Comments on Tixier, P. et al., 2004. “SIMBA-POP: A cohort population model for long-term simulation of banana crop harvest” [Ecol. Model. 180, 407–417]

2010 ◽  
Vol 221 (12) ◽  
pp. 1648
Author(s):  
Andrés Ochoa
2004 ◽  
Vol 180 (2-3) ◽  
pp. 407-417 ◽  
Author(s):  
P. Tixier ◽  
E. Malezieux ◽  
M. Dorel

Oryx ◽  
2012 ◽  
Vol 46 (3) ◽  
pp. 431-437 ◽  
Author(s):  
Carmina E. Gutiérrez-González ◽  
Miguel Á. Gómez-Ramírez ◽  
Carlos A. López-González

AbstractOur objective in this study was to determine the density of the jaguar Panthera onca from camera-trap data, using an open population model, in a private protected natural area, the Northern Jaguar Reserve, and 10 adjoining cattle ranches in the state of Sonora, Mexico. The region is considered a long–term jaguar conservation unit. As well as being the most northerly recorded reproductive population of the jaguar, the arid habitat of this region is atypical for the species. During 16 months of sampling we identified 10 individual jaguars and the data met the three main assumptions of open population models. The estimated mean density was 1.05±SE 0.4 individuals per 100 km2, with a constant survival probability of 0.94 and capture probability of 0.23. This estimate of density is lower than reported in studies of the jaguar from more southerly locations in Mexico, Belize, Costa Rica, Bolivia and Brazil but cannot be attributed to a single factor even though in general there is an apparent relationship between jaguar density and precipitation. The main objectives of the management of the Northern Jaguar Reserve are to reduce the impact of cattle and restore jaguar habitat, with strategies focused on water retention, removal of invasive grass, reforestation and environmental education. Livestock have been gradually excluded since 2003 and, combined with the protection provided under the agreements with the surrounding ranches, the area is now a suitable place for long-term studies of the jaguar.


2007 ◽  
Vol 26 (3) ◽  
pp. 219-227 ◽  
Author(s):  
P.R. Westerman ◽  
A. van Ast ◽  
T.J. Stomph ◽  
W. van der Werf

2015 ◽  
Vol 4 (9) ◽  
pp. 516-526 ◽  
Author(s):  
J Berkhout ◽  
JA Stone ◽  
KM Verhamme ◽  
BH Stricker ◽  
MC Sturkenboom ◽  
...  

BMJ Open ◽  
2013 ◽  
Vol 3 (11) ◽  
pp. e003630 ◽  
Author(s):  
Giovanni Veronesi ◽  
Francesco Gianfagna ◽  
Lloyd E Chambless ◽  
Simona Giampaoli ◽  
Giuseppe Mancia ◽  
...  

1985 ◽  
Vol 42 (8) ◽  
pp. 1371-1379 ◽  
Author(s):  
D. Ruppert ◽  
R. L Reish ◽  
R. B. Deriso ◽  
R. J. Carroll

A model including an age-structure, a stochastic egg-recruitment relationship, density-dependent juvenile growth, age-dependent fishing mortality, and fecundity dependent upon size as well as age was used to investigate three types of harvesting strategies: constant yearly catch policies, constant fishing mortality rate policies, and "egg escapement" policies, which are defined in the article. Because of stochastic recruitment, constant yearly catch policies appear unsuitable for managing Atlantic menhaden (Brevoortia tyrannus). Both other types of policies are suitable, but the egg escapement policies have higher long-term average catches. Using decision theory, we investigated risks due to the randomness of recruitment and to the estimation errors for the biographical parameters in our model. The risks appear to be acceptable.


Weed Research ◽  
2008 ◽  
Vol 48 (4) ◽  
pp. 329-339 ◽  
Author(s):  
T A VAN MOURIK ◽  
F J J A BIANCHI ◽  
W VAN DER WERF ◽  
T J STOMPH

2020 ◽  
Author(s):  
Nicholas Howden ◽  
Fred Worrall ◽  
Tim Burt ◽  
Helen Jarvie ◽  
Francesca Pianosi

<p>Phosphorus (P) is critical for food production but rising P inputs to agricultural land have contributed to eutrophication of fresh and marine waters. Concurrently, wastewater effluent from increasing populations has also become a major P input to natural waters, particularly in urbanised catchments. This study considers the long-term phosphorus budget of the River Thames catchment from 1867 to the present. We combine databases of agricultural land use, human population and river monitoring to develop a phosphorus budget model for the gauged catchment area (9,948 km<sup>2</sup>) and identify key inputs, outputs and transfers over the period. We quantify P imports and exports of fertilizer, food, feedstuffs, and industrial products (1867-2017), along with direct discharge of fluvial P at the tidal limit (1936-2017).</p><p>Net P input to land from animal production was essentially stable at ~1,700 tonnes P until 1940, after which there was a steady rise, peaking at approximately 3,800 tonnes P in the early 1970s. Since then, P inputs to land have fallen to a current stable level of ~2,200 tonnes P. This represents a cumulative net input to land of 350 kT P since 1867. Whilst this input is somewhat counterbalanced by losses to the fluvial system and crop harvest, there is nevertheless a large P legacy in catchment soils.</p><p>Net inputs from wastewater (urine and faeces) rose steadily from 0.8 kT in 1936 to 2 kT in 2010, whilst the marked change occurred in relation to P in detergents rising from zero in 1950 to a peak of ~2kT in 1987, since when there has been a gradual decline to <1 kT at present. The total wastewater effluent contribution rose from 0.8 kT in 1936 to a peak of 3.4 kT at the end of the 1980s. The Urban Waste Water Treatment Directive (91/271/EEC) enforced enhanced removal of P in wastewater from the early 1990s, which led to an immediate, sharp decrease in wastewater contribution of 1 kT P since when there has been a steady decline to 0.4 kT at present. This has shifted the environmental pathway of wastewater P from discharge to rivers to accumulation in sludge which is now largely disposed of by application to agricultural land thus adding to the P legacy in catchment soils.</p><p> </p><p>Our analysis of the Thames P budget will end with a discussion of uncertainties in the P model, and the sensitivity of our overall conclusions to assumptions about model structure and parameters applied to our historical records.</p><p> </p><p> </p><p> </p>


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