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1 December 2005 Grey partridge Perdix perdix population status in central northern France: spatial variability in density and 1994–2004 trend
Elisabeth Bro, François Reitz, Philippe Landry
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The grey partridge Perdix perdix is an important management concern in the European farmland. Pair numbers severely declined during the 20th century. As a result, the species has been listed in SPEC category 3, i.e. ‘Unfavourable’ conservation status in Europe. The largest population of western Europe occurs in France. Its status there is, therefore, decisive for the European conservation status of the species as well as for the future of the species. Populations of partridges in central northern France have been routinely surveyed since the 1980s for hunting management purposes. In this paper, we use this long-term and wide-scale survey to portray the demographic status of partridge populations. We emphasise the amplitude of spatiotemporal variations in breeding densities. In the 2000s, a number of areas where agriculture is intensive and where the species is hunted still sustain > 50 pairs/km2, whereas densities are < 5 pairs/km2 in other areas. These low densities are, however, higher than those commonly reported from other parts of Europe. Density levels exhibit large differences at a small spatial scale and show large year-to-year fluctuations which make trend assessment difficult. The 1994–2004 and 1999–2004 trends displayed different patterns; densities increased, decreased or were stable depending upon agricultural region.

Like many bird species associated with agricultural land (e.g. Siriwardena et al. 1998, Rocamora & Yeatman-Berthelot 1999), the grey partridge Perdix perdix has experienced a dramatic decline in Europe since World War II (Tucker & Heath 1994). According to Potts (1997), breeding stocks have dropped by > 80% since the 1930s. As a result, the grey partridge has been listed in SPEC category 3, i.e. ‘Unfavourable’ conservation status in Europe, but with main numbers outside Europe (Tucker & Heath 1994, Aebischer & Kavanagh 1997). Recently, BirdLife International (2004) drew attention towards this species because “although the species was stable or increased in many eastern European countries during the period 1990–2000, it has continued to decline throughout most of western and central Europe - including sizeable populations in France and Poland - and underwent a large decline overall”. This decline is all the more worrying because agro-environmental schemes have been applied in most countries for the benefit of wildlife (see Kleijn & Sutherland 2003, Bro et al. 2004).

The European breeding stock of grey partridge (excluding the Russian and Turkish populations) was estimated at 1.7–2.9 million pairs in the mid-1980s (Aebischer & Kavanagh 1997), and at 1–2.3 million pairs in the 1990s (BirdLife International 2004) with the largest population occurring in France. Reitz (2003) estimated the breeding population size at ca 750,000 pairs in France in spring 1998. The status of the French population is, therefore, decisive for the overall European conservation status of the species as well as for the future of the species in western Europe.

In France the grey partridge is a culturally important gamebird. Within the sedentary small game species inhabiting cultivated plains, the grey partridge ranked fourth in number of individuals killed by hunting after pheasant Phasianus colchicus, rabbit Oryctolagus cuniculus and red-legged partridge Alectoris rufa (ONCFS 2000). Ca 1.5 million birds were shot during the 1998/99 hunting season (Reitz 2000), but the proportion of released birds in the bag was unknown. Tupigny (1996) estimated that two million grey partridges were reared in France in 1995. However releases are mostly practised in regions where the species has almost disappeared (Reitz 2003a). In central northern France, where the species is still well represented, progressive hunting management has been practised since the mid-1980s (see Reitz 2003a) to ensure sustainable hunting (Aebischer 1997) and to preserve wild birds. Within this context, a survey of partridge populations assessing breeding density and reproductive success is conducted annually (see Reitz 1999, Bro et al. 2003). The primary objective of this survey is to calculate bag limits (quotas) to adjust hunting pressure to pair density and reproductive output at a local scale (Reitz 2003b).

In our paper, we use this long-term and wide-scale survey to portray the status of the grey partridge in central northern France, emphasising the large spatiotemporal variability. We present a map of 2000–2002 breeding densities at the ‘commune’ scale and assess both the 1994–2004 (long-term) and 1999–2004 (recent short-term) trends in densities for each ‘farming region’.


