Estuarine, Coastal and Shelf Science (1992) 35, 637-648
Spatial Distribution o f M u n i d a i n t e r m e d i a and M. s a r s i (Crustacea: A n o m u r a ) on the Galician Continental Shelf (NW Spain): Application of Geostatistical Analysis
J. F r e i r e a, E. G o n z h l e z - G u r r i a r ~ n
a a n d I. O l a s o b
~Departamento de Bioloxia Animal, Universidade da Coruaa. 15071 A Coruaa, Spain and blnstituto Espaaol de Oceanografia. Apartado 240. 39080 Santander, Spain Received 30 May 1991 and in revisedform 1 ffune 1992
Keywords: geostatistical analysis; variograms; kriging; spatial distribution; Munida intermedia, Munida sarsi; Galician continental shelf; N W Spain Geostatistical methodology was used to analyse spatial structure and distribution of the epibenthic crustaceans Munida intermedia and M. sarsi within sets of data which had been collected during three survey cruises carried out on the Galician continental shelf(1983 and 1984). This study investigates the feasibility of using geostatistics for data collected according to traditional methods and of enhancing such methodology. The experimental variograms were calculated (pooled variance minus spatial covariance between samples taken one pair at a time vs. distance) and fitted to a ' spherical' model. The spatial structure model was used to estimate the abundance and distribution of the populations studied using the technique of kriging. The species display spatial structures, which are well marked during high density periods and in some areas (especially northern shelf). Geostatistical analysis allows identification of the density gradients in space as well as the patch grain along the continental shelf of 16-25 km diameter for M. intermedia and 12-20 km for M. sarsi. Patches of both species have a consistent location throughout the different cruises. As in other geographical areas, M. intermedia and M. sarsi usually appear at depths ranging from 200 to 500 m, with the highest densities in the continental shelf area located between Fisterra and Estaca de Bares. Although sampling was not originally designed specifically for geostatistics, this assay provides a measurement of spatial covariance, and shows variograms with variable structure depending on population density and geographical area. These ideas are useful in improving the design of future sampling cruises.
Introduction T h e r e c e n t a p p l i c a t i o n o f geostatistical analysis (Clark, 1979; M a t h e r o n , 1971) to b i o l o g y ( B u r r o u g h s , 1987; L e g e n d r e & F o r t i n , 1989), a n d p a r t i c u l a r l y to t h e s t u d y o f i n v e r t e b r a t e s s u b j e c t to e x p l o i t a t i o n ( C o n a n , 1985) has o p e n e d the w a y to n e w a p p r o a c h e s in t h e a s s e s s m e n t o f p o p u l a t i o n s , b y i n t r o d u c i n g t h e analysis o f spatial d i s t r i b u t i o n in stock a b u n d a n c e estimates. 0272-7714/92/012637 + 12 $08.00/0
© 1992 Academic Press Limited
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Up to the present, studies have focused on species under exploitation, and analyse the applicability of kriging to estimate stock abundance and biomass (Nicolajsen & Conan, 1987). These studies also show its value as a technique for spatial distribution analysis (Conan, 1987; Conan & Maynard, 1987; Conanetal., 1989; Sullivan, 1991). Geostatistical analysis is an alternative approach to traditional methods (Hurlbert, 1990), which do not take into account the spatial autocorrelation (Cliff & Ord, 1973) between samples: kriging allows the analysis and modelling of the variability of a population in space in order to enhance both mean and variance estimates (Matheron, 1971). Munida intermedia and Aft. sarsi (Crustacea, Anomura, Galatheidae) are abundant epibenthic species on the Galician continental shelf, which is an area of overlap in their geographic distribution (Gonz/dez-Gurriarfin & Olaso, 1987). Data from several cruises designed to assess the stocks of harvested demersal species and the by-catch of invertebrate and fish species were analysed by geostatistical techniques. In this way the spatial structure and distribution of the Munida species was described and mapped, and the abundance of the populations was assessed. Geostatistical analysis does not require a special sampling design although the quality of variograms, mapping and assessments is improved when samples are taken along a regular grid (Burroughs, 1987). The present study investigates: (1) the feasibility of using geostatistics for existing data collected by traditional sampling methods, and (2) the feasibility of enhancing such methodology.
