibr" rid="scirp.35705-ref50">50</xref>]; s.f. [50,126].</p><p>SR—Selection range [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. The size range in which the probability of capture varies. &#167; sr [<xref ref-type="bibr" rid="scirp.35705-ref81">81</xref>]. &#167;&#167; To not be confounded with the reversed logistic curve [SR in 74].</p><p>SS—Sum of squares [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. &#167; SQ [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>].</p><p>ST—Steady state, situations in which all the demographic processes (recruitment, growth and mortality) are cons. along the time (deterministic models) or the same processes are randomly varying in time without no trend (stochastic models). &#167; One of the more common hypotheses in classic fisheries science and the most criticised assumption nowadays [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>].</p><p>St<sub>c</sub>—Stomach contain in weight. &#167; F [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>SPR—Spawning stock-biomass per recruit [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>SRR—Stock-recruitment relationships [11,70,117]. &#167; Recruitment curve as a graph of recruits (Y ax) against spawners [<xref ref-type="bibr" rid="scirp.35705-ref56">56</xref>]. S/R [27,74]. S-R [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>].</p><p>SSB—Spawning stock biomass [70,117] &#167; SP [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. SB spawning biomass [<xref ref-type="bibr" rid="scirp.35705-ref104">104</xref>].</p><p>Σ—Summation sign [65,71]</p><p>t—Time [63,76]. Time in month [<xref ref-type="bibr" rid="scirp.35705-ref61">61</xref>]. t<sub>0</sub> cons. that adjust the time scale to an origin at the inflexion point of a curve [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>] t<sub>h</sub> at hatching. t<sub>s</sub> sets the beginning of sinusoidal growth oscillating with respect to t = 0 (72) in the seasonally version of the VBGF (also summertime; 74). As subscript, tagging related par. [<xref ref-type="bibr" rid="scirp.35705-ref151">151</xref>]. Time or phase shift according to Jennings et al. [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>] and Quinn and Deriso [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>], respectively. t<sub>z</sub> origin of the VBGF in calendar time expressed as fraction of a year (in Shepherd’s method). &#167; Age [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. t<sub>D</sub> end of (finite) lifetime [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. &#167;&#167; Total population [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>]. N˚ of tags liberated [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. t˚ temperature [<xref ref-type="bibr" rid="scirp.35705-ref98">98</xref>]. Freedom period in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. t<sub>s</sub> as the age at the end of the first fishing season [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. t<sub>s</sub> earliest age at spawning; time dimension in migration model; maximum age of the cohort [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Age. t<sub>L</sub> age when the year class leaves the fished area; t<sub>0</sub> age at maximum biomass peak [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>τ—Free. &#167;&#167; Portion of the ration ultimately recovered as net energy [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. Time [<xref ref-type="bibr" rid="scirp.35705-ref120">120</xref>] interval [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Fraction of population at some stage or condition [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Different par. related to survival from fishing and natural mortality [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Variance related par. in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Age at sex or sex ratio change [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Time interval; density independent mortality component [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Fraction of or whole year; time spent in searching and handling; reference ages in growth models; n˚ of years represented in the plus group [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] τ<sub>P</sub> age at which 100(P)% of the population remains [<xref ref-type="bibr" rid="scirp.35705-ref114">114</xref>]. Mean length at first recruitment; as subscript, size at recapture [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>].