Field procedures

The French national partridge survey

Monitoring of grey partridge populations was initiated in the early 1980s in a few areas and was progressively extended to many other areas in central northern France. Spring censuses and brood surveys have been conducted every year to assess breeding density and reproductive success (see Reitz 1999, Bro et al. 2003).

Because the primary objective of this survey is to calculate hunting bag limits, these areas correspond to hunting estates where hunting management is undertaken to manage wild grey partridge populations; only few of these hunting estates practised releases of a small number of hand-reared birds for shooting purposes (Fig. 1). Therefore these areas were not selected at random or using a particular sampling procedure. However, extensive counts are carried out in some farming regions, hence they correctly reflect partridge status (Fig. 2 & Table 1, and see the sections ‘Statistical analyses’ steps 3a and 3b and ‘Discussion’).

Figure 1.

Central northern France with indications of the communes where counts were carried out in spring 1998, and where hand-reared birds were released for shooting purpose during the 1997/98 hunting season (from Reitz 2003a). The grey area shows the range where partridge populations were routinely surveyed and the black area shows Paris and its suburbs. See Figure 3 for the definition of French administrative divisions.


Figure 2.

Breeding density (in pairs/km2) of grey partridge populations at the commune scale in central northern France. Data are means from 2000–2002.


Table 1.

Levels of grey partridge density (pairs/km2, mean ± SE) in each farming region of central northern France in 1994–2004. Proportions of the communes and arable land sampled were estimated using data from 2000–2004. This information is given to assess data representativity. The proportion of arable land censused is reported as classes because the area actually censused may vary from year to year.


Table 1.



Figure 3.

The administrative division of communes and departments. Communes are nested within departments. Farming region is another division, independent of department, pooling communes whose farming characteristics are similar. Counts were carried out in three different types of sample plots within communes; both were representative of the area.


Spring counts

Spring censuses were carried out to estimate the breeding stock. Counts were performed in March, when birds had paired and before the crop cover was too high (in particular oilseed rape and winter cereal). We censused partridges that flushed from the sample plot while fields were beaten by a line of people (see Reitz 1999). To achieve a census as complete as possible, 20–50 people were needed to count one sample plot depending upon its area (ranging approximately within 80–250 ha). Sample plots were representative of the ‘commune’ (Fig. 3).

Spring counts were reported either as (i) the number of pairs, trios and single birds (where density levels were low) or (ii) the total number of birds. In the former case, the number of pairs was calculated as the number of pairs and trios plus the number of single birds divided by 2.1; in the latter case as the total number of birds divided by 2.1 (Reitz & Berger 1994). The number 2.1 corrects for the unbalanced sex ratio in spring (Birkan & Jacob 1988). The spring sex ratio was estimated in the field by examining pairs and single birds using binoculars.

Statistical analyses

We estimated the trend of breeding density as the regression slope of density (previously log-transformed) against year (continuous variable). We used an autoregressive error model to diagnose and correct for serial correlation due to time series (proc AUTOREG - first-order autoregressive error, maximum-likelihood method). Missing values in time series were not filled because the procedure permits embedded missing values for both the independent and dependent variables.

The statistical unit was the ‘commune’ (see Fig. 3); density level in the commune was the average of densities estimated on sample plots. Communes were pooled to estimate density trends in farming regions. Trends were estimated for both the 1994–2004 (long-term trend) and 1999–2004 (recent short-term trend) periods, using communes with at least eight and five year's data, respectively. Trend analysis was performed in three steps:

  1. a regression was performed for each commune. Then we combined the results of these separate analyses in a file (farming region, commune, slope of the regression and standard error (SE), r-square of the model (r2), length of the time series (N) and P-value testing whether the slope was null) to be analysed in step 2;

  2. we conducted a meta-analysis for each farming region to test whether the distribution of the slopes was significantly different from zero (proc UNIVARIATE - sign-rank test because assumptions of parametric tests were violated);

  3. a) because counts were not carried out in random areas (see the section ‘Field procedures’) and this may bias results, we tested the robustness of the meta-analysis result using a resampling procedure. A random sample of ca 75% of communes was drawn from a uniform distribution (if ranuni(−1) ≤0.75 then selected = 1 else selected = 0) for each farming region. The seed was the computer clock. A meta-analysis (step 2) was performed on the random sample;

    b) we ran all of procedure 3a) 100 times using an iterative macrovariable.

