1
|
Chwoyka C, Linhard D, Durstberger T, Zaller JG. Ornamental plants as vectors of pesticide exposure and potential threat to biodiversity and human health. ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH INTERNATIONAL 2024; 31:49079-49099. [PMID: 39044056 PMCID: PMC11310276 DOI: 10.1007/s11356-024-34363-x] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/01/2024] [Accepted: 07/08/2024] [Indexed: 07/25/2024]
Abstract
The production of conventional ornamental plants is pesticide-intensive. We investigated whether pesticide active ingredients (AIs) are still present in ornamentals at the time of purchase and assessed their potential ecotoxicity to non-target organisms. We purchased 1000 pot plants and 237 cut flowers of different species from garden centers in Austria and Germany between 2011 and 2021 and analyzed them for up to 646 AIs. Ecotoxicological risks of AIs were assessed by calculating toxic loads for honeybees (Apis mellifera), earthworms (Eisenia fetida), birds (Passer domesticus), and mammals (Rattus norvegicus) based on the LD50 values of the detected AIs. Human health risks of AIs were assessed on the basis of the hazard statements of the Globally Harmonized System. Over the years, a total of 202 AIs were detected in pot plants and 128 AIs in cut flowers. Pesticide residues were found in 94% of pot plants and 97% of cut flowers, with cut flowers containing about twice as many AIs (11.0 ± 6.2 AIs) as pot plants (5.8 ± 4.0 AIs). Fungicides and insecticides were found most frequently. The ecotoxicity assessment showed that 47% of the AIs in pot plants and 63% of the AIs in cut flowers were moderately toxic to the considered non-target organisms. AIs found were mainly toxic to honeybees; their toxicity to earthworms, birds, and mammals was about 105 times lower. Remarkably, 39% of the plants labeled as "bee-friendly" contained AIs that were toxic to bees. More than 40% of pot plants and 72% of cut flowers contained AIs classified as harmful to human health. These results suggest that ornamental plants are vectors for potential pesticide exposure of consumers and non-target organisms in home gardens.
Collapse
Affiliation(s)
- Cecily Chwoyka
- Department of Integrative Biology and Biodiversity Research, Institute of Zoology, BOKU University, 1180, Vienna, Austria
| | - Dominik Linhard
- Umweltforschungsinstitut & Umweltorganisation Global 2000 (Friends of the Earth Austria), Neustiftgasse 36, 1070, Vienna, Austria
| | - Thomas Durstberger
- Umweltforschungsinstitut & Umweltorganisation Global 2000 (Friends of the Earth Austria), Neustiftgasse 36, 1070, Vienna, Austria
| | - Johann G Zaller
- Department of Integrative Biology and Biodiversity Research, Institute of Zoology, BOKU University, 1180, Vienna, Austria.
| |
Collapse
|
2
|
Porseryd T, Hellström KV, Dinnétz P. Pesticide residues in ornamental plants marketed as bee friendly: Levels in flowers, leaves, roots and soil. ENVIRONMENTAL POLLUTION (BARKING, ESSEX : 1987) 2024; 345:123466. [PMID: 38295928 DOI: 10.1016/j.envpol.2024.123466] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 12/08/2023] [Revised: 01/24/2024] [Accepted: 01/28/2024] [Indexed: 02/06/2024]
Abstract
Ornamental plants rich in pollen and nectar are often marketed as "pollinator-friendly" by flower retailers. However, even though the plants are attractive from a foraging perspective, i.e pollen and nectar rich, bees and other pollinating insects could be at risk from exposure of pesticide residues on the plants or from pesticide used during production. Pesticides used in ornamental plant production could lead to environmental emissions both during cultivation, at retailer displays and when planted in gardens by the consumers. This study aims to investigate what pesticides that are used in the production of perennial ornamental plants sold in Sweden and if the residues could pose a risk for wild pollinators. We analyze an array of 536 pesticides in whole flowers, leaves, roots and soil of 54 individual (46 had flowers) perennial plants specifically marketed as "bee friendly". In addition, seeds from 65 seed bags were analyzed for the same pesticides. Our result show for the first time the distribution of pesticide residues between flowers, leaves, roots and soils of ornamental plants. We also show that all ornamental plants analyzed contained at least one pesticide, and that some samples contained up to 19 different substances.