</p><p>θ—Z over K ratio (72). θ<sub>B</sub> Beverton and Holt. θ<sub>S</sub> Ssentongo and Larkin. θ<sub>P</sub> Powell. θ<sub>R</sub> regression. θ<sub>W</sub> Wetherall. θ<sub>J</sub> Jones and van Zalinge [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. &#167; Z/K [<xref ref-type="bibr" rid="scirp.35705-ref119">119</xref>]. r [<xref ref-type="bibr" rid="scirp.35705-ref115">115</xref>]. &#167;&#167; Angle [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Fraction of the total mortality [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Generic par. of interest; a priori estimate of a par. within the Bayesian-type approach; prop. of specimens which change sex; true prop. of fish by age; survival curve in length frequency analysis (LFA); ratio between the true but unknown n˚ of age a fish in a random sample and the overall fish population; annual rate of movement from region i to region j; migration prop. [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. T—Transport coefficient or rate of interchange of fish between adjacent areas [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Instantaneous rate of transfer [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167; T'' immigrating [<xref ref-type="bibr" rid="scirp.35705-ref145">145</xref>]. Destination area in fish migration [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. &#167;&#167; T<sub>α </sub>period of marking; ratio in Allen’s recruitment method. Total metabolism [98,143]. Different par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref2">2</xref>]. Duration of pregnancy or time to hatching in Elasmobranchs VBGF modelling [<xref ref-type="bibr" rid="scirp.35705-ref159">159</xref>]. Time interval [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Total n˚ of marked and non marked specimen [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Time delay or horizon; temperature as degree days [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. T<sub>h</sub> time at hatching; T<sub>0</sub> time of recruitment; test function; mean environmental [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>] or annual habitat temperature in ˚C [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. Age [93,101]. T<sub>max</sub> maximum age in absence of exploitation [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>]. Tonnage of a vessel; balance index; ocean-surface temperature anomaly; fishing time [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Age at which transition to the next pool occurs [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Total death; transformation of original data; time periods; age of recruitment; n<sup>th</sup> moment; T<sub>0</sub> mean generation length or mean age of reproduction; objective function; vector of tag release in different areas; threshold level [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Marked specimens [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Test function in Shepherd’s length-composition analysis; vessel lifetime; age at maturity; biological zero time temperature; foraging time [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Time at which the final harvest is to be performed [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>].</p><p>TL—Trophic level [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>Θ (theta)—M over K ratio. Θ<sub>∞</sub> as M<sub>∞</sub>/K [<xref ref-type="bibr" rid="scirp.35705-ref153">153</xref>]. &#167; M/K invariant. &#167;&#167; Vector of par. [<xref ref-type="bibr" rid="scirp.35705-ref93">93</xref>]. Mean; vector of unknown par. [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Set of par.; age-specific migration rate matrices and matrices in general [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Vector of par. [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>u—Ratio of recovery to marked fish released. &#167;&#167; Unavailable population (in unfished area) [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>]. Ratio of exploitation [<xref ref-type="bibr" rid="scirp.35705-ref89">89</xref>]. Yearly increase in length [<xref ref-type="bibr" rid="scirp.35705-ref120">120</xref>]. Average fish velocity [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Normally distributed random variable [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Typical fish weight [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Age at maturity— longevity product [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>]. Individual probability of capture; par. related to Fletcher quadratic model; normal random (0 - 1) variable [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Catch per unit of effort [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>υ—To not be used in order to avoid confusion with similar symbol.