All statistical analyses were performed using SAS/STAT software (SAS Publishing 1999).


Range of breeding densities in 2000–2002

Breeding densities (of wild grey partridges) of > 50 pairs/km2, and even exceeding 70 pairs/km2, still occurred in central northern France in the early 2000s (see Fig. 2 and Table 1). However, in other areas, density levels were as low as a few pairs/km2.

Spatial variability

The map of mean 2000–2002 breeding densities showed sharp contrasts in density levels at a small spatial scale (see Fig. 2). High density (i.e. > 50 pairs/km2) areas were not gathered in a core region but were scattered both in northern and southern regions (see Fig. 2 and Table 1).

Trend patterns

Trend patterns were contrasting across farming regions (Table 2). As for density levels, positive and negative trends were not geographically gathered, but distributed as a mosaic. However, few trends were statistically significant, either because the sample size (number of communes sampled) was low or because trends were not obvious due to large year-to-year fluctuations in density levels (Fig. 4 and see Discussion).

Table 2.

Trend in grey partridge density in each farming region of central northern France. See text for explanation about statistical analyses (full meta-analysis: step 2, resampling procedure: step 3). Results of the resampling procedure are given when the sign-rank test probability of the full meta-analysis is significant and/or when the number of communes is higher than 10.


Table 2.



Figure 4.

Examples of spatio-temporal variability in grey partridge density (in pairs/km2). The lines refer to independent areas.


The four regions Ponthieu, Vimeu, Plateau picard and Champagne crayeuse showed an increase in partridge density in the long term. This result was driven by a recent increase in density for Plateau picard and Champagne crayeuse. Contrarily, partridge density decreased in the Perche and Beauce regions. Short-term and a long-term declines were observed in the Gâtinais and Drouais-Thymerais regions, respectively.


Density levels

Density levels of grey partridge are very contrasting from one commune to another (and even at an infra scale; E. Bro, unpubl. data). Areas with densities as high as 50 or even 70 pairs/100 ha still exist in the early 2000s, whereas densities declined to a few pairs/100 ha in other areas. High and low density areas are spatially distributed as a mosaic at a small spatial scale, suggesting that high densities result from local, not global factors. However, environmental factors determining such variability is beyond the scope of this paper. Relationships between density and habitat characteristics were recently investigated at three nested spatial scales and a paper reporting results is currently in preparation.

The levels of density commonly found in France, not only high densities, are quite favourable compared to those frequently reported from other European countries (Table 3). The Polish partridge population that ranks second in size in Europe after the French population (Aebischer & Kavanagh 1997, BirdLife International 2004) sharply declined during the 1990s and densities reached an average of a few pairs/100 ha in many regions (Panek 2005). Densities as high as ca 20 pairs/km2 or even exceeding 60 pairs/km2 were recently reported as partridge ‘hotspots’ in suburbs of Praha (Salek et al. 2004) and Frankfurt (Kugelschafter & Richarz 2001). But these areas seem to be spatially restricted, and large city suburbs are not designated as long-term wildlife conservation areas.

Table 3.

Levels of grey partridge breeding density in some European countries and USA in the 1990s and 2000s.


Trends in numbers

Grey partridge numbers are reported to decline at the national scale. Reitz (2003a) estimated that the overall abundance of the species had decreased by ca 20% during 1979–1998. An other independent source of data in France reported a 49% decline of partridge numbers between 1989 and 2001 (CRBPO 2005).