Collapse
Affiliation(s)
- Tove Porseryd
- School of Natural Sciences, Technology and Environmental Studies, Södertörn University, Huddinge, Sweden; The Swedish Society for Nature Conservation, Stockholm, Sweden.
| | | | - Patrik Dinnétz
- School of Natural Sciences, Technology and Environmental Studies, Södertörn University, Huddinge, Sweden
| |
Collapse
|
3
|
Carillo P, Pannico A, Cirillo C, Ciriello M, Colla G, Cardarelli M, De Pascale S, Rouphael Y. Protein Hydrolysates from Animal or Vegetal Sources Affect Morpho-Physiological Traits, Ornamental Quality, Mineral Composition, and Shelf-Life of Chrysanthemum in a Distinctive Manner. PLANTS 2022; 11:plants11172321. [PMID: 36079702 PMCID: PMC9460061 DOI: 10.3390/plants11172321] [Citation(s) in RCA: 2] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Abstract] [Track Full Text] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Received: 08/11/2022] [Revised: 08/26/2022] [Accepted: 09/01/2022] [Indexed: 11/16/2022]
Abstract
Protein hydrolysates (PHs) are a prominent category of plant biostimulants, mainly constituted of amino acids, oligopeptides and polypeptides, obtained by partial hydrolysis of animal or plant protein sources. Despite scientific evidence supporting the biostimulant action of PHs on vegetables, the morphological, physiological, and shelf-life performances underlying the PH action on cut flowers are still poorly explored. Accordingly, the aim of this research is to assess the effects of three commercial biostimulants, one animal PH (PH A, Hicure®) and two plant PHs (PH V1, Trainer® and PH V2, Vegamin©), on two chrysanthemum (Chrysanthemum morifolium) cultivars (Pinacolada and Radost). In both cultivars, only the plant-derived PH (V1 and V2) treatments recorded significantly higher fresh plant biomass than the control (on average +18%, in both cultivars). The foliar application of the vegetal-derived PHs but not the animal one, particularly in Pinacolada, improved the status of plants, stimulating stem elongation and the apical flower diameter. In Pinacolada, applications with PH V1 resulted in a significant increase in nitrate and P concentration in leaves and Ca content in flowers compared with the control (+43%, +27%, and +28% for nitrate, P, and Ca, respectively). In Radost, PH A and PH V2 applications caused a significant reduction in nitrate concentration in both leaves and flowers compared with the control. One week after harvest, in both cultivars, PH A applications caused flower stems to wilt faster than the control. In contrast, plants treated with PH V1 revealed significantly slower flower stem senescence compared to the control. Flower wilting during vase life was correlated to a decrease in the K-to-Na ratio in flowers due to an inability to transport K to the flowers from the leaves rather than an increase in Na in the flowers themselves.
Collapse
Affiliation(s)
- Petronia Carillo
- Department of Environmental, Biological and Pharmaceutical Sciences and Technologies, University of Campania “Luigi Vanvitelli”, Via Vivaldi 43, 81100 Caserta, Italy
| | - Antonio Pannico
- Department of Agricultural Sciences, University of Naples Federico II, 80055 Portici, Italy
| | - Chiara Cirillo
- Department of Agricultural Sciences, University of Naples Federico II, 80055 Portici, Italy
| | - Michele Ciriello
- Department of Agricultural Sciences, University of Naples Federico II, 80055 Portici, Italy
| | - Giuseppe Colla
- Department of Agriculture and Forest Sciences, University of Tuscia, 01100 Viterbo, Italy
| | - Mariateresa Cardarelli
- Department of Agriculture and Forest Sciences, University of Tuscia, 01100 Viterbo, Italy
| | - Stefania De Pascale
- Department of Agricultural Sciences, University of Naples Federico II, 80055 Portici, Italy
| | - Youssef Rouphael
- Department of Agricultural Sciences, University of Naples Federico II, 80055 Portici, Italy
- Correspondence:
| |
Collapse
|
4
|
Boye K, Boström G, Jonsson O, Gönczi M, Löfkvist K, Kreuger J. Greenhouse production contributes to pesticide occurrences in Swedish streams. THE SCIENCE OF THE TOTAL ENVIRONMENT 2022; 809:152215. [PMID: 34890678 DOI: 10.1016/j.scitotenv.2021.152215] [Citation(s) in RCA: 6] [Impact Index Per Article: 3.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/01/2021] [Revised: 11/02/2021] [Accepted: 12/02/2021] [Indexed: 06/13/2023]
Abstract
