A preconcentration procedure for heavy metal ions in biological and water samples has been presented. The procedure is based on the sorption of [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+], and [Pb.sup.2+] on cellulose nanoparticles modified with folic acid. The prepared adsorbent was characterized by FT-IR, SEM, TEM, and BET measurements. Potentiometric titration is used to prove the complexation between metal ions and the modified cellulose as well as to calculate the cation-exchange capacity of the sorbent. The influences of the analytical parameters including pH, amount of adsorbent, shaking time, temperature, conditions of desorption, and the effects of matrix ions were studied. Under the optimized conditions, the calibration curves for [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+], and [Pb.sup.2+] were linear in the range of 2.7-200, 0.5-50, 0.37-150, and 10-300 µg [L.sup.-1], respectively. The detection limits (3s, n = 10) for [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+], and [Pb.sup.2+] were 0.81, 0.15, 0.11, and 3.9 µg [L.sup.-1], respectively. The proposed method offers a preconcentration factor of 200 for all of the ions studied and an enhancement factor for [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+], and [Pb.sup.2+] of 40.0, 30.8, 40.4, and 34.2, respectively. The accuracy of the suggested method was tested by analyzing spiked samples. The method was successfully applied to the determination of these metal ions in water and blood samples. Key words: modified cellulose nanoparticles, folic acid, solid-phase extraction, trace metal ions, atomic absorption spectrometry. Nous presentons une procedure de preconcentration d'ions de metaux lourds dans des echantillons biologiques et des echantillons d'eau. La procedure repose sur la sorption d'ions [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+] et [Pb.sup.2+] sur des nanoparticules de cellulose modifiee par l'acide folique. Nous avons caracterise l'adsorbant par des analyses FT-IR, MEB, MET et BET. Nous avons employe la technique de titrage potentiometrique pour faire la preuve de la complexation entre les ions metalliques et la cellulose modifiee ainsi que pour calculer la capacite d'echange cationique du sorbant. Nous avons etudie l'influence de parametres analytiques comme le pH, de la quantite d'adsorbant, du temps d'agitation, de la temperature, des conditions de desorption et des effets des ions de la matrice. En conditions optimisees, les courbes de calibration des ions [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+] et [Pb.sup.2+] etaient lineaires dans les intervalles de concentrations de 2,7 a 200, de 0,5 a 50, de 0,37 a 150 et de 10 a 300 µg [L.sup.-1] respectivement. Les limites de detection (3s, n = 10) des ions [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+] et [Pb.sup.2+] etaient de 0,81, 0,15, 0,11 et 3,9 µg [L.sup.-1] respectivement. La methode proposee permet d'obtenir un facteur de preconcentration de 200 pour tous les ions a l'essai et un facteur d'enrichissement des ions [Cu.sup.2+], [Cd.sup.2+], [Hg.sup.2+] et [Pb.sup.2+] de 40,0, 30,8, 40,4 et 34.2 respectivement. Nous avons mis a l'epreuve l'exactitude de la methode proposee en analysant des echantillons dopes. La methode a permis de doser avec succes ces ions metalliques dans des echantillons d'eau et de sang. [Traduit par la Redaction] Mots-cles: nanoparticules de cellulose modifiee, acide folique, extraction en phase solide, ions de metaux traces, spectrometrie d'absorption atomique., Introduction Trace analysis of metal ions in real samples is still difficult due to their low concentrations as well as the matrix interference. This issue can be resolved by preconcentration [...]