Decline in numbers can result from an overall decline in densities or/and a range contraction. The decline of the grey partridge in France seems to be a combination of the two phenomena. This work did not allow range assessment because counts were carried out in areas where partridge densities were high enough to encourage hunters to survey and manage wild populations, but Reitz (2003a) documented this point comparing two inquiries. He reported a range contraction of the species in France between 1979 and 1998. The grey partridge has declined most in the Bretagne, Lorraine, Franche-Comté, Limousin, Auvergne and Rhônes-Alpes regions. The situation is more complex in central northern France where trend patterns were contrasting at the regional scale. Densities were roughly stable over the last decade in all but a few regions where densities either decreased (Perche, Drouais-Thymerais, Beauce) or increased (Ponthieu, Vimeu, Champagne crayeuse, Plateau picard). These findings are similar to Reitz's results using independent data sets (Reitz 2003a). Indeed, he found that the proportion of communes with densities of > 15 pairs/100 ha increased between 1979 and 1998 whereas the proportion of communes with densities of 6–15 pairs/100 ha decreased, but he observed an overall decline. These convergent results provide confidence in our conclusions (opposite trends depending upon regions). Yet the problem of low-density areas (few pairs/100 ha) persists. Indeed when partridge densities reach low levels, hunters lose their interest in the species because they cannot hunt it any longer (unless they release hand-reared birds for shooting purposes), and they often stop the survey. The other available methods to monitor partridge populations (survey using farmer's observations (Brun et al. 1990), prospection of linear features (Brun et al. 1990), presence of faeces (Pinet et al. 1981) or male call counts (Panek 1998)) are time-consuming and except the first one, they are not extensively carried out into practice. As a consequence, long-term surveys are biased towards high density areas (i.e. central northern France) and population dynamics at low density are little documented. Unfortunately, other monitoring programmes, such as the STOC (CRBPO 2005) or the ACT (Boutin et al. 2003) are not suitable for the grey partridge and thus can not complete our survey at the national scale.

We estimated trends in density performing a meta-analysis on regression slopes of log-transformed density levels against years. This procedure may nevertheless be questioned for species such as the grey partridge whose population dynamics are highly fluctuating from year to year (see Fig. 4). Our long-term survey showed that a number of areas sustained very high densities (> 70 pairs/km2) only temporarily. Peaks often occur simultaneously in a number of areas (for instance Petit Caux in 1997 and Beauce in 1991; see Fig. 4) and are generally related to a good reproductive success the previous year (E. Bro, unpubl. data). A positive or a negative trend may result from such peaks when they occur at the beginning or at the end of the survey. Siriwardena et al. (1998) recommended the use of smoothed index series to solve the problem. We preferred to describe trend patterns providing the corresponding data (see Tables 1 and 2).

Management considerations

Together with other farmland birds, the grey partridge has been reported to be a species whose conservation status has worsened alarmingly (see BirdLife International 2004). Indeed, numbers have continued to decline over the last decade in western Europe despite the application of agro-environmental schemes in most countries (see Kleijn & Sutherland 2003). Moreover, the species is all the more exposed because it is huntable (listed on annex II of the Bird Directive). For all that, hunting is not necessarily the reason for the persisting decline. Sustainable hunting may be justified (see Ellison 1991, Aebischer 1997). Our survey of the grey partridge in farmlands shows firstly that high density wild populations still occur in intensively cultivated areas (cereal ecosystems where wheat yield may reach 120 Q/ha) where partridge hunting is culturally important. Secondly, it highlights that except in a few farming regions, densities did not particularly decline during the last decade but fluctuated from year to year. In most of central northern France, the species is likely to benefit from sustainable hunting in three ways:

  • Hunting provides financial resources for scientific research (carried out by the governmental Game & Wildlife Agency, ONCFS). The population dynamics of the grey partridge are uniquely well studied among farmland birds. Research involves a large-scale and long-term survey (this paper), large-scale experiments (see Bro et al. 2004) and widespread field management (Bro et al. 2004). Understanding the cause of its decline allows scientists to make recommendation about conservation and agricultural management (see Potts 1997). Some management prescriptions were included in recent CAP reforms.