</p><p>U—Catch per unit of effort [25,27,65,70,76,107,129]. U<sub>C</sub> in n˚ (pieces). U<sub>Y</sub> in weight. U<sub>M</sub> per unit mortality (equivalent to CPUM by Quinn and Deriso [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. &#167; Catch-per-Unit-of-Effort [<xref ref-type="bibr" rid="scirp.35705-ref95">95</xref>]. c.p.u.e., C.P.U.E., CPUE, p.u.e, PUE, CUE [22,25,67,76,107]. C/f, Y/f [<xref ref-type="bibr" rid="scirp.35705-ref107">107</xref>]. C/f, Y/f, fishing success. Prop. harvested [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. The symbol “p” for “per” should not be used; also the c.p.u.e. and allies symbols should be no more employed. A term used in yield-per-recruit model [<xref ref-type="bibr" rid="scirp.35705-ref108">108</xref>]. &#167;&#167; Energy introduced in the growth process in the “equation of continuity” [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Average net velocity [<xref ref-type="bibr" rid="scirp.35705-ref147">147</xref>]. Par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Expansion factor [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Mean of a distribution; expansion factor [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Weight related par. in Schnute [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>] model. Complement of L<sub>c</sub>/L<sub>∞</sub> as U= 1- L<sub>c</sub>/L<sub>∞</sub> (74). Random variable; expansion factor in B&amp;H Y/R model; penalty weight function in LFA; utility function [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Exploitation rate [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>] U'—Catch per unit of area. &#167; CPUA [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>].</p><p>v—Co-ordinate defining sub-areas. &#167;&#167; Natural death fraction [<xref ref-type="bibr" rid="scirp.35705-ref69">69</xref>]. Swimming speed [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. Virgin or pristine; equilibrium [<xref ref-type="bibr" rid="scirp.35705-ref76">76</xref>]. Weight 1 year prior to recruitment; a particular weight of fish; normally distributed random variable [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Natural mortality—longevity product [<xref ref-type="bibr" rid="scirp.35705-ref113">113</xref>]. Age specific vulnerability [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Vulnerability [<xref ref-type="bibr" rid="scirp.35705-ref151">151</xref>]. Maximum mortality rate that a predator can exert on a prey [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Selection par. related to haul [<xref ref-type="bibr" rid="scirp.35705-ref73">73</xref>]. Par. related to Fletcher’s quadratic model; residuals [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Vulnerability to the fishery [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Rates of behavioural exchange between vulnerable and invulnerable state in Ecosim; sets of observations [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>*v—Value of fish in the specified monetary unit. &#167; v as average price [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]; for example, *v<sub>$</sub>. p as price or V as value of income [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. v fish value [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>].</p><p>V—Virtual population [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>], cohort analysis [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] and, in general, age-structured related par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. &#167; VPA (74]. &#167;&#167; The (logarithmic) rate of natural increase; growth rate of biomass; catch in weight at equilibrium [88,105]. Value [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. Energy removed in the growth process in the “equation of continuity” [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Water volume [<xref ref-type="bibr" rid="scirp.35705-ref140">140</xref>]. Trawling speed and fluid velocity [<xref ref-type="bibr" rid="scirp.35705-ref106">106</xref>]. Weight at recruitment; a particular weight of fish; normally distributed random variable; value [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Variance [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Weight at recruitment to area and gear [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Amount of prey biomass or n˚ of species eaten by a predator; value; vessel effect; n˚ of vessels in the fishing fleet [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Reproductive value [<xref ref-type="bibr" rid="scirp.35705-ref87">87</xref>]. Biomass of prey I available to predator j [<xref ref-type="bibr" rid="scirp.35705-ref82">82</xref>]. Value in Thompson and Bell analysis [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Variance; V<sub>0</sub> volume of eggs in the ovaries; penalty function for mortality and variance within length interval in LFA; accumulated variance among ages; variance-covariance matrix [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Overlap index in length frequency analyses; sustainable profit; value [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>*V—Swimming speed [<xref ref-type="bibr" rid="scirp.35705-ref146">146</xref>]. b in body lengths s-1 [<xref ref-type="bibr" rid="scirp.35705-ref99">99</xref>]. &#167; Fish velocity [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>].