31 research outputs found
Structure Features of Bismuth Films Doped with Tellurium
The influence of doping degree on the structural characteristics of bismuth films doped with tellurium
in the concentration range 0.005-0.150 at. % Te and the thickness range 0.3-0.7 Β΅m is studied at present
article. Authors have established that an increase of the doping degree with tellurium in bismuth films
leads to a significant decreasing of the growth figures. The weak influence of annealing on the crystallite
size of bismuth films doped with tellurium indicates their high temporal stability of the structure
Baikal-GVD
We present the status of the Gigaton Volume Detector in Lake Baikal (Baikal-GVD) designed for the detection of high energy neutrinos of astrophysical origin. The telescope consists of functionally independent clusters, sub-arrays of optical modules (OMs), which are connected to shore by individual electro-optical cables. During 2015 the GVD demonstration cluster, comprising 192 OMs, has been successfully operated in Lake Baikal. In 2016 this array was upgraded to baseline configuration of GVD cluster with 288 OMs arranged on eight vertical strings. Thus the instrumented water volume has been increased up to about 5.9 Mtons. The array was commissioned in early April 2016 and takes data since then. We describe the configuration and design of the 2016 array. Preliminary results obtained with data recorded in 2015 are also discussed
ΠΡΡΠ΅ΠΊΡΠΈΠ²Π½ΠΎΡΡΡ ΡΡΠ΅ΡΡΠ°Π»ΡΠ½ΠΎΠΉ ΡΠ½Π΄ΠΎΡΡΠΈΠ½ΠΊΡΠ΅ΡΠΎΠΏΠ»Π°ΡΡΠΈΠΊΠΈ Ρ Π΄Π΅ΡΠ΅ΠΉ Ρ Π½Π΅Π΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ΠΌ ΠΌΠΎΡΠΈ ΠΏΡΠΈ ΠΌΠΈΠ΅Π»ΠΎΠ΄ΠΈΡΠΏΠ»Π°Π·ΠΈΠΈ ΠΈ ΡΠΏΠΈΡΠΏΠ°Π΄ΠΈΠΈ
BACKGROUND: Periurethral injections of various materials in the treatment of stress urinary incontinence have been known since 1938. In the literature, we could not find reports of endosurgical correction of urinary incontinence as the main method of treatment in children with myelodysplasia and epispadias and a pathogenetically based examination algorithm to predict the result of the injection, taking into account the endoscopic technique and volume of the injected drug.
AIM: To present an assessment of long-term results, i.e., correction of stress urinary incontinence in children with myelodysplasia and epispadias, after endoimplantation of a stable synthetic volume-forming polymer.
MATERIALS AND METHODS: The study analyzed 38 patients (517 years old) with urinary incontinence with myelodysplasia and epispadias: boys and girls with epispadias (n = 9 and n = 3, respectively) and with myelodysplasia (n = 10 and n = 16), respectively. For diagnostic purposes, clinical and instrumental (excretory urography, cystography, cystoscopy, uroflowmetry, electrophysiological, and urodynamic) examination methods were used. To correct incontinence, intra- and paraurethral endoinjections of a stable polyacrylamide mesh polymer with silver ions were performed.
RESULTS: According to the literature, the effectiveness of the intraurethral administration of stable implants with urinary incontinence in catamnesis for up to 12 months reached 50%; with longer follow-up, positive results did not exceed 40% of observations. In this study, complete retention of urine was achieved in 25 (66%) children. Satisfactory result (incontinence in the afternoon up to 40 mL) was observed in 8 (21%) children, and unsatisfactory in 5 (13%) children.
DISCUSSION: Indications for endosphincteroplasty in children with stress incontinence having myelodysplasia and epispadias with a stable implant should be determined considering urodynamics, blood circulation, innervation, and functional (urethral profilometry) parameters in the detrusor-sphincters-pelvic floor system.