  • Hunting management requires annual and local field data to attribute quotas to hunting estates, hence it provides long-term and wide-scale monitoring of partridge populations.

  • Hunters invest time and effort in managing farmland habitats and controlling predator abundance to increase hunting bags. This land management favours partridge abundance and productivity (Tapper et al. 1996), and this often results in higher densities in areas where the partridge is hunted than in areas where the partridge is not hunted. This is what N. Aebischer named “the paradox of wise use” (Aebischer 1997). Such generic conservation actions are likely to benefit other farmland species, also.

In other parts of France where the species has declined to near extinction, hunters should resist the temptation to release hand-reared birds for shooting purpose while continuing land management in order to try to preserve the last wild birds.


The French ‘grey partridge national network’ is a collaboration between the Federation Nationale des Chasseurs (FNC), the Fédérations Départementales des Chasseurs (FDC) and the Office National de la Chasse et de la Faune Sauvage (ONCFS). We acknowledge all field technicians of FDC and ONCFS and hunters who have been collecting the data for many years.



N. J. Aebischer 1997. Impact of hunting on the population dynamics of wild birds.-. Gibier Faune Sauvage/Game and Wildlife 14:183–200. Google Scholar


N. J. Aebischer and B. Kavanagh . 1997. Grey partridge.-. In W. J. M. Hagemeijer and M. J. Blair , editors. (Eds). The EBCC atlas of European Breeding Birds. Their distribution and abundance. Poyser. Great Britain. pp. 212–213. Google Scholar


BirdLife International 2004. Birds in Europe: population estimates, trends and conservation status.-. BirdLife International (BirdLife Conservation Series n°12). U.K. 374. pp. Google Scholar


M. Birkan and M. Jacob . 1988. La perdrix grise. Hatier. France. 284. pp. (In French). Google Scholar


J-M. Boutin, D. Roux, and C. Eraud . 2003. Breeding bird monitoring in France: the ACT survey.-. Ornis Hungarica 12–13:239–241. Google Scholar


E. Bro, B. Deldalle, M. Massot, F. Reitz, and S. Selmi . 2003. Density dependence of the reproductive success in the grey partridge Perdix perdix population in France: management implications.-. Wildlife Biology 9:93–102. Google Scholar


E. Bro, P. Mayot, E. Corda, and F. Reitz . 2004. Impact of habitat management on grey partridge populations: assessing wildlife cover using a multisite B.A.C.I. experiment.-. Journal of Applied Ecology 41:846–857. Google Scholar


J-C. Brun, P. Che, and J. Aubineau . 1990. Comparaison de trois méthodes de dénombrement de perdrix (Alectoris rufa et Perdix perdix) en milieu bocager. (In French with an English summary: Comparison of three census methods for partridges (Alectoris rufa and Perdix perdix) in a bocage habitat).-. Gibier Faune sauvage 7:127–144. Google Scholar


F. Buner, M. Jenny, N. Zbinden, and B. Naef-Daenzer . 2005. Ecologically enhanced areas - a key habitat structure for reintroduced grey partridges Perdix perdix.-. Biological Conservation 124:373–381. Google Scholar


L. Ellison 1991. Under what conditions can shooting of declining tetraonids be justified in France?.-. Gibier Faune Sauvage 8:353–366. Google Scholar


S. Farago 1998. Habitat improvement of Hungarian partridge populations (Perdix perdix): the Hungarian partridge conservation program (HPCP).-. Gibier Faune Sauvage/Game and Wildlife 15:145–156. Google Scholar


GCT 2004. The Game Conservancy Trust annual review of 2003, no 35. 104. pp. Google Scholar