Greenhouse and other covered cultivation systems have increased globally over the past several decades, leading to considerably improved product quality and productivity per land area unit. However, there is a paucity in information regarding the environmental impacts of covered production systems, especially regarding pesticides entering the surrounding environment. Aiming to address this knowledge gap, we collected grab samples downstream of greenhouses from seven Swedish streams every 14 days during a 12 month period. In three of the streams, samples were also taken upstream of the greenhouses and in four of the streams time-integrated samples were collected by TIMFIE samplers in the period between grab sampling occasions. The samples were analyzed for 28 substances (27 that were permitted for use in greenhouse production systems in Sweden and one degradation product to a permitted substance). Pesticide use journals were collected from the greenhouse producers for the 12 month period. The results were examined for indications of greenhouse contributions to detection frequencies, maximum and average concentrations, and potential ecotoxicicity in several ways: (1) comparing locations downstream of greenhouses with registered use of a substance with those without registered use, (2) comparing results from this study with those from the Swedish environmental monitoring program of pesticides in surface water from catchments with no greenhouses from the same period and region, (3) comparing concentration trends with registered pesticide application times in the greenhouses, and (4) comparing up- and downstream concentrations. The results strongly suggest that greenhouse applications do contribute to pesticide occurrences, maximum and median concentrations for most of the pesticides included in this study, and to potential toxicity to aquatic organisms for several of them, most notably imidacloprid, acetamiprid, carbendazim, and pirimicarb.
Collapse
Affiliation(s)
- Kristin Boye
- SLU Centre for Pesticides in the Environment, Swedish University of Agricultural Sciences, P.O. Box 7066, SE-750 07 Uppsala, Sweden; Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, P.O. Box 7050, SE-75007 Uppsala, Sweden.
| | - Gustaf Boström
- SLU Centre for Pesticides in the Environment, Swedish University of Agricultural Sciences, P.O. Box 7066, SE-750 07 Uppsala, Sweden; Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, P.O. Box 7050, SE-75007 Uppsala, Sweden
| | - Ove Jonsson
- SLU Centre for Pesticides in the Environment, Swedish University of Agricultural Sciences, P.O. Box 7066, SE-750 07 Uppsala, Sweden; Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, P.O. Box 7050, SE-75007 Uppsala, Sweden
| | - Mikaela Gönczi
- SLU Centre for Pesticides in the Environment, Swedish University of Agricultural Sciences, P.O. Box 7066, SE-750 07 Uppsala, Sweden; Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, P.O. Box 7050, SE-75007 Uppsala, Sweden
| | - Klara Löfkvist
- HIR Skåne, Borgeby Slottsväg 11, SE-237 91 Bjärred, Sweden
| | - Jenny Kreuger
- SLU Centre for Pesticides in the Environment, Swedish University of Agricultural Sciences, P.O. Box 7066, SE-750 07 Uppsala, Sweden; Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, P.O. Box 7050, SE-75007 Uppsala, Sweden
| |
Collapse
|
5
|
Jeong JY, Kim B, Ji SY, Baek YC, Kim M, Park SH, Jung H. Effect of Flutriafol Exposure on Residue Characteristics in Pig Muscle and Fat Tissue. Food Sci Anim Resour 2022; 42:186-196. [PMID: 35028583 PMCID: PMC8728499 DOI: 10.5851/kosfa.2021.e61] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.5] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 09/17/2021] [Revised: 10/13/2021] [Accepted: 10/14/2021] [Indexed: 01/10/2023] Open
Abstract
This study investigated the effect of exposure to flutriafol based on residues in
pigs. Pigs were exposed to different concentrations (0.313, 0.625, 3.125, 6.25,
and 12.5 mg/kg bw/d, n=20) for 4 wk in different treatment groups. Serum
biochemical analysis, residue levels, and histological analysis were conducted
using the VetTest chemistry analyzer, liquid chromatography mass spectrometry,
and Masson’s trichrome staining, respectively. The body weight (initial
and final) was not significantly different between groups. Parameters such as
creatinine, blood urea nitrogen, alanine aminotransferase, and lipase levels
were significantly different as compared to the control group. Flutriafol
increased the residue limits in individual tissue of the pigs in a dose
dependent manner. Flutriafol exposures indicated the presence of fibrosis, as
confirmed from Masson’s trichrome staining. These results suggest that
flutriafol affects the morphology and serum levels in pigs. The dietary
flutriafol levels can provide a basis for maximum residue limits and food safety
for pork and related products.