Materials and methods
Sampling The sampling is described in detail by Gonzfilez-Gurriar~n and Olaso (1987). In this paper, we analyse the results of three cruises that took place in the Galician continental shelf: CARIOCA 83 (C83, September 1983), I C T I O - N W 84 (184, May 1984) and CARIOCA 84 (C84, August-September 1984). During each cruise a randomly stratified sampling was carried out (up to 500 m deep), in which the shelf was divided into three geographical areas (Mifio-Fisterra, Fisterra-Estaca de Bares and Estaca de Bares-Ortegal), considering two strata to be divided by the isobath of 200 m (Figure 1). A Baka type trawl was used, with each tow lasting between 30 and 60 min. For data analysis, the densities of the different species caught were standardised to 60 min tows.
Dam ana&sis In geostatistical methodology (Clark, 1979; Conan, 1985; Matheron, 1971), the covariance of the parameter studied is analysed and modelled in terms of the distance between sampling units. Also the optimum weights are calculated for each sample in order to estimate the parameter, whether at a point (point kriging) or a block (block kriging). T h e representation of the covariance in terms of distance is carried out using a variogram, where the semivariance (r(h)) is represented. This is equal to the variance between independent samples minus the covariance between samples separated by a distance h. x(h) is estimated by: N
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TABLE 1. Mean catches (number. one hour tow -t) of Munida intermedia and Munida sarsiduring cruises C83, I84 and C84 on the Galiciancontinentalshelf and the north and south areas (standard deviation, SD, is shown). Parameters of the spherical models of variograms fitted for each species and cruise (C0=nugget effect, C=sill-nugget, a= range). In cases with experimental variograms without spatial covariance a nugget model was fitted, and this parameter is shown Mean catch Species
Cruise
Munida intermedia C83 I84
C84
Munida sarsi C83 I84
C84
Area
Total North South Total North South Total North South Total North South Total North South Total North South
n .h -t
Spherical model SD
7.68 20.62 10.00 24.98 4-33 9-94 1-95 5-87 2-11 7"26 1-72 2.85 163"95 877.44 190-60 1029-71 100"37 377"61 6.64 11-09 0.46 15-39 25-86 0-32
83"57 122.11 8.53
25-55 32-83 1.83 79.20 101.79 1-05 289-02 349.13 17.50
Co
410.5 623.8 98-7 0 0 8.1 0 0 -0 0 3-3 0 0 1"1 0 0 --
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a
34 70
22 16
750 000 1 060 000
25 20
650 1070
15 12
6300 10 300
15 15
83 500 120 000 --
20 20 --
where Z(xi) a n d Z(xi-[- h) are the d e n s i t y at p o i n t x i a n d i n the samples located at a distance h (lag) from xl, n is the n u m b e r of pairs of stations sampled, a n d N the n u m b e r o f s a m p l i n g points. A theoretical m o d e l is t h e n fitted to the e x p e r i m e n t a l variogram. I n the p r e s e n t study, we u s e d the spherical m o d e l , w h i c h is the m o s t c o m m o n i n the analysis o f a n i m a l p o p u lations a n d i n geostatistics i n general. Others, such as the fractal model, are c u r r e n t l y b e i n g researched, a n d they appear to give a n accurate p i c t u r e o f the spatial d i s t r i b u t i o n of certain o r g a n i s m s ( C o n a n & W a d e , 1989). T h e spherical m o d e l has the following form: r(h) = C O + C(3/2 h/a -
1/2 h3/a 3)
where C o is the n u g g e t effect, d u e to the variability b e t w e e n replicates, the m i c r o s t r u c t u r e w h i c h r e m a i n s u n d e t e c t e d because of the size o f the sample, or errors in m e a s u r e m e n t or location. C represents the sill-nugget effect, where the sill is the a s y m p t o t i c value of semivariance, reached with a value of h = a, called range, w h i c h represents the m a x i m u m distance at w h i c h spatial effects are detected. T h e m o d e l of the variogram a n d the s a m p l i n g data were used to calculate the o p t i m u m weights a t t r i b u t e d to each s a m p l i n g u n i t , w h i c h allowed us to estimate the d e n s i t y (Z*) at a n u n s a m p l e d p o i n t ( p o i n t kriging) or area (block kriging), as well as the variance o f the estimate,
Geostatistical analysis of spatial distribution of M u n i d a
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Affunida intermedia during cruises (:83, I 8 4 a n d C 8 4 in the Galician continental s h e l l ( I n cases o f spatial covariance undetected, only experimental variograms are shown.)