</p><p>VBGF—Von Bertalanffy Growth Function [70,71,82] or formula [71,113]. &#167; VBGE, equation [<xref ref-type="bibr" rid="scirp.35705-ref153">153</xref>] LVB, Ludwig von Bertalanffy [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. VBGM, model [<xref ref-type="bibr" rid="scirp.35705-ref135">135</xref>]. The (3 par.) von Bertalanffy equation [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>VPA—Virtual population analysis [65,70]. &#167; Age structured, sequential, integrated or synthetic analysis [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>] MSVPA multispecies [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>w—Individual [74,120] measured fish weight. Body mass [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>] or weight [25,70]. Fish weight [<xref ref-type="bibr" rid="scirp.35705-ref63">63</xref>]. w<sub>r</sub> round (overall-total). w<sub>g</sub> gutted (eviscerated). w<sub>dry</sub> dehydrated organism after a standard time in an oven (incorporated in McGurk [<xref ref-type="bibr" rid="scirp.35705-ref168">168</xref>] model. &#167; Typical fish weight and other related par. in Schnute [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>] model. w<sub>k</sub> weight at recruitment; normally distributed random variable [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Round and gutted weight also in Lleonart [<xref ref-type="bibr" rid="scirp.35705-ref22">22</xref>]. &#167;&#167; Par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Non linear scaling par. [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Width of the length frequency intervals in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Relative (statistical) weight; width of a vessel action [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Statistical weight [for example, in the Extended Survivors Analysis;70], usually the inverse of variance, applied to a datum [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Akaike’s weigh factor [<xref ref-type="bibr" rid="scirp.35705-ref135">135</xref>].</p><p><sub>•w</sub>—Individual body component weight.</p><p>wd—Individual measured fish width; especially in rays and skates it indicates the distance from the tip of the left to the tip of the right “wing” [<xref ref-type="bibr" rid="scirp.35705-ref109">109</xref>].</p><p>W—Theoretical (parametric) fish weight at stock level [25,61,67,70,76,86]. See a for other specifications (such as W<sub>c</sub> and W<sub>R</sub>). &#167; Somatic weight [<xref ref-type="bibr" rid="scirp.35705-ref99">99</xref>]. Mean weight of a fish at age t [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Individual weight [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. &#167;&#167; Total weight of a stock [<xref ref-type="bibr" rid="scirp.35705-ref120">120</xref>]. Empirical weighting factor [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Net width [<xref ref-type="bibr" rid="scirp.35705-ref137">137</xref>]. Penalty term in LFA [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>W<sub>∞</sub>—Asymptotic weight. See L<sub>∞</sub> and allies for the analogous specifications.</p><p>WP—Winter Point in the seasonal VBGF; the period of the year (expressed as fraction of year) when growth is slowest; related to t<sub>s</sub> through WP = t<sub>s</sub> + 0.5 [66,72] &#167; t<sub>w</sub> [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>].</p><p>x—Independent variable generally in linear regression [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. &#167;&#167; N˚ of tagged specimens found in a sample [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. Par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Coefficient of proportionality between Gulland MSY and MB<sub>0</sub> expression [128,173]. Label for categories of interest in gear selectivity; sampling units; position dimension in migration model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Spatial coordinate in Individual Based Models; age [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. x<sub>m</sub> age at maturity in Jensen’s invariant [<xref ref-type="bibr" rid="scirp.35705-ref27">27</xref>].