Collapse
Affiliation(s)
- Jin Young Jeong
- Animal Nutrition & Physiology Division, National Institute of Animal Science, Rural Development Administration, Wanju 55365, Korea
| | - Byeonghyeon Kim
- Animal Nutrition & Physiology Division, National Institute of Animal Science, Rural Development Administration, Wanju 55365, Korea
| | - Sang Yun Ji
- Animal Nutrition & Physiology Division, National Institute of Animal Science, Rural Development Administration, Wanju 55365, Korea
| | - Youl Chang Baek
- Animal Nutrition & Physiology Division, National Institute of Animal Science, Rural Development Administration, Wanju 55365, Korea
| | - Minji Kim
- Animal Nutrition & Physiology Division, National Institute of Animal Science, Rural Development Administration, Wanju 55365, Korea
| | - Seol Hwa Park
- Animal Nutrition & Physiology Division, National Institute of Animal Science, Rural Development Administration, Wanju 55365, Korea
| | - Hyunjung Jung
- Animal Nutrition & Physiology Division, National Institute of Animal Science, Rural Development Administration, Wanju 55365, Korea
| |
Collapse
|
6
|
Pereira PCG, Parente CET, Carvalho GO, Torres JPM, Meire RO, Dorneles PR, Malm O. A review on pesticides in flower production: A push to reduce human exposure and environmental contamination. ENVIRONMENTAL POLLUTION (BARKING, ESSEX : 1987) 2021; 289:117817. [PMID: 34333268 DOI: 10.1016/j.envpol.2021.117817] [Citation(s) in RCA: 4] [Impact Index Per Article: 1.3] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 01/18/2021] [Revised: 07/16/2021] [Accepted: 07/19/2021] [Indexed: 06/13/2023]
Abstract
In several countries, flower import regulations are restricted to food security, by establishing maximum residue limits (MRL) for pesticides in flower-based food products and biosafety, in order to limit the circulation of vectors, pests and exotic species across borders. In this context, the lack of limits on pesticides in flower-products for ornamental purposes can influence the pesticide overuse in production areas, as well as the transfer of contaminated products between countries. Therefore, the purpose of this review was to discuss possible adverse effects on human and environmental health of pesticides used in floriculture, evaluating regulations on the use of these pesticides in the main importing and flower-producing countries. This review included 92 documents. The use of 201 compounds was identified by interviews and analytical measurements. Among them, 93 are banned by the European Union (EU), although 46.3 % of these compounds have been identified in samples from European countries. Latin American countries have a large number of scientific publications on pesticides in flower production (n = 51), while the EU and China have less studies (n = 24) and the United States and Japan have no studies. Regarding adverse health effects, poorer neurobehavioral development, reproductive disorders, congenital malformations and genotoxicity have been reported for residents of flower production areas and workers throughout the flower production cycle. Studies including water samples show overuse of pesticides, while environmental impacts are related to water and air contamination, soil degradation and adverse effects on the reproduction and development of non-target organisms. This review points out that the absence of MRL for non-edible flowers can be crucial for the trade of contaminated products across borders, including pesticides banned in importing countries. Furthermore, setting limits on flowers could reduce the use of pesticides in producing countries.
Collapse
Affiliation(s)
- Patrícia C G Pereira
- Laboratório de Radioisótopos Eduardo Penna Franca, Instituto de Biofísica Carlos Chagas Filho, Universidade Federal Do Rio de Janeiro, Av. Carlos Chagas Filho S/n, Bloco G, Sala 060, Subsolo, 21941-902, Cidade Universitária, Rio de Janeiro, RJ, Brazil.
| | - Cláudio E T Parente
- Laboratório de Radioisótopos Eduardo Penna Franca, Instituto de Biofísica Carlos Chagas Filho, Universidade Federal Do Rio de Janeiro, Av. Carlos Chagas Filho S/n, Bloco G, Sala 060, Subsolo, 21941-902, Cidade Universitária, Rio de Janeiro, RJ, Brazil.
| | - Gabriel O Carvalho
- Laboratório de Radioisótopos Eduardo Penna Franca, Instituto de Biofísica Carlos Chagas Filho, Universidade Federal Do Rio de Janeiro, Av. Carlos Chagas Filho S/n, Bloco G, Sala 060, Subsolo, 21941-902, Cidade Universitária, Rio de Janeiro, RJ, Brazil.