N Z* =
E
wiZ(xi)
i=l
where N is the number o f samples, w i is the weight attributed to sample x; and •wi= 1 (in the traditional methods all samples show the same weight w - - l / N ) . Variograms were calculated for the overall sampling area and for two geographical zones of the shelf: North, from Fisterra to Ribadeo, with S W - N E shoreline orientation; and South, from Mifio to Fisterra, with N - S orientation and a great influence from the Rias (in the C84 cruise experimental variograms for the southern area were not calculated because the number of sampling points was too small). Results presented correspond to isotropic variograms; anisotropy was not studied in detail, although anisotropic variograms calculated in the direction o f the shoreline (not shown) have a similar structure to isotropic variograms for each area. In the present case point kriging was used for estimating values at the nodes o f a 5 x 5 k m grid covering survey area extending from the coast to the 500 m isobath. Variogram models fitted for the overall sampling area were used for kriging.
642
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M u n i d a intermedia
The variograms differ between cruises (Figure 2; Table 1). In C83, a period of low density (7.68 h-1), spatial covariance is undetected (C83). In I84 (also with low densities, 1.95 h-~), the variogram has a spatial covariance showing two maxima of semivariance at 13 and 22 km, although the first lags are noise. This structure corresponds both to the variogram for all sampling points and for the north area, whereas in the south, where the densities are very low, spatial covariance is not detected. In cruise C84, which the highest densities were encountered (163.95 h - ~), spatial covariances range up to 25 km (20 km in the North). Variograms showing spatial covariance do not present nugget effects.
Geostatistical analysis of spatial distribution of Munida
643
o
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F i g u r e 3(b).
Figure 3. Spatial distribution of Munida intermedia on the Galician continental shelf during cruises I84 and C84: Density isocontours obtained from point kriging. (Isocontour densities are 0, 2, 5 and 10 in I84 map and 0, 200, 400, 800 and 1600 in C84 map.)
T h e densities o f M . intermedia are lower in cruises C83 a n d I84, w i t h m a x i m u m catches located in the d e e p e s t zone o f the F i s t e r r a - E s t a c a de Bares area a n d o u t o f the Rias, n e a r the coast ( F i g u r e 3). D u r i n g C84 M . intermedia o c c u r r e d at v e r y h i g h densities w i t h a spatial s t r u c t u r e in p a t c h e s a l o n g t h e c o n t i n e n t a l s h e l f ( F i g u r e 3). T w o large g r o u p i n g s can be d i s t i n g u i s h e d , one c o i n c i d i n g w i t h s t r u c t u r e s e n c o u n t e r e d in earlier cruises in the d e e p n o r t h e r n area (up to > 1600 h-~), has a c o m p l e x i n t e r n a l s t r u c t u r e , a n d the o t h e r is s i t u a t e d o p p o s i t e the m o s t s o u t h e r n Rias Baixas in m o r e shallow waters (up to > 800 h - l ) .