</p><p>ξ—Free. &#167;&#167; Probability of being recaptured [<xref ref-type="bibr" rid="scirp.35705-ref141">141</xref>]. Variance related par. in MULTIFAN [<xref ref-type="bibr" rid="scirp.35705-ref102">102</xref>]. Par. in Deriso-Schnute’s stock recruitment and mark recapture version of Schnute’s growth model; fraction of fish not caught that do not die due to natural mortality [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p><p>Ξ (csi)—Free. &#167;&#167; Annual food consumption of a fish population.</p><p>X—Mark (tagging) and recapture related par. N<sub>X</sub> n˚ of tagged specimens before the samplings [<xref ref-type="bibr" rid="scirp.35705-ref139">139</xref>]. <sub>r</sub>N<sub>X</sub> n˚ of tags (tagged fish) recovered [25,151] X<sub>D </sub>disappearance rate of marks [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. X<sub>OL</sub> other loss rate (in tagging). X<sub>P</sub> probability of recapture. &#167; m in Jones [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. R for recaptures [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. &#167;&#167; Exploitation rate as F(1-exp-Z)/Z [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>]. N˚ of baits undisturbed [<xref ref-type="bibr" rid="scirp.35705-ref90">90</xref>]. Annual instantaneous mortality other than fishing [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. “Perturbed” and “unperturbed” outputs in sensitivity analysis [<xref ref-type="bibr" rid="scirp.35705-ref71">71</xref>]. Independent observation; population level; n˚ of groups [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Ancillary variable as l/L<sup>∞</sup> [<xref ref-type="bibr" rid="scirp.35705-ref72">72</xref>]. Average weight of the entire recruitment population and other related par. [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Coefficient of proportionality between M and F<sub>MSY</sub> [<xref ref-type="bibr" rid="scirp.35705-ref173">173</xref>]. Any “second” stock in multispecies analysis; generic independent variable [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Value of a environmental factor [<xref ref-type="bibr" rid="scirp.35705-ref103">103</xref>]. Multiplication factor of F in Thompson and Bell analysis [<xref ref-type="bibr" rid="scirp.35705-ref74">74</xref>]. Average year class size over a period of time; total sampling units; critical value; environmental variables; transformed variable; matrix related symbols; disappearance rate of marks [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Generic variable [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Proportional escapement [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>]. XSA—Extended survivors analysis [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>y—Dependent variable generally in linear regression [<xref ref-type="bibr" rid="scirp.35705-ref66">66</xref>]. &#167;&#167; Par. in tagging experiments [<xref ref-type="bibr" rid="scirp.35705-ref92">92</xref>]. Total yield as a fraction of the N(t<sub>0</sub>)W<sub>∞</sub> product [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Calendar year and year of commercial data [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Initial conditions [y<sub>l </sub>and y<sub>2</sub>; 93] in Schnute’s growth model; position dimension in migration model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].Year; spatial coordinate in Individual Based Models [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>*y—Year. &#167; y [74;61;70]</p><p>Y—Yield [25,67,76,83,120]. (Total) catch in weight [70,82,105,117,122]. Total yield from a year-class [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. (Total) catch in biomass units [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Y<sub>∞</sub> total yield over the lifetime of a cohort. Y<sub>*</sub> at equilibrium [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Y<sub>g</sub> gross. Y<sub>by</sub> not target. Y<sub>r</sub> retained on board. Y<sub>l</sub> live. Y<sub>d</sub> landed. <sub>R</sub>Y replacement yield [RY in 117]. &#167; Net economic yield [<xref ref-type="bibr" rid="scirp.35705-ref96">96</xref>]. Cohort strength; actual catch [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Y<sub>W </sub>average weight of fish and other related par. [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. &#167;&#167; N˚ of fish hooked whether or not they subsequent escape [<xref ref-type="bibr" rid="scirp.35705-ref90">90</xref>]. Average weight within the newly recruited population [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Total n˚ of year of fishery data [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Length, weight, or some other determinant of fish size [<xref ref-type="bibr" rid="scirp.35705-ref93">93</xref>]. Rate of a certain metabolic function [<xref ref-type="bibr" rid="scirp.35705-ref103">103</xref>]. Recruitment variable; generic individual size; n˚ of size classes [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Generic [dependent; 25] variable [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>Y/R—Yield-per-recruit [76;65]; catch in weight per recruit. Y/R<sub>max</sub> maximum value (at F<sub>max</sub>). Y/R<sub>F∞</sub> maximum possible value in the isopleth diagram. Y'/R relative. &#167; (Y<sub>W</sub>/R)<sub>max</sub>. (Y/R)' relative (74). YPR [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>].