| | - João P M Torres
- Laboratório de Micropoluentes Jan Japenga, Instituto de Biofísica Carlos Chagas Filho, Universidade Federal Do Rio de Janeiro, Av. Carlos Chagas Filho S/n, Bloco G, Sala 060, Subsolo, Rio de Janeiro, 21941-902, Brazil.
| | - Rodrigo O Meire
- Laboratório de Radioisótopos Eduardo Penna Franca, Instituto de Biofísica Carlos Chagas Filho, Universidade Federal Do Rio de Janeiro, Av. Carlos Chagas Filho S/n, Bloco G, Sala 060, Subsolo, 21941-902, Cidade Universitária, Rio de Janeiro, RJ, Brazil.
| | - Paulo R Dorneles
- Laboratório de Radioisótopos Eduardo Penna Franca, Instituto de Biofísica Carlos Chagas Filho, Universidade Federal Do Rio de Janeiro, Av. Carlos Chagas Filho S/n, Bloco G, Sala 060, Subsolo, 21941-902, Cidade Universitária, Rio de Janeiro, RJ, Brazil.
| | - Olaf Malm
- Laboratório de Radioisótopos Eduardo Penna Franca, Instituto de Biofísica Carlos Chagas Filho, Universidade Federal Do Rio de Janeiro, Av. Carlos Chagas Filho S/n, Bloco G, Sala 060, Subsolo, 21941-902, Cidade Universitária, Rio de Janeiro, RJ, Brazil.
| |
Collapse
|
7
|
Stepanycheva E, Petrova M, Chermenskaya T, Pavela R. Fumigant effect of essential oils on mortality and fertility of thrips Frankliniella occidentalis Perg. ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH INTERNATIONAL 2019; 26:30885-30892. [PMID: 31446593 DOI: 10.1007/s11356-019-06239-y] [Citation(s) in RCA: 20] [Impact Index Per Article: 4.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 05/07/2019] [Accepted: 08/16/2019] [Indexed: 05/26/2023]
Abstract
The western flower thrips (Frankliniella occidentalis Perg.) is one of the most economically important insect pests of greenhouse plants. Plant protection against this pest is based predominantly on synthetic insecticides; however, this form of protection poses problems in terms of thrip resistance to the active substances, along with health risks associated with insecticide residues on the treated plants. Therefore, new active substances need to be sought. Essential oils could be a new, appropriate, and safe alternative for greenhouse culture protection. As greenhouses are enclosed areas, fumigation application of EOs is possible. This paper presents acute toxicity results for 15 commercial EOs applied by fumigation, as well as the effect of sublethal concentrations on fertility of F. occidentalis females. The most efficient EOs were obtained from Mentha pulegium and Thymus mastichina, with LC50(90) estimated as 3.1(3.8) and 3.6 (4.6) mg L-1 air, respectively. As found for the very first time, sublethal concentrations of EOs could result in a significant reduction in the fertility of surviving T. occidentalis females. Among the tested EOs, the EO from Nepeta cataria provided the highest inhibition of fertility, with EC50(90) estimated as 0.18 (0.36) mg L-1 air. Chemical composition of the most efficient EOs and possible applications of the results in practice are discussed. In conclusion, in light of the newly determined facts, EOs can be recommended as active substances for botanical insecticides to be applied against Thysanopteran pests by fumigation.
Collapse
Affiliation(s)
- Elena Stepanycheva
- All-Russian Institute of Plant Protection, Podbelsky sh. 3, St. Petersburg-, Pushkin, Russia, 196608
| | - Mariya Petrova
- All-Russian Institute of Plant Protection, Podbelsky sh. 3, St. Petersburg-, Pushkin, Russia, 196608
| | - Taisiya Chermenskaya
- All-Russian Institute of Plant Protection, Podbelsky sh. 3, St. Petersburg-, Pushkin, Russia, 196608
| | - Roman Pavela
- Crop Research Institute, Drnovska 507, 161 06, Prague, 6 - Ruzyne, Czech Republic.