M. Jenny, B. Lugrin, and J. L. Regamey . 1998. Habitat restoration programme for agricultural-land breeding birds in Switzerland.-. Gibier Faune Sauvage/Game and Wildlife 15:547–554. Google Scholar


W. Kaiser 1998. Autumn-winter habitat use by radio-tagged grey partridges (Perdix perdix) in north Bavaria.-. Gibier Faune Sauvage/Game and Wildlife 15:471–479. Google Scholar


B. Kavanagh 1998. Can the Irish grey partridge (Perdix perdix) be saved?.-. Gibier Faune Sauvage/Game and Wildlife 15:533–546. Google Scholar


E. Klansek 2002. Effects of landscape structure on Perdix perdix in Austria: outline and outlook.-. Zeitschrift für Jagd-wissenschaft 48:(suppl). 340–345. Google Scholar


D. Kleijn and W. J. Sutherland . 2003. How effective are European agri-environment schemes in conserving and promoting biodiversity?.-. Journal of Applied Ecology 40:947–969. Google Scholar


K. Kugelschafter and K. Richarz . 2001. The current and past grey partridge (Perdix perdix) population in Hesse (Germany).-. Game and Wildlife Science 18:231–241. Google Scholar


C. Matteucci and S. Toso . 1985. Historical review and status update of gray partridge in Italy.-. In K. E. Church, R. E. Warner, and S. J. Brady , editors. (Eds). Perdix V: gray partridge and ring-necked pheasant workshop. Kansas Department Wildlife and Parks. Emporia. pp. 41–46. Google Scholar


A. Meriggi, D. Montagna, D. Zacchetti, C. Matteucci, and S. Toso . 1985. Population dynamics of the gray partridge in relation to agriculture and weather in northern Italy.-. In K. E. Church, R. E. Warner, and S. J. Brady , editors. (Eds). Perdix V: gray partridge and ring-necked pheasant workshop. Kansas Department of Wildlife and Parks. Emporia. pp. 241–256. Google Scholar


H. Nösel 1992. Grey partridge (Perdix perdix) population dynamics in east Germany.-. Gibier Faune Sauvage 9:351–357. Google Scholar


ONCFS 2000. Enquête nationale sur les tableaux de chasse à tir saison 1998–1999. Faune Sauvage 251:216. pp. (In French). Google Scholar


M. Panek 1998. Use of call counts for estimating spring density of the grey partridge Perdix perdix.-. Acta Ornithologica 33:143–148. Google Scholar


M. Panek 2005. Demography of grey partridge Perdix perdix in Poland in the years 1991–2004: reasons of population decline.-. European Journal of Wildlife Research 51:14–18. Google Scholar


M. Panek and R. Kamienarz . 1998. Agricultural landscape structure and density of grey partridge (Perdix perdix) populations in Poland.-. Gibier Faune Sauvage/Game and Wildlife 15:309–320. Google Scholar


E. Papaevangelou, C. Thomaides, G. Handrinos, and A. Haralambides . 2001. Status of partridge (Alectoris and Perdix) species in Greece.-. Game and Wildlife Science 18:253–260. Google Scholar


J-M. Pinet, F. Reitz, and J-C. Ricci . 1981. Les indices copro-logiques de la perdrix grise, indicateurs de la fréquentation et guides pour l'aménagement d'un territoire.-. Bulletin Scientifique et Technique de l'O.N.C. Nov pp. 43–55. (In French). Google Scholar


G. R. Potts 1997. Cereal farming, pesticides and grey partridge.-. In D. J. Pain and M. W. Pienkowski , editors. (Eds.). Farming and birds in Europe. The common agricultural policy and its implications for bird conservation. Academic Press. U.K. pp. 150–177. Google Scholar


G. R. Potts and N. J. Aebischer . 1995. Population dynamics of the grey partridge Perdix perdix 1793–1993: monitoring, modelling and management.-. Ibis 137:Suppl.S29–S37. Google Scholar


F. Reitz 1999. The status of partridges in north-central France.-. Hungarian Small Game Bulletin 5:151–163. Google Scholar