CONCLUSIONS: In patients with myelodysplasia and epispadias with isolated insufficiency of urethral sphincters, surgical treatments can be performed independently, and their effectiveness can reach 70%.ΠΠΊΡΡΠ°Π»ΡΠ½ΠΎΡΡΡ. ΠΠ΅ΡΠΈΡΡΠ΅ΡΡΠ°Π»ΡΠ½ΡΠ΅ ΠΈΠ½ΡΠ΅ΠΊΡΠΈΠΈ ΡΠ°Π·Π»ΠΈΡΠ½ΡΡ
ΠΌΠ°ΡΠ΅ΡΠΈΠ°Π»ΠΎΠ² Π² Π»Π΅ΡΠ΅Π½ΠΈΠΈ ΠΏΠ°ΡΠΈΠ΅Π½ΡΠΎΠ² ΡΠΎ ΡΡΡΠ΅ΡΡΠΎΠ²ΡΠΌ Π½Π΅Π΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ΠΌ ΠΌΠΎΡΠΈ ΠΈΠ·Π²Π΅ΡΡΠ½Ρ Ρ 1938 Π³. Π Π»ΠΈΡΠ΅ΡΠ°ΡΡΡΠ½ΡΡ
ΠΈΡΡΠΎΡΠ½ΠΈΠΊΠ°Ρ
Π½Π°ΠΌ Π½Π΅ ΡΠ΄Π°Π»ΠΎΡΡ Π²ΡΡΡΠ΅ΡΠΈΡΡ ΡΠΎΠΎΠ±ΡΠ΅Π½ΠΈΠΉ ΠΎΠ± ΡΠ½Π΄ΠΎΡ
ΠΈΡΡΡΠ³ΠΈΡΠ΅ΡΠΊΠΎΠΉ ΠΊΠΎΡΡΠ΅ΠΊΡΠΈΠΈ Π½Π΅Π΄Π΅ΡΠΆΠ°Π½ΠΈΡ ΠΌΠΎΡΠΈ ΠΏΡΠΈ ΠΌΠΈΠ΅Π»ΠΎΠ΄ΠΈΡΠΏΠ»Π°Π·ΠΈΠΈ ΠΈ ΡΠΏΠΈΡΠΏΠ°Π΄ΠΈΠΈ Ρ Π΄Π΅ΡΠ΅ΠΉ ΠΊΠ°ΠΊ ΠΎΡΠ½ΠΎΠ²Π½ΠΎΠ³ΠΎ ΠΌΠ΅ΡΠΎΠ΄Π° Π»Π΅ΡΠ΅Π½ΠΈΡ, ΠΏΠ°ΡΠΎΠ³Π΅Π½Π΅ΡΠΈΡΠ΅ΡΠΊΠΈ ΠΎΠ±ΠΎΡΠ½ΠΎΠ²Π°Π½Π½ΠΎΠ³ΠΎ Π°Π»Π³ΠΎΡΠΈΡΠΌΠ° ΠΎΠ±ΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ Π΄Π»Ρ ΠΏΡΠΎΠ³Π½ΠΎΠ·ΠΈΡΠΎΠ²Π°Π½ΠΈΡ ΡΠ΅Π·ΡΠ»ΡΡΠ°ΡΠ° ΠΈΠ½ΡΠ΅ΠΊΡΠΈΠΈ Ρ ΡΡΠ΅ΡΠΎΠΌ ΡΠ½Π΄ΠΎΡΠΊΠΎΠΏΠΈΡΠ΅ΡΠΊΠΎΠΉ ΡΠ΅Ρ
Π½ΠΈΠΊΠΈ ΠΈ ΠΎΠ±ΡΠ΅ΠΌΠ° Π²Π²Π΅Π΄Π΅Π½Π½ΠΎΠ³ΠΎ ΠΏΡΠ΅ΠΏΠ°ΡΠ°ΡΠ°.