Munida sarsi M. sarsi d i s p l a y s w e l l - d e f i n e d spatial s t r u c t u r e in t h e t h r e e cruises o n t h e w h o l e area a n d on the n o r t h shelf, w h i c h is satisfactorily m o d e l l e d u s i n g a spherical v a r i o g r a m w i t h a
J. Freire et al.
644
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/
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0 I0 2 0 30 40 50 6 0 Distance (h) Figure 4. Experimental variograms (dashed line) and spherical models (solid line) for Munida sarsiduring cruises C83, I84 and C84 in the Galician continental shelf. ( I n cases of spatial covariance undetected, only experimental variograms are shown.)
range of 12-15 km in C83 and I84 and 20 km in C84, and a nugget effect practically nonexistent (Table 1; Figure 4). In the south the densities are lower than in the north and the variogram does not show a spatial covariance effect (Table 1; Figure 4). This species is distributed along the Galician continental shelf reaching maximum densities in the Fisterra-Estaca de Bares area, especially in the deep water zones (over 200 m). The position of the groupings remained unchanged throughout the cruises (Figure 5), despite great fluctuations in density (from 6.64 and 15.39 h - i in C83 and I84 to 83.57 h - i in C84). However, the distribution within these areas becomes more complex in areas or periods of highest abundance. Discussion Assessment methods which do not take into account spatial covariance may provide simplified analyses as they usually assume that the present density areas or strata are internally homogeneous unless the sampling design is perfectly random (Conan, 1987; Sullivan, 1991). Analysis of the spatial pattern of populations has not been carried out
Geostatistical analysis of spatial distribution of M u n i d a
645
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646
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Figure 5(c). Figure 5. Spatial distribution of Munida sarsi on the Galician continental shelf during cruises C83, I84 and C84: Density isocontours obtained from point kriging. (Isocontour densities are 0, 5, 10, 15, 20, 25 and 30 in C83 map, 0, 50, 100 and 200 in I84 map and 0, 50, 100, 300, 500, 700 and 900 in C84 map.)
a c c u r a t e l y u s i n g t r a d i t i o n a l m e t h o d s ( H u r l b e r t , 1990), as t h e y do n o t allow a b u n d a n c e g r a d i e n t s to be m a p p e d a n d i n t e g r a t e d in space, defining g r a d i e n t d e n s i t y as well as the g r a i n (size) o f the patches. T h e s e factors are reflected in geostatistics g i v i n g a m o r e realistic view o f the d i s t r i b u t i o n o f a species. M u n i d a intermedia and M . sarsi are f o u n d in p a t c h e s along t h e G a l i c i a n c o n t i n e n t a l shelf that were relatively stable d u r i n g t h e different cruises. T h i s suggests t h a t t h e r e are stable p h y s i c a l factors that m a i n l y d e t e r m i n e h o w t h e two species are d i s t r i b u t e d . T h e G a l i c i a n c o n t i n e n t a l s h e l f is an area o f o v e r l a p b e t w e e n d i s t r i b u t i o n o f M . intermedia, a species characteristic o f w a r m t e m p e r a t e waters p r e s e n t in t h e M e d i t e r r a n e a n , a n d M . sarsi, w h i c h is c h a r a c t e r i s t i c o f cold t e m p e r a t e waters. I t has b e e n s u g g e s t e d t h a t t h e difference in z o n i n g o f t h e t w o species in t e r m s o f d e p t h is a r e s u l t o f t h e i r t e m p e r a t u r e p r e f e r e n c e s ( G o n z f i l e z - G u r r i a r f i n & Olaso, 1987). H o w e v e r , c o r r e l a t i o n b e t w e e n e n v i r o n m e n t a l factors, such as d e p t h a n d t e m p e r a t u r e , p r e v e n t s us f r o m d e t e r m i n i n g t h e p r i m a r y effects these factors have on t h e d i s t r i b u t i o n o f e p i b e n t h i c o r g a n i s m s (Basford et al., 1989). S t u d i e s c a r r i e d o u t in the M e d i t e r r a n e a n c o n t i n e n t a l shelf (Abell6 et al., 1988) as well as in t h e e a s t e r n A t l a n t i c ( L a g a r d e r e , 1973; Olaso, 1990) i n d i c a t e that b o t h species o f M u n i d a a p p e a r p r e d o m i n a n t l y at d e p t h s o f b e t w e e n 200 a n d 500 m a n d t h a t t h e y segregate to a certain extent. M . interrnedia t e n d s to be f o u n d in m o r e shallow waters than M . sarsi. O n