| |
Collapse
|
8
|
Aerts R, Joly L, Szternfeld P, Tsilikas K, De Cremer K, Castelain P, Aerts JM, Van Orshoven J, Somers B, Hendrickx M, Andjelkovic M, Van Nieuwenhuyse A. Silicone Wristband Passive Samplers Yield Highly Individualized Pesticide Residue Exposure Profiles. ENVIRONMENTAL SCIENCE & TECHNOLOGY 2018; 52:298-307. [PMID: 29185731 DOI: 10.1021/acs.est.7b05039] [Citation(s) in RCA: 50] [Impact Index Per Article: 8.3] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/23/2023]
Abstract
Monitoring human exposure to pesticides and pesticide residues (PRs) remains crucial for informing public health policies, despite strict regulation of plant protection product and biocide use. We used 72 low-cost silicone wristbands as noninvasive passive samplers to assess cumulative 5-day exposure of 30 individuals to polar PRs. Ethyl acetate extraction and LC-MS/MS analysis were used for the identification of PRs. Thirty-one PRs were detected of which 15 PRs (48%) were detected only in worn wristbands, not in environmental controls. The PRs included 16 fungicides (52%), 8 insecticides (26%), 2 herbicides (6%), 3 pesticide derivatives (10%), 1 insect repellent (3%), and 1 pesticide synergist (3%). Five detected pesticides were not approved for plant protection use in the EU. Smoking and dietary habits that favor vegetable consumption were associated with higher numbers and higher cumulative concentrations of PRs in wristbands. Wristbands featured unique PR combinations. Our results suggest both environment and diet contributed to PR exposure in our study group. Silicone wristbands could serve as sensitive passive samplers to screen population-wide cumulative dietary and environmental exposure to authorized, unauthorized and banned pesticides.
Collapse
Affiliation(s)
- Raf Aerts
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Laure Joly
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Philippe Szternfeld
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Khariklia Tsilikas
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Koen De Cremer
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Philippe Castelain
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Jean-Marie Aerts
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Jos Van Orshoven
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Ben Somers
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Marijke Hendrickx
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - Mirjana Andjelkovic
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| | - An Van Nieuwenhuyse
- Scientific Service Health and Environment, ‡Scientific Service Chemical Residues and Contaminants, §Operational Directorate Food, Medicines and Consumer Safety, £Scientific Service Toxicology, and ∥Scientific Service Mycology and Aerobiology, Scientific Institute of Public Health (WIV-ISP) , Brussels, Belgium
- Division Forest, Nature and Landscape, Department Earth and Environmental Sciences, #Measure, Model & Manage Bioresponses (M3-BIORES), Division Animal and Human Health Engineering, Department of Biosystems (BIOSYST), and ∇Environment and Health, Department of Public Health and Primary Care, University of Leuven (KU Leuven) , Leuven, Belgium
| |
Collapse
|
9
|
The Effects of Industrial Protective Gloves and Hand Skin Temperatures on Hand Grip Strength and Discomfort Rating. INTERNATIONAL JOURNAL OF ENVIRONMENTAL RESEARCH AND PUBLIC HEALTH 2017; 14:ijerph14121506. [PMID: 29207573 PMCID: PMC5750924 DOI: 10.3390/ijerph14121506] [Citation(s) in RCA: 8] [Impact Index Per Article: 1.1] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Received: 10/29/2017] [Revised: 11/27/2017] [Accepted: 12/01/2017] [Indexed: 11/16/2022]
Abstract
Daily working activities and functions require a high contribution of hand and forearm muscles in executing grip force. To study the effects of wearing different gloves on grip strength, under a variety of hand skin temperatures, an assessment of the maximum grip strength was performed with 32 healthy male workers with a mean age (standard deviation) of 30.44 (5.35) years wearing five industrial gloves at three hand skin temperatures. Their ages and anthropometric characteristics including body mass index (BMI), hand length, hand width, hand depth, hand palm, and wrist circumference were measured. The hand was exposed to different bath temperatures (5 °C, 25 °C, and 45 °C) and hand grip strength was measured using a Jamar hydraulic hand dynamometer with and without wearing the gloves (chemical protection glove, rubber insulating glove, anti-vibration impact glove, cotton yarn knitted glove, and RY-WG002 working glove). The data were analyzed using the Shapiro-Wilk test, Pearson correlation coefficient, Tukey test, and analysis of variance (ANOVA) of the within-subject design analysis. The results showed that wearing gloves significantly affected the maximum grip strength. Wearing the RY-WG002 working glove produced a greater reduction on the maximum grip when compared with the bare hand, while low temperatures (5 °C) had a significant influence on grip when compared to medium (25 °C) and high (45 °C) hand skin temperatures. In addition, participants felt more discomfort in both environmental extreme conditions. Furthermore, they reported more discomfort while wearing neoprene, rubber, and RY-WG002 working gloves.
Collapse
|