Π¦Π΅Π»Ρ ΠΎΡΠ΅Π½ΠΈΡΡ ΠΎΡΠ΄Π°Π»Π΅Π½Π½ΡΠ΅ ΡΠ΅Π·ΡΠ»ΡΡΠ°ΡΡ ΠΊΠΎΡΡΠ΅ΠΊΡΠΈΠΈ ΡΡΡΠ΅ΡΡΠΎΠ²ΠΎΠ³ΠΎ Π½Π΅Π΄Π΅ΡΠΆΠ°Π½ΠΈΡ ΠΌΠΎΡΠΈ Ρ Π΄Π΅ΡΠ΅ΠΉ Ρ ΠΌΠΈΠ΅Π»ΠΎΠ΄ΠΈΡΠΏΠ»Π°Π·ΠΈΠ΅ΠΉ ΠΈ ΡΠΏΠΈΡΠΏΠ°Π΄ΠΈΠ΅ΠΉ ΠΏΠΎΡΠ»Π΅ ΡΠ½Π΄ΠΎΠΈΠΌΠΏΠ»Π°Π½ΡΠ°ΡΠΈΠΈ ΡΡΠ°Π±ΠΈΠ»ΡΠ½ΠΎΠ³ΠΎ ΡΠΈΠ½ΡΠ΅ΡΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ ΠΎΠ±ΡΠ΅ΠΌΠΎΠΎΠ±ΡΠ°Π·ΡΡΡΠ΅Π³ΠΎ ΠΏΠΎΠ»ΠΈΠΌΠ΅ΡΠ°.
ΠΠ°ΡΠ΅ΡΠΈΠ°Π»Ρ ΠΈ ΠΌΠ΅ΡΠΎΠ΄Ρ. ΠΠ±ΡΠ΅ΠΊΡΠΎΠΌ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ Π±ΡΠ»ΠΈ 38 ΠΏΠ°ΡΠΈΠ΅Π½ΡΠΎΠ² (517 Π»Π΅Ρ) Ρ Π½Π΅Π΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ΠΌ ΠΌΠΎΡΠΈ Ρ ΠΌΠΈΠ΅Π»ΠΎΠ΄ΠΈΡΠΏΠ»Π°Π·ΠΈΠ΅ΠΉ ΠΈ ΡΠΏΠΈΡΠΏΠ°Π΄ΠΈΠ΅ΠΉ: ΠΌΠ°Π»ΡΡΠΈΠΊΠΎΠ² Ρ ΡΠΏΠΈΡΠΏΠ°Π΄ΠΈΠ΅ΠΉ 9, Π΄Π΅Π²ΠΎΡΠ΅ΠΊ 3; Ρ ΠΌΠΈΠ΅Π»ΠΎΠ΄ΠΈΡΠΏΠ»Π°Π·ΠΈΠ΅ΠΉ ΠΌΠ°Π»ΡΡΠΈΠΊΠΎΠ² 10, Π΄Π΅Π²ΠΎΡΠ΅ΠΊ 16. Π‘ Π΄ΠΈΠ°Π³Π½ΠΎΡΡΠΈΡΠ΅ΡΠΊΠΎΠΉ ΡΠ΅Π»ΡΡ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π»ΠΈ ΠΊΠ»ΠΈΠ½ΠΈΡΠ΅ΡΠΊΠΈΠ΅, ΠΈΠ½ΡΡΡΡΠΌΠ΅Π½ΡΠ°Π»ΡΠ½ΡΠ΅ (ΡΠΊΡΠΊΡΠ΅ΡΠΎΡΠ½ΡΡ ΡΡΠΎΠ³ΡΠ°ΡΠΈΡ, ΡΠΈΡΡΠΎΠ³ΡΠ°ΡΠΈΡ, ΡΠΈΡΡΠΎΡΠΊΠΎΠΏΠΈΡ, ΡΡΠΎΡΠ»ΠΎΡΠΌΠ΅ΡΡΠΈΡ, ΡΠ»Π΅ΠΊΡΡΠΎΡΠΈΠ·ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΠ΅ ΠΈ ΡΡΠΎΠ΄ΠΈΠ½Π°ΠΌΠΈΡΠ΅ΡΠΊΠΈΠ΅) ΠΌΠ΅ΡΠΎΠ΄Ρ ΠΎΠ±ΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ. ΠΠ»Ρ ΠΊΠΎΡΡΠ΅ΠΊΡΠΈΠΈ ΠΈΠ½ΠΊΠΎΠ½ΡΠΈΠ½Π΅Π½ΡΠΈΠΈ Π²ΡΠΏΠΎΠ»Π½ΡΠ»ΠΈ Π²Π½ΡΡΡΠΈ- ΠΈ ΠΏΠ°ΡΠ°ΡΡΠ΅ΡΡΠ°Π»ΡΠ½ΡΡ ΡΠ½Π΄ΠΎΠΈΠ½ΡΠ΅ΠΊΡΠΈΡ ΡΡΠ°Π±ΠΈΠ»ΡΠ½ΠΎΠ³ΠΎ ΠΏΠΎΠ»ΠΈΠ°ΠΊΡΠΈΠ»Π°ΠΌΠΈΠ΄Π½ΠΎΠ³ΠΎ ΡΠ΅ΡΡΠ°ΡΠΎΠ³ΠΎ ΠΏΠΎΠ»ΠΈΠΌΠ΅ΡΠ° Ρ ΠΈΠΎΠ½Π°ΠΌΠΈ ΡΠ΅ΡΠ΅Π±ΡΠ°.