F. Reitz 2000. La perdrix grise. Enquête nationale sur les tableaux de chasse à tir saison 1998–1999.-. Faune Sauvage 251:38–45. (In French). Google Scholar


F. Reitz 2003a. Le statut communal de la perdrix grise et de la perdrix rouge en France: résultats d'une enquête.-. Faune Sauvage 258:25–33. (In French). Google Scholar


F. Reitz 2003b. La gestion quantitative des perdrix grises en plaine.-. Faune Sauvage 260:14–20. (In French). Google Scholar


F. Reitz and F. Berger . 1994. Le suivi des populations de perdrix en 1993 dans le Nord, le Bassin parisien et le Centre.-. Bulletin Mensuel de l'O.N.C 186:13–22. (In French). Google Scholar


G. Rocamora and D. Yeatman-Berthelot . 1999. Oiseaux menacés et à surveiller en France. Liste rouge et priorité. Populations, tendances, menaces et conservation. Société d'Etudes Ornithologiques de France/Ligue pour la Protection des Oiseaux. Paris. 598. pp. (In French). Google Scholar


J. J. Rotella, J. T. Ratti, K. P. Reese, M. L. Taper, and B. Dennis . 1996. Long-term population analysis of gray partridge in eastern Washington.-. Journal of Wildlife Management 60:817–825. Google Scholar


M. Salek, P. Marhoul, and J. Pintir . 2002. Spring to autumn home range and habitat use of a high density population of the grey partridge (Perdix perdix) in Praha, Czech Republic.-. Folia Zoologica 51:299–306. Google Scholar


M. Salek, P. Marhoul, J. Pintir, T. Kopecky, and L. Slaby . 2004. Importance of wasteland patches for the grey partridge Perdix perdix in suburban areas.-. Acta Oecologica 25:23–33. Google Scholar


SAS Publishing 1999. SAS/STAT User's Guide, Version 8, Volumes 1, 2 and 3. SAS Publishing. Cary, NC, USA. 2301. pp. Google Scholar


G. M. Siriwardena, S. R. Baillie, S. T. Buckland, R. M. Fewster, J. H. Marchant, and J. D. Wilson . 1998. Trends in the abundance of farmland birds: a comparative comparison of smoothed Common Birds Census indices.-. Journal of Applied Ecology 35:24–43. Google Scholar


S. C. Tapper, G. R. Potts, and M. H. Brockless . 1996. The effects of an experimental reduction in predation pressure on the breeding success and population density of grey partridges Perdix perdix.-. Journal of Applied Ecology 33:965–978. Google Scholar


S. S. Traylor, K. E. Church, and D. L. Draheim . 2001. Range expansion of grey partridge (Perdix perdix) in the central Great Plains, USA.-. Game and Wildlife Science 18:243–252. Google Scholar


G. M. Tucker and M. F. Heath . 1994. Birds in Europe: their conservation status.-. Birdlife Conservation Series no 3. Cambridge. Birdlife International. 600. pp. Google Scholar


B. Tupigny 1996. Production et commercialisation des gibiers. Tome 1, gibiers à plumes: faisan, perdrix, canard colvert. Institut Technique d'Aviculture. Paris. 119. pp. (In French). Google Scholar


A. Turtola 1998. Improving grey partridge (Perdix perdix) habitat by set-aside management in Finland.-. Gibier Faune Sauvage/Game and Wildlife 15:455–562. Google Scholar


[1] Article accepted for publication in Game and Wildlife Science (GWS) prior to the merger between Wildlife Biology and GWS. Therefore, this article has not been peer-reviewed by Wildlife Biology Associate Editors

Elisabeth Bro, François Reitz, and Philippe Landry "Grey partridge Perdix perdix population status in central northern France: spatial variability in density and 1994–2004 trend," Wildlife Biology 11(4), 287-298, (1 December 2005).[287:GPPPPS]2.0.CO;2
Published: 1 December 2005

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