</p><p>YEB—Yield exploitable biomass; the fraction of a stock which is considered economically usable. In case M is low then YEB ≈ MSY (on the opposite YEB &gt; MSY) [170-172].</p><p>z—Ratio of fished to unfished areas (→ ∞ when the whole area is fished). &#167;&#167; Function of the virtual population [<xref ref-type="bibr" rid="scirp.35705-ref127">127</xref>]. Cons. in the parabolic generalisation of the growth—metabolic process [<xref ref-type="bibr" rid="scirp.35705-ref91">91</xref>]. Standard metabolism [<xref ref-type="bibr" rid="scirp.35705-ref143">143</xref>]. Dummy variable [<xref ref-type="bibr" rid="scirp.35705-ref86">86</xref>]. Specific growth rate in Schnute’s model; steepness of the SRR [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Par. (N<sub>t</sub> – N<sub>* </sub>or<sub> </sub>B<sub>t</sub> – B<sub>*</sub>) in delay difference models [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>]. Spatial coordinate in Individual Based Models [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. Shape par. in Pella-Tomlinson’s model [<xref ref-type="bibr" rid="scirp.35705-ref117">117</xref>].</p><p>ζ—Free. &#167;&#167; Maintenance food coefficient. Efficiency or correction factor [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>].</p><p>Z—Instantaneous rate of stock total mortality from all causes [130,76,67,86,107,25,82,74,65,61,70]. Z<sub>H</sub> Heincke. Z<sub>R</sub> Robson and Chapman. Zr = 0 maximum level that a population can withstand [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>]. Z<sub>*a</sub> area specified (as Z<sub>y,a,Ar,q</sub> in [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>]. &#167; Z* reference mortality in a variant of B&amp;H expression relating mortality to length at maturity [<xref ref-type="bibr" rid="scirp.35705-ref128">128</xref>]. S<sub>stock</sub> [<xref ref-type="bibr" rid="scirp.35705-ref70">70</xref>] See F ad M for other specifications. &#167;&#167; Catch in term of n˚ of fish on the line [<xref ref-type="bibr" rid="scirp.35705-ref90">90</xref>]. Standardised normal variate [<xref ref-type="bibr" rid="scirp.35705-ref97">97</xref>]. Mean depth [<xref ref-type="bibr" rid="scirp.35705-ref67">67</xref>]. Average weight within the previously exploited population and other related par. [<xref ref-type="bibr" rid="scirp.35705-ref64">64</xref>]. Logarithm of relative rate of change in Schnute model [<xref ref-type="bibr" rid="scirp.35705-ref65">65</xref>].</p></sec><sec id="s3_2"><title>3.2. Final Thoughts</title><p>A simply insight in both “Milestone” and “proposed” list allows the immediate perception that convenience and opportunity were the general criteria followed by the Authors in defining and using the symbols. Even in the same contribute or textbook, the same symbols were often employed with different meanings [<xref ref-type="bibr" rid="scirp.35705-ref68">68</xref>] and rarely according to any point of the decalogue, with some exception (for example, the 8<sup>th</sup> point in [<xref ref-type="bibr" rid="scirp.35705-ref25">25</xref>]. Overall, only an handful of symbols resulted to be used in a quite consistent and standard manner; in particular, those related to natural (M) and total (Z) instantaneous mortality rates, and the coefficient of proportionality (q as catchability) relating fishing mortality (F) to fishing effort (f).</p><p>Another interesting aspect consists in a sort of reluctance in using symbols in most of the contributes and books produced at the beginning of the fishery science. At the Symposium on Fish Populations, held in Toronto in 1947 [<xref ref-type="bibr" rid="scirp.35705-ref174">174</xref>], few specific symbols were used only in two of the nine contributes presented [59;95]; few symbols were also used in Ricker [<xref ref-type="bibr" rid="scirp.35705-ref53">53</xref>], a contribution likely prepared before his 1958 handbook). Apparently, the burst of the use of symbols in fisheries occurred with the Beverton and Holt contributes, especially those published in 1956, 1957 and 1959; in the 1957 book, in particular, the Authors were forced to adopt almost the whole Latin and Greek alphabet.