Π Π΅Π·ΡΠ»ΡΡΠ°ΡΡ. ΠΠΎ Π΄Π°Π½Π½ΡΠΌ Π»ΠΈΡΠ΅ΡΠ°ΡΡΡΡ, ΡΡΡΠ΅ΠΊΡΠΈΠ²Π½ΠΎΡΡΡ Π²Π½ΡΡΡΠΈΡΡΠ΅ΡΡΠ°Π»ΡΠ½ΠΎΠ³ΠΎ Π²Π²Π΅Π΄Π΅Π½ΠΈΡ ΡΡΠ°Π±ΠΈΠ»ΡΠ½ΡΡ
ΠΈΠΌΠΏΠ»Π°Π½ΡΠΎΠ² ΠΏΡΠΈ Π½Π΅Π΄Π΅ΡΠΆΠ°Π½ΠΈΠΈ ΠΌΠΎΡΠΈ Π² ΠΊΠ°ΡΠ°ΠΌΠ½Π΅Π·Π΅ Π΄ΠΎ 12 ΠΌΠ΅Ρ. Π΄ΠΎΡΡΠΈΠ³Π°Π»Π° 50 %, ΠΏΡΠΈ Π±ΠΎΠ»Π΅Π΅ Π΄Π»ΠΈΡΠ΅Π»ΡΠ½ΠΎΠΌ Π½Π°Π±Π»ΡΠ΄Π΅Π½ΠΈΠΈ ΠΏΠΎΠ»ΠΎΠΆΠΈΡΠ΅Π»ΡΠ½ΡΠ΅ ΡΠ΅Π·ΡΠ»ΡΡΠ°ΡΡ Π½Π΅ ΠΏΡΠ΅Π²ΡΡΠ°Π»ΠΈ 40 % Π½Π°Π±Π»ΡΠ΄Π΅Π½ΠΈΠΉ. Π ΠΏΡΠ΅Π΄ΡΡΠ°Π²Π»Π΅Π½Π½ΠΎΠΉ ΡΠ°Π±ΠΎΡΠ΅ ΠΏΠΎΠ»Π½ΠΎΠ΅ ΡΠ΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ ΠΌΠΎΡΠΈ Π΄ΠΎΡΡΠΈΠ³Π½ΡΡΠΎ Ρ 25 Π΄Π΅ΡΠ΅ΠΉ (66 %). Π£Π΄ΠΎΠ²Π»Π΅ΡΠ²ΠΎΡΠΈΡΠ΅Π»ΡΠ½ΡΠΉ ΡΠ΅Π·ΡΠ»ΡΡΠ°Ρ (ΠΈΠ½ΠΊΠΎΠ½ΡΠΈΠ½Π΅Π½ΡΠΈΡ Π΄Π½Π΅ΠΌ Π΄ΠΎ 40 ΠΌΠ») Π·Π°ΡΠ΅Π³ΠΈΡΡΡΠΈΡΠΎΠ²Π°Π½ Π² 8 Π½Π°Π±Π»ΡΠ΄Π΅Π½ΠΈΡΡ
(21 %). ΠΠ΅ΡΠ΄ΠΎΠ²Π»Π΅ΡΠ²ΠΎΡΠΈΡΠ΅Π»ΡΠ½ΡΠΉ ΡΠ΅Π·ΡΠ»ΡΡΠ°Ρ Ρ 5 Π΄Π΅ΡΠ΅ΠΉ (13 %).