Geostatistical analysis of spatial distribution of Munida
647
the Galician continental shelf the same pattern is encountered, although the main segregation factor is not evident. However during cruise C84, M . intermedia, as well as other species of epibenthic crustaceans, were located in areas near the coast off the Rias Baixas and at depths less than 200 m (Gonz$1ez-Gurriar~n & Olaso, 1987). This may be due to the fact that this area witnesses a high rate of biological productivity caused by the runoff of nutrient rich waters from the rias, as well as upwelling processes that occur periodically. This provides an increase in the availability of food to other levels of the food web (Tenore et al., 1984). T h e length of the tows and the distance between location of the stations do not allow spatial effects to be analysed and modelled over short ranges ( < 3-5 km). However, the results, in particular the practically non-existent nugget effect in the variograrns, indicate that the microstructures have minimal importance, in contrast to the situation for other species found in the same area (Gonz~lez-Gurriar~n & Freire, unpubl, data). In the present analysis, it is not possible to produce high resolution maps, but this could be achieved with a modified sampling strategy. This application of geostatistical techniques suggests the following: (1) the existence of a spatial covariance with a range of 12-25 km, and (2) the variograms have a variable structure depending on the population density and/ or geographical area. These ideas will be useful in the design of future sampling programmes, that must be carried out on a regular grid (Burroughs, 1987; Conan, 1987), with short tows and taking special care in the location of sampling points. T h e application of geostatistical techniques could be improved in areas such as the Galician continental shelf, where they could be extremely useful in mapping and estimating population size, particularly for fished species. T h e study of spatial distribution and structure of the different species or assemblages would be the first step towards an analysis of their relationships with the different environmental or biotic factors, and the spatial dynamics of the populations.
Acknowledgements We would like to thank Mr E. Wade and D r G. Y. Conan (Marine Biology Research Centre, Moncton, Canada) for their assistance in the application ofgeostatistical methods and in data processing. We would like to give special thanks to Dr G. Y. Conan for his interest and critical reading of the manuscript. Ms C. P. Teed prepared the English version. This paper was based on data obtained from the fishery survey cruises carried out by the Instituto Espafiol de Oceanografia ( A T N program--Fisheries in the I C E S area).
References Abell6, P., Valladares, F. J. &Castell6n, A. 1988Analysisof the structure of decapodcrustaceans assemblages offthe Catalan coast (North-West Mediterranean). Marine Biology 98, 39-49. Basford, D. J., Eleftheriou, A. & Raffaelli, D. 1989 The infauna and epifauna of the northern North Sea. Netherlands ffournal of Sea Research 25, 165-176. Burroughs, P. 1987 Spatial aspects of ecologicaldata. In Data analysis in community and landscape ecology, Jogman, R. H. G., ter Braak, C. J. F. & van Tongeren, O. F. R., eds). Pudoc Wageningen,pp. 213-251. Clark, I. 1979Practicalgeostatistics. Elsevier, London, 129 pp. Cliff, A. D. & Ord, J. K. 1973 Spatial autocorrelation. Pion, Piou, London, 178 pp. Conan, G. Y. 1985 Assessment of shellfish stocks by geostatistical techniques. ICES, Shellfish Committee, C.AI. 1985/K: 30, 24 pp. Conan, G. Y. 1987 The paradigm of random sampling patches and the genesis of lognormal and negative binomial related models. ICES, Shellfish Committee, C.M. 1987/K:25, 11 pp.
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ft. Freire et al.
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