</p><p>As previously stated, the opportunity of symbols standardisation was highlighted at the end of fifty [14-16], but thereafter, the feeling is that the Authors were more worried about the agreement on definitions instead of symbols.</p><p>The consequences of a lack of standardization have determined long-standing problems mainly due to confusing symbols, definitions and applications. One of the most interesting examples of such as ambiguity might be referred to the “asymptotic” length in the von Bertalanffy growth function. Beside the biological interpretation (where it has any), the main troubles arise from a) confounding the maximum individual length with maximum mean length at age [101,160]; b) assuming that the maximum ever length could be used as the theoretical asymptotic length [<xref ref-type="bibr" rid="scirp.35705-ref175">175</xref>] or as a proxy of it (L<sub>∞</sub> ≈ L<sub>max</sub>/0.95; 71); and c) forgiving that present maximum length in a exploited stock might be quite lower than the maximum length in the pristine condition (even at small rate of fishing; [<xref ref-type="bibr" rid="scirp.35705-ref54">54</xref>]), resulting in lower asymptotic length even maintaining the same rate of approaching it [<xref ref-type="bibr" rid="scirp.35705-ref176">176</xref>]. Considering that L<sub>∞</sub> (more rarely L<sub>inf</sub> or L<sub>asy</sub>) is generally used for different defined asymptotic length estimations, which are on their turn used to compare data or to get invariants [177,178], it is evident of the possible confusing effects and the opportunity for a better correspondence between the symbol and the defined parameter.</p><p>Another example of misusing is represented by what Beverton and Holt (see the Milestone list) have defined as the “fishable life span” (denoted with λ), which represented an arbitrary upper bound to the computations, reflecting the progressive rarefaction of the oldest age classes in the samples. Convenience has induced the Authors to set λ ≈ ∞, obtaining a simplification in the computations. Thereafter, the fishable life span was often associated to the longevity, which is evidently an error at least because the two parameters have a different definition.</p><p>Finally, present results support the Beverton and Holt’s 1957 sentence about the discrepancy between the number of items employed in fisheries assessment and the number of possible not confusing symbols. The present proposal tends to offer an operative solution by associating all the Latin letters to key quantities/items relevant to fisheries assessment and leaving free (with few consolidated exceptions) the Greek letters to identify different parameters and items (<xref ref-type="table" rid="table1">Table 1</xref> in Annex). Obviously, the scheme presented here should be intended as a consistent example which should be used as a starting point towards the establishment of an international communication standards in fisheries assessment.</p><table-wrap-group id="1"><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Synoptic table of correspondence between item/parameters and symbols proposed (PS) in the present contribute. In the examples column, a selection of other meanings attributed to the given symbol in fishery science are presented (see both the “Milestone” and “Proposed list” sections for abbreviations and other details)</title></caption></table-wrap-group></sec></sec><sec id="s4"><title>4. ACKNOWLEDGEMENTS</title><p>A special thank to Lady Alexis Pacey, Publications Manager of the North Atlantic Fisheries Organisation (NAFO), Dartmouth, NS, who has provided the original historical ICNAF reports and Dr. Adamo Giovanna for her genuine interest in this paper.</p></sec><sec id="s5"><title>REFERENCES</title></sec></body><back><ref-list><title>References</title><ref id="scirp.35705-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Cushing, D.H. (1983) Key papers on fish populations. Irl Press, Oxford.</mixed-citation></ref><ref id="scirp.35705-ref2"><label>2</label><mixed-citation publication-type="book" xlink:type="simple">Smith, T.D. (1988) Stock assessment methods: The first fifty years. 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In: Wolstenholme, C.E.W. and O’Connor, M., Eds., Ciba Foundation Colloquia on Ageing, J and A Churchill Ltd., London, 142-179.</mixed-citation></ref><ref id="scirp.35705-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Gulland, J.A. (1955) On the estimation of growth and mortality in commercial fish population. Fishery Investigations, 18, 46.</mixed-citation></ref><ref id="scirp.35705-ref9"><label>9</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Gulland</surname><given-names> J.A. </given-names></name>,<etal>et al</etal>. 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