ΠΠ±ΡΡΠΆΠ΄Π΅Π½ΠΈΠ΅. ΠΠΎΠΊΠ°Π·Π°Π½ΠΈΡ ΠΊ ΡΠ½Π΄ΠΎΡΡΠΈΠ½ΠΊΡΠ΅ΡΠΎΠΏΠ»Π°ΡΡΠΈΠΊΠ΅ Ρ Π΄Π΅ΡΠ΅ΠΉ ΡΠΎ ΡΡΡΠ΅ΡΡΠΎΠ²ΠΎΠΉ ΠΈΠ½ΠΊΠΎΠ½ΡΠΈΠ½Π΅Π½ΡΠΈΠ΅ΠΉ ΠΏΡΠΈ ΠΌΠΈΠ΅Π»ΠΎΠ΄ΠΈΡΠΏΠ»Π°Π·ΠΈΠΈ ΠΈ ΡΠΏΠΈΡΠΏΠ°Π΄ΠΈΠΈ ΡΡΠ°Π±ΠΈΠ»ΡΠ½ΡΠΌ ΠΈΠΌΠΏΠ»Π°Π½ΡΠΎΠΌ Π΄ΠΎΠ»ΠΆΠ½Ρ ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΡΡΡΡ Ρ ΡΡΠ΅ΡΠΎΠΌ ΡΡΠΎΠ΄ΠΈΠ½Π°ΠΌΠΈΠΊΠΈ, ΠΊΡΠΎΠ²ΠΎΠΎΠ±ΡΠ°ΡΠ΅Π½ΠΈΡ, ΠΈΠ½Π½Π΅ΡΠ²Π°ΡΠΈΠΈ ΠΈ ΡΡΠ½ΠΊΡΠΈΠΎΠ½Π°Π»ΡΠ½ΡΡ
(ΡΡΠ΅ΡΡΠ°Π»ΡΠ½Π°Ρ ΠΏΡΠΎΡΠΈΠ»ΠΎΠΌΠ΅ΡΡΠΈΡ) ΠΏΠ°ΡΠ°ΠΌΠ΅ΡΡΠΎΠ² Π² ΡΠΈΡΡΠ΅ΠΌΠ΅ Π΄Π΅ΡΡΡΠ·ΠΎΡ ΡΡΠΈΠ½ΠΊΡΠ΅ΡΡ ΡΠ°Π·ΠΎΠ²ΠΎΠ΅ Π΄Π½ΠΎ.
ΠΠ°ΠΊΠ»ΡΡΠ΅Π½ΠΈΠ΅. ΠΠΏΠ΅ΡΠ°ΡΠΈΠΈ Π΄Π°Π½Π½ΠΎΠ³ΠΎ ΡΠΈΠΏΠ° Ρ ΠΏΠ°ΡΠΈΠ΅Π½ΡΠΎΠ² Ρ ΠΌΠΈΠ΅Π»ΠΎΠ΄ΠΈΡΠΏΠ»Π°Π·ΠΈΠ΅ΠΉ ΠΈ ΡΠΏΠΈΡΠΏΠ°Π΄ΠΈΠ΅ΠΉ Ρ ΠΈΠ·ΠΎΠ»ΠΈΡΠΎΠ²Π°Π½Π½ΠΎΠΉ Π½Π΅Π΄ΠΎΡΡΠ°ΡΠΎΡΠ½ΠΎΡΡΡΡ ΡΡΠ΅ΡΡΠ°Π»ΡΠ½ΡΡ
ΡΡΠΈΠ½ΠΊΡΠ΅ΡΠΎΠ² ΠΌΠΎΠ³ΡΡ ΠΏΡΠΎΠ²ΠΎΠ΄ΠΈΡΡΡΡ ΠΊΠ°ΠΊ ΡΠ°ΠΌΠΎΡΡΠΎΡΡΠ΅Π»ΡΠ½ΡΠΉ ΠΌΠ΅ΡΠΎΠ΄, Π° ΠΈΡ
ΡΡΡΠ΅ΠΊΡΠΈΠ²Π½ΠΎΡΡΡ Π΄ΠΎΡΡΠΈΠ³Π°ΡΡ 70 %
Interactive effects of age and gender on levels of toxic and potentially toxic metals in children hair in different urban environments
Children growth and development may be affected by metal exposure. The objective of the present study was to investigate the interactive effects of age and gender on children hair toxic metal levels in urban environment of two Russian cities. A total of 2021 children living in Moscow and Novosibirsk aged 1β18Β years old were examined. Hair Al, As, Cd, Hg, Ni, Pb and Sn levels were assessed using inductively-coupled plasma mass-spectrometry in dynamic reaction cell mode. Children from Novosibirsk were characterised by higher hair Al (37%), As (385%), Cd (127%), Hg (11%), Ni (23%), Pb (72%) and Sn (25%) in comparison to Moscow values. In the general cohort, boys had higher Al (13%), As (51%), Cd (65%), Pb (63%) and Sn (18%) levels, whereas hair Ni was higher in girls (17%). Further analysis demonstrated age-specific gender differences. In particular, only hair Ni and Cd levels were higher in male toddlers and pre-schoolers from Novosibirsk as compared to females. No gender difference was detected in Moscow. Maximal gender differences in hair metal levels were detected in adolescents for both locations. International Union of Pure and Applied Chemistry (IUPAC) reference values for all groups were also calculated. The overall reference limits for the studied children population were Al (1.335β3.340Β Β΅g/g), As (0.021β0.384Β Β΅g/g), Cd (0.000β1.389Β Β΅g/g), Hg (0.024β0.722Β Β΅g/g), Ni (0.076β0.701Β Β΅g/g), Pb (0.050β1.490Β Β΅g/g) and Sn (0.070β1.026Β Β΅g/g). Two-way ANOVA demonstrated significant effects of age, gender and age*gender interaction on hair metals in both cities. At the same time, the age-specific changes in hair metal content were more expressed in children from Novosibirsk, being exposed to higher metal pollution. The obtained data demonstrate that age, gender as well as the particular rate of pollution in each location should be taken into account during interpretation of hair test results. Β© 2018, Β© 2018 Informa UK Limited, trading as Taylor & Francis Group
Interactive effects of age and gender on levels of toxic and potentially toxic metals in children hair in different urban environments
Children growth and development may be affected by metal exposure. The objective of the present study was to investigate the interactive effects of age and gender on children hair toxic metal levels in urban environment of two Russian cities. A total of 2021 children living in Moscow and Novosibirsk aged 1β18Β years old were examined. Hair Al, As, Cd, Hg, Ni, Pb and Sn levels were assessed using inductively-coupled plasma mass-spectrometry in dynamic reaction cell mode. Children from Novosibirsk were characterised by higher hair Al (37%), As (385%), Cd (127%), Hg (11%), Ni (23%), Pb (72%) and Sn (25%) in comparison to Moscow values. In the general cohort, boys had higher Al (13%), As (51%), Cd (65%), Pb (63%) and Sn (18%) levels, whereas hair Ni was higher in girls (17%). Further analysis demonstrated age-specific gender differences. In particular, only hair Ni and Cd levels were higher in male toddlers and pre-schoolers from Novosibirsk as compared to females. No gender difference was detected in Moscow. Maximal gender differences in hair metal levels were detected in adolescents for both locations. International Union of Pure and Applied Chemistry (IUPAC) reference values for all groups were also calculated. The overall reference limits for the studied children population were Al (1.335β3.340Β Β΅g/g), As (0.021β0.384Β Β΅g/g), Cd (0.000β1.389Β Β΅g/g), Hg (0.024β0.722Β Β΅g/g), Ni (0.076β0.701Β Β΅g/g), Pb (0.050β1.490Β Β΅g/g) and Sn (0.070β1.026Β Β΅g/g). Two-way ANOVA demonstrated significant effects of age, gender and age*gender interaction on hair metals in both cities. At the same time, the age-specific changes in hair metal content were more expressed in children from Novosibirsk, being exposed to higher metal pollution. The obtained data demonstrate that age, gender as well as the particular rate of pollution in each location should be taken into account during interpretation of hair test results. Β© 2018, Β© 2018 Informa UK Limited, trading as Taylor & Francis Group